EPA-450/3-74-053
SEPTEMBER 1974
DEVELOPMENT OF AN EXAMPLE
10-YEAR AIR QUALITY
MAINTENANCE PLAN
FOR THE DENVER AQMSA
U.S. ENVIRONMENTAL PROTECTION AGENCY
Office of Air and Waste Management
Office of Air Quality Planning and Standards
Research Triangle Park, North Carolina 2771]
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EPA-450/3-74-053
DEVELOPMENT OF AN EXAMPLE
10-YEAR AIR QUALITY
MAINTENANCE PLAN
FOR THE DENVER AQMSA
by
GCA Corporation, GCA/Technology Division
Burlington Road,
Bedford, Massachusetts 01730
Contract No. 68-02-1376
EPA Project Officer: David C. Sanchez
Prepared for
ENVIRONMENTAL PROTECTION AGENCY
Office of Air and Waste Management
Office of Air Quality Planning and Standards
Research Triangle Park, North Carolina 27711
September 1974
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This report is issued by the Environmental Protection Agency to report technical
data of interest to a limited number of readers. Copies are available free of
charge to Federal employees, current contractors and grantees, and nonprofit
organizations - as supplies permit - from the Air Pollution Technical Information
Center, Environmental Protection Agency, Research Triangle Park, North
Carolina 27711, or, for a fee, from the National Technical Information Service,
5285 Port Royal Road, Springfield, Virginia 22151.
This report was furnished to the Environmental Protection Agency by the GCA
Corporation, GCA-/ Technology Division, Bedford, Massachusetts 07130, in ful-
fillment of Contract No. 68-02-1376. The contents of this report are reproduced
herein as received from the GCA Corporation, GCA/Technology Division. The
opinions, findings, and conclusions expressed are those of the author and not
necessarily those of the Environmental Protection Agency. Mention of company
or product names is not to be considered as an endorsement by the Environmen-
tal Protection Agency.
Publication No. EPA-450/3-74-053
11
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CONTRACTOR DISCLAIMER
This report was prepared as a demonstration of the administrative and
technical procedures available for preparation of an air quality mainte-
nance plan. Because this was a demonstration exercise rather than an
official plan and because time and resources were quite restricted it
was necessary to make certain compromises in data collection, analysis,
and plan preparation. In using this report readers are cautioned that
some numerical results may need refinement before being used for setting
policy or selecting pollution control measures. No quantitative results
in this report are known to be greatly in error but neither should they
be regarded as precise. GCA/Technology Division would be pleased to
assist any reader who wishes guidance on using any of the specific data
herein.
iii
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ACKNOWLEDGMENTS
Many individuals and several organizations have been helpful in carrying
out this study; for these contributions the GCA/Technology Division ex-
tends its sincere gratitude.
Continued project direction and guidance were given by Mr. David Sanchez
(Project Officer) of the Standards Implementation Branch, EPA, Durham,
North Carolina, and Mr. John Philbrook of EPA, Region VIII, Denver.
Many members of federal, state, and local agencies supplied data and
other information to this study, and their assistance is gratefully
acknowledged. Particular thanks are extended to the Colorado Air Pol-
lution Control Commission, the Colorado Air Pollution Control Division,
the Colorado Division of Highways, the Denver Regional Council of Govern-
ments, the Regional Transportation District, the Colorado Land Use Com-
mission, and the Revion VIII office of the U.S. Environmental Protection
Agency.
iv
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CONTENTS
Page
Contractor Disclaimer iii
Acknowledgments iv
List of Figures ix
List of Tables xiii
Section
I INTRODUCTION 1
BACKGROUND TO PLAN DEVELOPMENT 1
II DENVER AIR QUALITY MAINTENANCE STUDY AREA
REGIONAL SETTING 8
PHYSICAL DESCRIPTION 8
SOCIOECONOMIC DESCRIPTION 40
AIR QUALITY AND PLANNING AGENCIES 58
REGIONAL LEGAL AUTHORITY FOR AIR QUALITY
CONTROL 76
LEGAL AUTHORITY FOR LAND USE PLANNING 80
CURRENT EMISSION CONTROL REGULATIONS 82
REFERENCES 100
III EMISSION ALLOCATION AND PROJECTION METHODOLOGY 103
PROJECTION BASIS 103
POINT SOURCE EMISSIONS 104
MOBILE SOURCE EMISSIONS 107
NEDS AREA SOURCE EMISSIONS 112
FUGITIVE DUST EMISSIONS 113
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CONTENTS (Continued)
Section
IV
REFERENCES
ASSESSMENT OF EXISTING AND FUTURE AIR QUALITY
TOTAL SUSPENDED PARTICIPATES
CARBON MONOXIDE
PHOTOCHEMICAL OXIDANTS
REFERENCES
CONTINGENCY ATTAINMENT STRATEGIES
INTRODUCTION
TRANSPORTATION CONTROLS
FUGITIVE DUST CONTROLS
OTHER AREA SOURCE ATTAINMENT MEASURES FOR
PARTICULATES
THE PLAN FOR THE MAINTENANCE OF AIR QUALITY
INTRODUCTION
MAINTENANCE PLAN DESCRIPTION
EXPECTED AIR QUALITY IMPACT OF STRATEGY
MAINTENANCE MEASURES
IMPLEMENTATION TOOLS
SOCIAL AND ECONOMIC IMPACTS
REFERENCES
Appendix
A ECONOMIC DATA FOR THE DENVER AQMSA BY COUNTY
EXPLANATION OF COUNTY DATA SHEETS
VI
Page
125
127
127
155
166
182
184
184
185
189
192
197
197
199
201
203
212
216
221
A-l
A-l
VI
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CONTENTS (Continued)
Append ix Page
ADAMS COUNTY A-2
ARAPAHOE COUNTY A-3
BOULDER COUNTY A-4
CLEAR CREEK COUNTY A-6
DENVER COUNTY A-7
DOUGLAS COUNTY A-8
GILPIN COUNTY A-9
JEFFERSON COUNTY A-10
LARIMER COUNTY A-11
WELD COUNTY A-12
B COLORADO AIR POLLUTION CONTROL ACT - 1970 B-l
C 40 CFR 52, SUBPART G - COLORADO C-l
D HOUSE BILL 1041 D-l
E COLORADO EMISSION CONTROL REGULATIONS AND AMBIENT
AIR QUALITY STANDARDS - AS AMENDED E-l
F THE COLORADO PLAN FOR FEDERAL SECONDARY AMBIENT
AIR QUALITY STANDARDS (PARTICIPATE MATTER AND
SULFUR OXIDES) ADOPTED FEBRUARY 28, 1974 F-l
G PROJECTION OF POINT SOURCE PARTICULATE EMISSIONS G-l
H PROJECTION OF AREA SOURCE PARTICULATE EMISSIONS H-l
I ALLOCATION OF FUGITIVE DUST EMISSIONS 1-1
J PROJECTION OF FUGITIVE DUST EMISSIONS J-l
GENERAL J-l
ESTIMATING CONTROL FROM EXISTING REGULATIONS J-2
VII
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CONTENTS (Continued)
Append ix Page
ESTIMATING CONTROL FROM PROPOSED ADDITIONAL
REGULATIONS J-8
FORECASTS OF GROWTH IN FUGITIVE DUST EMISSIONS J-10
REFERENCES J-21
K DETAILS OF THE CLIMATOLOGICAL DISPERSION MODEL
(COM) AND THE HANNA-GIFFORD MODEL K-l
CLIMATOLOGICAL DISPERSION MODEL K-l
HANNA-GIFFORD MODEL K-8
REFERENCES K-ll
L PROCEDURES FOR CALCULATION OF PROJECTED EMISSION
DENSITIES FOR THE DENVER METROPOLITAN GRID AND FOR
THE CITIES OF BOULDER, FT. COLLINS, AND GREELEY L-l
Vlll
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FIGURES
No. Page
1 Colorado Air Quality Control Regions 10
2 Spatial Characteristics of the Metropolitan
Denver AQCR 11
3 Spatial Characteristics of Larimer and Weld Counties 12
4 Topographic Map of the Metropolitan Denver AQCR 13
5 Monthly Wind Roses for Denver, Colorado 17
6 Monthly Mean Mixing Heights at Denver, Colorado Based
on an 8-Year Period 18
1 Average Wind During Pollution Episodes From 10 a.m.
to 2 p.m. (a,b,c) 22
8 Diurnal Variations in Total Oxidants (a) and Carbon
Monoxide (b) at the CAMP station in Denver for
Selected Months 23
9 Annual Growth Rates for Economic Activity Showing
Land Use Development Potential, Denver Region 27
10 Denver Region 29
11 Denver Region 30
12 Off-Street Parking Inventory in the Denver Central
Business District, January 1970 38
13 County Shares of Regional Population 1900-1980 for
Metropolitan Denver 43
14 Present and Projected Population of Colorado and
the Denver Metropolitan Area 44
15 Present and Projected Employment by Industry Group
in the Metropolitan Denver Region 50
16 1970 Employment Density Per Acre 52
17 1980 Employment Density Per Acre 53
IX
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FIGURES (Continued)
No. Page
18 Minority Population as a Percentage of Total
Population 57
19 Organization Chart for Air Pollution Control Division 61
20 JRPP: Transportation and Land Use Planning Structure 72
21 Six County JRPP Area - By Super Districts 106
22 Fugitive Dust Zones for Larimer, Weld, and Boulder
Counties (1972 Emissions in Tons/Yr/4 ktn2) 117
23 Fugitive Dust Zones for Adams, Arapahoe, Clear Creek,
Denver, Douglas, Gilpin and Jefferson Counties (1972
Emissions in Tons/Yr/4 km^) 118
24 Priority I Area in the Denver AQMSA 120
25 Average Annual Suspended Particulate Concentrations
Measured Within the Denver AQMSA During 1970-1972 133
26 Relationship Between the Annual Geometric Mean of
Total Suspended Particulate Concentration and the
Percentage of 24-Hour Average Concentration Above
the Secondary Standard 136
2
27 (a) Source Strengths in (j.g/m /sec (b) Resultant
Concentrations in |j.g/m3 141
28 Frequency of Wind Directions After Summation Over
Wind Speeds and Stabilities 142
29 Isopleths of Projected Carbon Monoxide Emission
Densities From Motor Vehicles in Denver County and
Surrounding Areas in 1975 159
30 Isopleths of Projected Carbon Monoxide Emission
Densities From Motor Vehicles in Denver County and
Surrounding Area in 1980 160
31 Isopleths of Projected Carbon Monoxide Emission
Densities From Motor Vehicles in Denver County and
Surrounding Area in 1985 161
x
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FIGURES (Continued)
No. Page
32 CO Emissions Within Denver Core Area 165
33 Carbon Monoxide Emission Densities for Four Cities
in the Denver AQMSA 168
34 Isopleths of Projected Hydrocarbon Emission Densities
from Motor Vehicles in Denver County and Surrounding
Area in 1975. Units are kg/mi2/day. 170
35 Isopleths of Projected Hydrocarbon Emission Densities
from Motor Vehicles in Denver County and Surrounding
Area in 1980. Units are kg/mi2/day. 171
36 Isopleths of Projected Hydrocarbon Emission Densities
from Motor Vehicles in Denver County and Surrounding
Area in 1985. Units are kg/mi2/day. 172
37 HC Emissions within Denver Metropolitan Area 175
38 Isopleths of Projected Vehicular Emissions of Nitrogen
Oxides in Denver County and the Surrounding Area in
1975. Units are kg/mi*/day. 178
39 Isopleths of Projected Vehicular Emissions of Nitrogen
Oxides in Denver County and Surrounding Area in 1980.
Units are kg/mi2/day. 179
40 Isopleths of Projected Vehicular Emissions of Nitrogen
Oxides in Denver County and Surrounding Area in 1985.
Units are kg/mi2/day. 180
41 Joint Regional Planning Program Transit System 205
42 Joint Regional Planning Program Highway Plan 211
Appendix
L-la Average Speed Correction Factor for All Model Years,
Carbon Monoxide L-4
L-lb Average Speed Correction Factor for All Model Years,
Hydrocarbons L-5
xi
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FIGURES (Continued)
No. Page
L-lc Average Speed Correction Factor for All Model Years,
Nitrogen Oxides L-6
L-2 Map of the Denver Metropolitan Area Showing VMT
Grid Centers L-7
xii
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TABLES
No. Page
1 Climatological Summary for Denver, Colorado (from
the Weather Handbook, Conway Publications) 16
2 Percentage of Frequency of Low-Level Inversion
(Stapleton International Airport) 20
3 Motor Vehicle Usage in the Denver Metropolitan
Area: Distribution of Trips by Purpose, and
Automobile Occupancy 34
4 Annual Transit Passengers in the Denver Metropolitan
Area 1969-74 35
5 Parking Inventory and Usage in the Denver CBD,
Average Weekday, January 1970 39
6 Population in Larimer and Weld Counties, 1940-1970 46
7 Projected Population in Larimer and Weld Counties
1970-2000 47
8 Forecasted Annual Rates of Employment Growth,
Metropolitan Denver 1970-2000 51
9 Means of Transportation to Place of Work in the
Denver SMSA 54
10 Demographic Characteristics for the Denver Standard
Metropolitan Statistical Area, 1970 55
11 Budget: Colorado Air Pollution Control Activities
(FY 1974) 62
12 County Master Plans 77
13 Colorado Ambient Air Standards for Suspended Parti-
culate Matter and Sulfur Dioxide (Micrograms per
Cubic Meter - ug/m3) 83
14 Point Source Growth Rates for Particulate Emissions
(Baseyear 1975) 108
15 Area Source Growth Rates for Particulate Emissions
(Baseyear 1972) 115
Kill
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TABLES (Continued)
No.
16 Fugitive Dust Emission Densities by Zones (Tons/
Year/4 km2) 119
17 Fugitive Dust Emissions Growth Rates by Zones 123
18 Summary of National Ambient Air Quality Standards 128
19 Denver Front Range AQMSA Air Quality Data; Annual
Geometric Means, Particulate Matter 129
20 Average Conditions at Sampler Locations 131
21 Percentage of Observations Exceeding the Secondary
Standards 134
3
22 Calculated Particulate Concentration (|_ig/m ) 144
23 Fitted Particulate Concentrations (|_ig/m ) 145
24 Percentage Contribution of Particulate Source
Sectors 1972 148
25 Calculated Particulate Concentrations Due to Point
Sources - 1972 and 1975 (ug/m3) 149
26 Percentage Contribution of Particulate Source
Sectors 1975 150
27 Percentage Contribution of Particulate Source
Sectors 1980 151
28 Percentage Contribution of Particulate Source
Sectors 1985 152
29 Fitted Particulate Air Quality For 1972, 1975, 1980,
1985 153
30 Denver Area Carbon Monoxide Data 156
31 Carbon Monoxide Emissions from Motor Vehicles Within
the Denver Core Area 163
32 Denver Area Oxidant Data Obtained in 1973 by
Chemiluminescence 167
xiv
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TABLES (Continued)
No. Page
33 Hydrocarbon Emissions Within the Denver Metropolitan
Area 173
34 Vehicular Emissions of Nitrogen Oxides within Denver
Metropolitan Area 177
35 Fugitive Dust Emissions Growth Rates by Zones with
Maximum Feasible Controls 191
36 Percentage Contribution of Particulate Source Sectors
for Maximum Control Case for Fugitive Dust 1975 193
37 Percentage Contribution of Particulate Source Sectors
for Maximum Control Case for Fugitive Dust 1980 194
38 Percentage Contribution of Particulate Source Sectors
for Maximum Control Case for Fugitive Dust 1985 195
39 Examination of Alternative Growth Trends for Denver
Area 202
40 Annual Budgets for a Four-Person Family - Denver
Metropolitan Area 219
xv
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APPENDIX TABLES
No. Page
G-l Employment in the Super Districts (1970) G-2
G-2 Percentage of Employment in Each Super District (1970) G-4
G-3 Particulate Point Source Emissions in JRPP Counties
(1972 NEDS Data - tons/year) G-5
G-4 Allocation of Particulate Point Emissions to the
Super Districts - 1972 (tons/year) G-6
G-5 Growth Rates of Employment in the Super Districts
(Baseyear 1972) G-7
G-6 Projected Particulate Point Emissions in the Super
Districts - 1975 (tons/year) G-8
G-7 Projected Particulate Point Source Emissions in the
Super Districts - 1980 (tons/year) G-9
G-8 Projected Particulate Point Source Emissions in the
Super Districts - 1985 (tons/year) G-10
G-9 Projected Particulate Point Source Emissions in the
Super Districts - 1990 (tons/year) G-ll
G-10 Point Source Emission Reductions Due to Promulgated
Regulations - By County G-13
H-l Population and Employment in the Super Districts
(1970) H-2
H-2 Percentage of Population and Employmentin the
Super Districts (1970) H-4
H-3 Particulate Area Emissions in JRPP Counties (1972
NEDS Data - tons/year) H-5
H-4 Allocation of Particulate Area Emissions to the
Super Districts - 1972 (tons/year) H-6
H-5 Growth Rates of Population and Employment in the
Super Districts - 1972 to 1975 H-7
H-6 Growth Rates of Population and Employment in the
Super Districts - 1972 to 1980 H-8
xv i
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APPENDIX TABLES (Continued)
No. Page
H-7 Growth Ratio of Population and Employment in the
Super Districts - 1972 to 1985 H-9
H-8 Growth Ratio of Population and Employment in the
Super Districts - 1972 to 1990 H-10
H-9 Projected Particulate Area Source Emissions in the
Super Districts - 1975 (tons/year) H-ll
H-10 Projected Particulate Area Source Emissions in the
Super Districts - 1980 (tons/year) H-12
H-ll Projected Particulate Area Source Emissions in the
Super Districts - 1985 (tons/year) H-13
H-12 Projected Particulate Area Source Emissions in the
Super Districts - 1990 (tons/year) H-14
H-13 Stationary Area Source Growth Rates by Super Districts
(Baseyear 1972) H-16
H-14 Functional-System Annual Travel Data H-17
1-1 Colorado AQMSA Fugitive Dust Inventory 1-4
J-l Estimated Average Daily Traffic on Unpaved Roads, by
County, 1972 J-3
J-2 Calculation of Amount of Traffic on Controlled Unpaved
Roads J-3
J-3 Degree of Control of Fugitive Dust on Unpaved Roads,
by County J-5
J-4 Estimated Percentage of Land Development Activity
in Priority I Area, by County J-5
J-5 Estimated Percentage of Residential-Commercial Con-
struction Activity in Priority I Area, by County J-6
J-6 Estimated 1975 Fugitive Dust Emissions With Present
Regulation No. 1 J-7
J-7 Estimated 1975 Fugitive Dust Emissions With Proposed
Maximum Control J-9
xvii
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APPENDIX TABLES (Continued)
No. Page
J-8 Growth Factors for Sand on Paved Roads J-ll
J-9 Calculation of Activity Growth Factors for Con-
struction and Development in JRPP Area J-13
J-10 Calculation of Emissions Growth Factors for Con-
struction and Development in JRPP Area, With
Adjustment for Population Growth J-14
J-ll Calculation of Activity Growth Factor for Highway
Construction in JRPP Area J-15
J-12 Calculation of Emissions Growth Factors for Highway
Construction in JRPP Area, With Adjustment for
Population Growth J-16
J-13 Estimated 1980 Fugitive Dust Emissions With Present
Regulation No. 1 J-17
J-14 Estimated 1985 Fugitive Dust Emissions With Present
Regulation No. 1 J-18
J-15 Estimated 1980 Fugitive Dust Emissions With Maximum
Feasible Controls J-19
J-16 Estimated 1985 Fugitive Dust Emissions With Maximum
Feasible Controls J-20
K-l Central Wind Speeds K-2
K-2 Exponents for Wind Profile K-4
K-3 Parametric Values for o~z (p) K-5
L-la Light-Duty Vehicle Exhaust Emission Factors for High-
Altitude Cities (cip) L-8
L-lb Heavy-Duty Gasoline-Powered Vehicle Exhaust Emission
Factors for High-Altitude Areas (cip) L-9
L-2a Carbon Monoxide Deterioration Factors for Light-Duty
Gasoline-Powered Vehicles in All Areas Except
California (dipn) L-10
xviii
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APPENDIX TABLES (Continued)
No. Page
L-2b Exhaust Hydrocarbon Deterioration Factors for Light-
Duty Gasoline -Powered Vehicles in All Areas Except
California (dipn) L-ll
L-2c Nitrogen Oxide Deterioration Factors for Light-Duty
Gasoline-Powered Vehicles in All Areas Except
California (dn) L-12
L-3 Weighted Annual Travel for Light (LDV) and Heavy (HDV)
Duty Vehicles L-13
L-4 Light-Duty and Heavy-Duty Vehicle Crankcase and
Evaporative Hydrocarbon Emissions for All Areas
Except California L-14
L-5 Road Classification and Speeds for Denver Metropolitan
Area L-15
L-6a Average Daily VMT on Freeways in 1972 L-16
L-6b Average Daily VMT on Expressways in 1972 L-17
L-6c Average Daily VMT on Primary Arterials in 1972 L-18
L-6d Average Daily VMT on Minor Arterials in 1972 L-19
L-6e Average Daily VMT on Collectors in 1972 L-20
L-6f Average Daily VMT on Centroid Connectors in 1972 L-21
L-6g Average Daily VMT on Ramps in 1972 L-22
L-6h Average Daily VMT on Major Arterials in 1972 L-23
L-6i Average Daily VMT on Freeways in the Year 2000 L-24
L-6j Average Daily VMT on Expressways in the Year 2000 L-25
L-6k Average Daily VMT on Primary Arterials in the Year 2000 L-26
L-61 Average Daily VMT on Minor Arterials in the Year 2000 L-27
L-6m Average Daily VMT on Collectors in the Year 2000 L-28
L-6n Average Daily VMT on Centroid Connectors in the Year
2000 L-29
xix
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APPENDIX TABLES (Continued)
No. Page
L-6o Average Daily VMT on Ramps in the Year 2000 L-30
L-6p Average Daily VMT on Major Arterials in the Year 2000 L-31
L-7a Projected Vehicular Emissions of Carbon Monoxide for
the Denver Metro Grid in 1975 (Units are KG/MI2/Day) L-32
L-7b Projected Vehicular Emissions of Carbon Monoxide for
the Denver Metro Grid in 1980 (Units are KG/MI2/Day) L-33
L-7c Projected Vehicular Emissions of Carbon Monoxide for
the Denver Metro Grid in 1985 (Units are KG/MI2/Day) L-34
L-7d Projected Vehicular Emissions of Hydrocarbons for
the Denver Metro Grid in 1975 (Units are KG/MI2/Day) L-35
L-7e Projected Vehicular Emissions of Hydrocarbons for
the Denver Metro Grid in 1980 (Units are KG/MI2/Day) L-36
L-7f Projected Vehicular Emissions of Hydrocarbons for
the Denver Metro Grid in 1985 (Units are KG/MI2/Day) L-37
L-7g Projected Vehicular Emissions of Nitrogen Oxides for
Denver Metro Grid in 1975 (Units are KG/MI2/Day) L-38
L-7h Projected Vehicular Emissions of Nitrogen Oxides for
the Denver Metro Grid in 1980 (Units are KG/MI2/Day) L-39
L-7i Projected Vehicular Emissions of Nitrogen Oxides for
the Denver Metro Grid in 1985 (Units are KG/MI2/Day) L-40
L-8a Functional-System Annual Travel by Urban Area (in
Millions of Vehicle Miles) - 1968 L-41
L-8b Functional-System Annual Travel by Urban Area (in
Millions of Vehicle Miles) - 1990 L-42
L-9 Road Classification and Speeds for Boulder, Ft. Collins,
and Greeley L-43
xx
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EXECUTIVE SUMMARY
INTRODUCTION
The report summarized herein was commissioned by the U.S. Environmental
Protection Agency (EPA) in 1974, as a test and demonstration of the tech-
niques for the preparation of plans for the maintenance of air quality
for the ten-year period from 1975 to 1985. The report contains a draft
plan for both attainment and maintenance of air quality standards in the
Denver Front Range Air Quality Maintenance Study Area (AQMSA).
Maintenance plans, such as the example plan presented in this report, are
required by EPA regulations as a supplement to the air quality planning
in State Implementation Plans which related primarily to the initial at-
tainment of air quality standards. Maintenance planning is directed
towards ensuring the air quality standards will not be violated over the
long term.
The report is organized as follows.
Section I - This section provides an introduction, and
summarizes the difficulties encountered by
the consultants in preparation of the ex-
ample maintenance plan, with an emphasis on
what improvements are needed in the data and
techniques for the planning process.
Section II - This section provides the physical, socio-
economic, and legal setting of the Air
Quality Maintenance Study Area (AQMSA).
xxo.
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Section III - A review of the emission allocation and
projection methodologies used for deter-
mining the air quality in 1975, 1980, and
1985 is given.
Section IV - An assessment of existing and future air
quality is then provided, forming the basis
for the quantified approach to the formula-
tion of the Air Quality Maintenance Plan
(AQMP).
Section V - A contingency air quality attainment strategy
is presented in this section.
Section VI - This last section consists of the air quality
maintenance strategy for the AQMSA. De-
scriptions of the measures, their legal foun-
dation (existing and proposed), and the roles
of agencies involved in the strategy im-
plementation are given.
A summary of the above-mentioned report sections follows.
SECTION II--DENVER AIR QUALITY MAINTENANCE STUDY AREA REGIONAL SETTING
In order to develop appropriate and effective air quality maintenance
measures, it was necessary to achieve a thorough understanding of the
regional and community setting. Section II includes an extensive pre-
sentation of the physical and socioeconomic setting, including
topography, climatology, meteorology, hydrology, land use, transportation
system, demography, employment and residence patterns, institutional ar-
rangements, and related characteristics. Also presented in this section
is a discussion of present organizations and measures for controlling air
pollution in the AQMSA.
Characteristics of Denver Front Range AQMSA
The Denver Front Range Air Quality Maintenance Study Area (AQMSA) includes
the Metropolitan Denver Air Quality Control Region (AQCR), containing
xxii
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Adams, Arapahoe, Boulder, Clear Greek, Denver, Douglas, Gilpin, and
Jefferson Counties, and Larimer and Weld Counties of the Pawnee AQCR.
The AQMSA extends eastward from the Continental Divide into the plains,
with the major urban centers located along the foothills of the Rockies.
The greater Denver area lies within the South Platte River drainage basin
with the City of Denver having an elevation in excess of 5,000 feet above
sea level. Roughly 20 miles to the west the mountains reach elevations of
10,000 to 14,000 feet; to the southwest, the land rises more gradually
along the South Platte River valley. The principal areas of concern for
the development of the Air Quality Maintenance Plan (AQMP) are the popu-
lation centers along the eastern foothills. In addition to the City of
Denver, the AQMSA includes the major urban centers of Boulder, Longmont,
and Broomfield in Boulder County, Fort Collins and Loveland in Larimer
County, Greeley in Weld County and Brighton in Adams County.
The pollutants designated to be of interest in the AQMSA are total sus-
pended particulates, carbon monoxide, nitrogen oxides, and photochemical
oxidants. The particulate problem is basically a result of the arid con-
ditions of the region which are conducive to entrainment and re-entrain-
ment of particulates during windy conditions. Fugitive dust, a major
component of total particulates, has several man-made sources: unpaved
roads, sand on paved roads, agriculture, land development, residential,
industrial, and commercial construction, highway construction, aggregate
storage, cattle feedlots, and quarrying, mining, and tailings.
The other pollutants of interest, CO, NOX, and photochemical oxidants,
result largely from the extensive use of motor vehicles in the Denver AQMSA.
The Denver metropolitan area is characterized by a high growth rate of
motor vehicles (5.2 percent per year increase in registrations) and the
highest per capita automobile registration in the nation, one automobile
for every 1.5 persons. The motor vehicle pollutant problem for the AQMSA
is exacerbated by the high elevation of the region since operating
characteristics of internal combustion engines and the effectiveness of
control devices are functions of ambient air density, with higher altitude
generally resulting in higher vehicular emission rates.
xxiii
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Bus transit is now only used by a small portion of the region's popula-
tion. It was estimated that from 2 to 5 percent of all trips in the Denver
region use the bus system. Bus ridership has been steadily increasing in
recent years, however. Also, in Denver itself the bus system does carry a
significant portion of all trips, accounting for an estimated 20 per-
cent of all central business district-oriented work trips. A major
planning and engineering effort is underway at the Regional Transportation
District to plan and construct a fixed-guideway mass transit system for
the Denver region.
The topography of the region adds to the high ambient concentrations of
pollutants. Under light nighttime wind conditions, surface air, made
relatively more dense by radiational cooling, drains down the river valley
toward the northeast and lower elevations. Thus cold air drainage ap-
parently stops just beyond the suburbs and the shallow air mass, which has
accumulated pollutants from city sources, is frequently brought back by a
sudden wind reversal around noon. Under a light wind regime, crossing and
recrossing of the pollutant source (i.e., the urban area) by the same air
mass may continue for several days, thus leading to an excessive local
accumulation of pollutants.
An understanding of socioeconomic characteristics of the AQMSA provided
important criteria in evaluating the potential effectiveness and applica-
bility of control measures, and in selection of measures for final plan
development. The Denver region's population has grown at a fast pace in
the past 3 decades, the rate of growth ranging from 3 to 4.6 percent
per year. Population is decreasing in the central city as urban sprawl
moves to the north and south along the front range. The suburban com-
munities have accounted for approximately 80 percent of the area's popula-
tion increase between 1950 and 1970. This trend is expected to continue
with the percentage of the total metropolitan Denver population residing
in Denver County going from 65 percent in 1950 to 25 percent in the year
2000.
xxiv
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General land use trends for the Denver area show agricultural and vacant
land being transformed to single-family residential use. Major portions
of the urbanized areas in the region are characterized by single-family
tract housing, strip commercial developments and a substantial freeway
network. Low density and dispersed residential development patterns
characterizing the regions are expected to continue with circumferential
growth occurring from city centers and radial growth along transportation
corridors. Other housing trends, such as a declining number of persons
per housing unit and popularity of low density residences, are expected
to continue based on existing trends, economic forces and social attitudes.
Approximately two-thirds of the employment growth between 1964 and 1970
occurred in Denver County, while about 95 percent of the population
growth was in surrounding counties. This indicates an inward work trip
transportation flow for the region. Projected employment density patterns
illustrate that employment will not disperse significantly through the
region, but will continue to be concentrated in the core region, thus
requiring continued commuter traffic. Some services have followed the
residential development in the suburbs, but as yet no clear proliferation
of industrial development is apparent.
Government Agencies Responsible for Planning and for Air Quality in the
AQMSA
As part of the maintenance study, several agencies were contacted for in-
formation, for aid, or to understand their potential role in air
quality maintenance. The responsibilities of the agencies with major
roles in air quality maintenance planning are summarized below.
Colorado Air Pollution Control Commission - The duties of the Colorado Air
Pollution Control Commission include the development and implementation
of a comprehensive program for prevention, control and abatement of air
pollution throughout the entire state, including a program for control of
emissions from all significant sources of air pollution; the promulgation
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of ambient air goals for every portion of the state; the adoption and
promulgation of ambient air quality standards and emission control regu-
lations; at its discretion, the hearing and determination of violations
and applications for the granting of variances; and, at its discretion,
the review of any variance order or determination of the variance board.
Colorado Air Pollution Control Division - The Division is empowered to
conduct studies and research with respect to air pollution; determine if
the ambient air standards are being violated in any area of the state;
investigate actual, suspected, or potential sources of air pollution;
furnish technical advice and services; notify any affected jurisdiction
of standards which are not being met; and to issue contaminant emission
notices. The Division also has the authority to enforce compliance with
the promulgated emission control regulations.
The Department of Health, in which the Air Pollution Control Division was
established, is designated as the "state agency" for all purposes of the
Federal Clean Air Act, as amended, and regulations promulgated under that
act.
Colorado Division of Planning - The Division of Planning, in the Depart-
ment of Local Affairs, serves as an advisory and coordinating agency with
no regulatory authority. The duties of the Division of Planning are
primarily those of assistance in the gathering and using of data. It also
helps to coordinate the planning activities of other departments or agen-
cies, at the state and local level, to ensure a degree of harmony. The
population statistics, estimates, and projections prepared, maintained,
and interpreted by the Division of Planning are designated as the official
data for state government purposes.
Colorado Land Use Commission - The Colorado Land Use Commission was es-
tablished within the Office of the Governor to encourage planned and
orderly land use development. For the past 3 years the Land Use
Commission has been working to identify a program that will provide a
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framework and a process whereby the State of Colorado and its various
political subdivisions can guide future development. This has culminated
in a report entitled, "A Land Use Program for Colorado," which is briefly
discussed in this report. The Land Use Commission recommendations included
a development permit system which would apply to all developments located
in areas of critical environmental concern and to proposed activities of
regional or State significance.
Joint Regional Planning Program - Denver SMSA - The responsible agency for
comprehensive planning in the Denver SMSA is the Denver Regional Council
of Governments. The responsibility for continuingj comprehensive, and co-
operative (3-C) transportation planning rests with the Joint Regional
Planning Program (JRPP), a cooperative transportation planning effort
carried out jointly by the Denver Regional Council of Governments (DRCOG),
the Regional Transportation District (RTD), and the Colorado Division of
Highways (CDH). Consistent with its role as intergovernmental coordinator
for the SMSA region, the Council of Governments coordinates the joint
planning efforts with federal, state and local units and agencies of
governments. In carrying out this role, the Council makes application for
federal assistance to the planning program, coordinates the planning pro-
gram with the planning for all modes of transportation, coordinates the
needs and findings of the planning program with units of local govern-
ments, coordinates with state planning efforts, and, upon adoption,
certifies land use and public transportation plans to the federal govern-
ment. General policy guidelines are established cooperatively by the
policy bodies of each agency. The staffs of the Council of Governments,
the Regional Transportation District, and the Colorado Division of High-
ways have responsibility for management and control of the planning
elements and tasks assigned to their respective agencies.
Larimer-Weld Regional Planning Commission - The only regional planning
commission which has been created in the Denver Air Quality Maintenance
Study Area, other than the Denver Regional Council of Governments, is the
Larimer-Weld Regional Planning Commission. The Larimer-Weld RPC has
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developed and adopted a master plan which states the goals and policies
for the Larimer-Weld region and provides the development plan for these
two counties.
Air Pollution Control in the AQMSA
A review of the State and Federal regulations controlling emissions and
providing needed review processes was conducted to determine the extent
and impact of the measures already promulgated. In addition, the Colorado
State Air Pollution Control Act of 1970, as amended, and the recently
enacted House Bill No. 1041 were analyzed to identify the existing legal
authority which serves as the basis for the development of maintenance
measures.
In general, it was shown that the Colorado State Air Pollution Control Act
has provided the legal authority required under Federal regulations and
that the Colorado Air Pollution Control Commission has complied with the
Federal requirements by having submitted the required Air Quality Im-
plementation Plan for the State of Colorado and the State of Colorado Air
Pollution Control Transportation and Land Use Plan. These plans have
been reviewed by EPA and found to be conditionally acceptable based upon
the control measures therein. EPA has also promulgated regulations to
deal with the problem of hydrocarbon and carbon monoxide emissions in the
Denver metropolitan area. These regulations, and the ones promulgated by
the Colorado Air Pollution Control Commission, are summarized by pollutant
in the report.
The legal authority provided by House Bill No. 1041 deals with land use
planning measures in Colorado. This law provides that local governments,
or the Colorado Land Use Commission, may designate certain areas or cer-
tain activities as being of state interest. Such areas or activities must
then be administered by the local government in accordance with either
guidelines provided by the legislation or by certain state agencies.
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SECTION III--EMISSION ALLOCATION AND PROJECTION METHODOLOGY
This section summarizes the procedures used for the allocation and pro-
jection of air pollution emissions in the Denver Front Range AQMSA.
Geographic distribution of emission sources was known from existing data
on carbon monoxide, hydrocarbons/oxidants, and nitrogen oxides, but dis-
tributions had to be developed for area source emissions of particulates.
Fugitive dust sources received particular attention. All pollutants were
then analyzed for their expected future concentrations. Future emissions
were forecasted through indirect techniques involving the use of fore-
casts developed by others for various social, economic, and travel-
related parameters.
Data Sources
For the Denver metropolitan area, the best available data for forecasting
future air quality was the Denver Regional Council of Governments (DRCOG)
projections of growth for the Joint Regional Planning Program (JRPP) area.
The use of this data was a reasonable approach because DRCOG is the de-
velopment commission for this area and will be instrumental in policies
affecting the growth of the region. An important implication of the use
of this data is that, for the JRPP (metropolitan Denver) area, certain
assumptions concerning transportation facilities, population size and dis-
tribution, and the existence of certain highway networks are implicit in
the estimates.
For areas outside the JRPP area, official state projections were available
up to 1980. Additional forecasts were available from county planning
commissions and from the Federal OBERS data. Linear interpolation was
performed to estimate parameters for intervening years.
Data on both present and projected automobile travel, used for projecting
emissions, was supplied by the Colorado Division of Highways. Vehicle-
miles traveled (VMT) data was available by highway functional classifica-
tion and by geographic area. The major problem with this data is that it
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was given only for the years 1968 and 1990 for non-JRPP areas and for 1972
and 2000 in the case of the metropolitan Denver area. A linear interpola-
tion was used to estimate traffic activity for intervening years.
Point Source Emissions
Projections of particulate emissions from point sources were derived from
a review of regulations controlling these emissions and regional forecasts
of economic growth. Estimates of 1975 (base year) emissions were derived
by applying the regulations to known process rates to calculate maximum
emissions. Emissions in future years were estimated by using economic
forecasts for each portion of the study area, on the assumption that emis-
sions would be proportional to employment.
Point source emissions of carbon monoxide were found to be negligible,
compared to mobile sources, and were assumed to be constant. Hydrocarbon
emissions were forecasted based on the control regulations and estimated
effectiveness of the EPA-promulgated transportation control plan. In-
creases in nitrogen oxides emissions from point sources were based upon
forecasted changes in population and employment, but were forecasted only
for the metropolitan Denver area.
Mobile Source Emissions
Emission densities for CO, HC, and NOX were derived from the projected
traffic data for future years. Projected vehicle-miles of travel per day
were supplied by the Colorado Division of Highways for each cell on a grid
established for analysis of the Denver area. For each cell the data
included the VMT for each type of highway and speeds on each type of high-
way. Emissions were then calculated, using the EPA emission factors. For
this analysis it was assumed that emission standards would be delayed by
2 years and that high-altitude requirements would take effect by 1977.
Mobile source emissions were also calculated from projected travel in
selected urban portions of the study area outside the Denver metropolitan
area.
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Area Source Emissions From National Emissions Data System (NEDS)
Projections of increases in emissions of carbon monoxide and nitrogen
oxides were not considered because of the minimal impact area sources
were known to have on ambient concentrations of these pollutants. Hydro-
carbon emissions from area sources were assumed to decrease as a result of
existing regulations.
Area source emissions of particulates provided by the NEDS were projected
to 1975, 1980, and 1985 on much the same basis as particulate point
sources; however, no regulations are applicable to these emissions to pro-
vide an initial decrease in emissions. In addition to employment pro-
jections by source sector, population growth rates were used to project
emissions from the residential sector. Projections of measured particulate
emissions as a result of motor vehicles were made by assuming that the
total emissions from the motor vehicles grow with the increased VMT. Un-
like the direct application of population and employment growth rates to
the emissions, the VMT growth rates were reduced by the degree of control
of particulate emissions expected due to the installation of catalytic
mufflers in new cars.
Fugitive Dust Emissions
The fugitive dust emissions were projected to 1975, 1980, and 1985 by
applying the regulation recently promulgated by the Colorado Air Pollution
Control Commission and the appropriate travel and socioeconomic growth
parameters to the corresponding source sectors for fugitive dust. The
fugitive emission reductions were determined for unpaved roads, land de-
velopment and construction activities, and mining and storage operations,
based on the analysis of control measures provided in a previous study by
PEDCo, thereby giving a new base line year of 1975 to which the growth
factors can be applied.
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Several source categories were seen as unlikely to greatly change in
activity in the AQMSA during the 10-year period: agriculture; quarrying,
mining and tailings; aggregate storage; and cattle feedlots. In addition,
it was expected that control measures on an increasing number of unpaved
roads would offset increased traffic on present low-volume unpaved roads.
Emissions due to sand on paved roads were projected to increase in direct
proportion to the total VMT; land development and residential-commercial
construction as calculated from JRPP projections of land use; and highway
construction activity as projected from the JRPP estimates of land use for
roadways.
SECTION IV--ASSESSMENT OF EXISTING AND FUTURE AIR QUALITY
In this section, an assessment is made of the existing and projected
future air quality by comparing measured and predicted air quality with
the Federal Ambient Air Quality Standards or by comparing predicted and
allowable emission density levels. Separate analyses were made for each
of the four pollutants under study.
Total Suspended Particulates
Baseline Air Quality Data for Particulates - For particulates, no overall
trend in the annual geometric means appeared to occur during the period
1970 to 1973. Since the individual 24-hour concentrations were not yet
available for 1973 and the annual data had not yet appeared in SAROAD, the
development of base line data was restricted to the years 1970, 1971, and
1972. The selection of the no-trend option provided for the use of a 3-
year average annual mean of 130 |_ig/iiP in Denver County. In effect, no air
quality base line year was determined for particulates.
Examination of particulates data from 34 sampling stations in the AQMSA
showed that the annual secondary standard of 60 (ig/m^ was exceeded at all
sites except three remote or rural sites. The primary annual standard of
75 |_ig/m3 was exceeded at 23 of the 34 stations. Highest concentrations
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were observed in the commercial areas of downtown Denver where the
secondary standard was exceeded about one third of the time. Concentra-
tions exceeding the secondary standard were found to occur most fre-
quently during the months from October through April and least frequently
during June or July. However, this seasonal trend appeared to be much
less evident in Weld County, where summertime concentrations also fre-
quently violated the secondary standard.
o
Using a background concentration of 30 p.g/m and the base line concentra-
3
tion of 130 (jg/m , it was determined that the required reduction in emis-
sions is 55 percent to meet the primary standard or 70 percent to meet
the secondary standard, in Denver County. Substantial reductions are
also needed in other cities and are discussed in the report.
Modeling of Particulate Air Quality - Atmospheric modeling was used to
provide projections of particulate air quality, thereby helping in the
analysis of the spatial concentration pattern and the changes in this
pattern due to variations in source strengths during the period of in-
terest. By calibrating the model with the actual air quality measure-
ments, it was possible to project the air quality over a much larger area
than that covered by the network of stations.
For purposes of air quality projections, it was decided to apply the
Climatological Dispersion Model (COM) to calculate average annual ground
level air pollutant concentrations due to point sources. Area and
fugitive dust source contributions were evaluated by means of the Hanna-
Gifford Area Source Model. The CDM was chosen for point sources with
buoyant plumes since it can account in more detail for the distribution
of wind speeds and stabilities in addition to the presence of a mixing
layer. The Hanna-Gifford model has the advantage that the air quality
within a particular grid square may be related directly to the emission
density within that square and those immediately adjacent.
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The modeling was performed on the 1972 emission levels for point, area,
and fugitive sources, and for 1975 point source emissions to provide an
estimate of the impact of the point source regulations on air quality.
The percentage contribution of each source sector to the total calculated
concentration was maintained and projected to 1975, 1980, and 1985 by use
of the emission growth factors derived earlier. By projecting the per-
centage contributions, new calculated concentrations could be determined
as well as new percentage contributions from each source sector. Ambient
level air concentrations of particulates were thus calculated for each of
the air sampling station locations.
Applying the various growth rates to the contributions from each source
sector and adjusting for the background levels, percentage contributions
and projected total fitted plus background concentrations for 1975, 1980,
and 1985 were calculated. In spite of the SIP attainment strategies, these
projections demonstrated that at most sampling sites the secondary stan-
dards for particulates would continue to be exceeded and the primary stan-
dard would not be attained in the urban areas of the AQMSA. Additional
reductions to obtain the primary and secondary standards in 1975 in down-
town Denver were determined to be 46 and 64 percent respectively. In the
more rural regions, the attainment of the secondary standards required a
further reduction of 43 percent.
The projected particulate air quality and the percentage contributions
from each source sector indicated that point sources, under current regula-
tions, contribute only to a small degree to the measured concentration of
particulates. The contributions from area and fugitive sources are com-
parable and represent the majority of the emissions contributing to the
increased level of particulates.
Carbon Monoxide
Base Line Air Quality Data for Carbon Monoxide - Carbon monoxide measure-
ments were made at only one station in 1971 and 1972 with five additional
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monitors being added in 1973. A review of the 1-hour and 8-hour con-
centrations measured indicated that control of the 8-hour concentrations
would ensure the attainment of the 1-hour standard also. As no trend
could be definitely established, examination of the second highest 8-hour
concentrations for the 3-year period indicated that the control
o
strategies would be based on the 1971 second high of 31.6 mg/m . Using
the concentration of 31.6 mg/m^, the required reduction in emissions is
68 percent, based upon a linear rollback from 1971 conditions.
No carbon monoxide data were available for portions of the AQMSA outside
the Denver urbanized area, but emission densities were calculated for
selected cities and compared with concentrations for a comparably sized
area in Denver. The result of this comparison was that Denver has by far
the highest CO emission density in the area, with only one other city
(Ft. Collins) experiencing emission densities high enough to probably
violate the ambient standards over a substantial area. Locally excessive
concentrations could be occurring in the vicinity of heavily traveled
streets, however.
Projected Carbon Monoxide Emissions and Concentrations - Using traffic pro-
jections, based upon the JRPP transportation and land use plan, and pro-
cedures described in Section III, average carbon monoxide emissions and
concentrations were calculated for 240 locations on a grid superimposed
over metropolitan Denver. The resulting forecasts show that maximum
concentrations of carbon monoxide will occur near the center of the
Denver CBD, will decrease markedly over each 5-year period, and will
decrease simultaneously throughout the metropolitan area. Thus, reduc-
tions in tailpipe emissions due to the Federal Motor Vehicle Control
Program more than compensate for the projected growth in vehicular traffic.
Calculations were then made to show the effect of the inspection and
maintenance and retrofit control strategies which EPA Region VIII con-
siders will be used as part of the Transportation Control Plan, namely:
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1. Semi-annual inspection and maintenance using the idle
test mode (failure rate of 50 percent).
2. Air bleed retrofit on pre-1968 light duty vehicles.
3. Air bleed retrofit with exhaust gas recirculation on
1968 to 1974 light duty vehicles.
Strategies 1 and 2 were promulgated by EPA in the official TCP, but strat-
egy 3 is a probable replacement for a high altitude modification proposed
originally.
Using the assumption, developed earlier, that a 68 percent reduction in CO
emissions will be necessary in 1977 in the Denver core area, the emissions
must be reduced by an amount equivalent to 34 percent of the light duty
vehicle travel in the core area, even with the tailpipe strategies listed
above. If, as is estimated by EPA and is discussed in Section V of the
report, the light duty vehicle travel can only be reduced by approximately
15 percent, then the analysis implies that the CO standard will not be
achieved before the end of 1979; thus some modification to the assumed
strategies must be made if the standards are to be met by 1977. (With
only the tailpipe strategies and no reduction in VMT by light duty vehi-
cles, the standards were forecasted to be met by the end of 1980.) Out-
side of Denver, the analysis showed that the emission densities should be
within the allowable amount calculated for Denver without the use of added
control strategies; and in Denver, carbon monoxide concentration was
predicted to remain within the allowable limits once the allowable limit
is achieved.
Photochemical Oxidants
Base Line Air Quality Data for Oxidants - The study of the oxidant con-
centrations reported since 1970 by a variety of methods, including the
approved chemiluminescence method begun in 1973, indicated that the second
highest 1-hour concentration of oxidants observed was 490 ng/m^ and oc-
curred in 1973. Therefore, 1973 must be the air quality baseline year for
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strategy determination. Use of this baseline concentration and the rela-
tionship from Appendix J of 40 CFR Part 51 showed that the required re-
duction in hydrocarbon emissions is 82 percent. The use of a straight
rollback would predict the need for a 67 percent reduction. It was de-
cided to use the straight rollback basis for computing allowable emissions.
Projected Emissions of Hydrocarbons and Concentrations of Photochemical
Oxidants - In a manner similar to that for CO, hydrocarbon emission den-
sities were calculated for the Denver metropolitan area. As was the case
with carbon monoxide, the maximum emission densities occur near the Denver
CBD and the trend is for reduced emissions throughout the area. Unlike CO,
however, emissions from non-mobile sources contribute significantly to the
hydrocarbon emissions and were thus added to the vehicular emissions.
Again assuming the tailpipe controls described earlier will be in effect,
it was calculated that an additional reduction in hydrocarbon emissions
equivalent to 45 percent of the light duty vehicle VMT must be achieved to
meet the standards in 1977. With a 15 percent reduction in VMT by light
duty vehicles, the standards were predicted to be met by early 1981. With
no reduction in VMT the standards would not be met until sometime in 1982.
As with CO, it was forecasted that the standards for photochemical oxidants
would be met throughout the remaining portion of the maintenance period
once the standards are initially achieved.
Nitrogen Oxides
Base Line Air Quality Data for Nitrogen Oxides - The only reported set of
nitrogen dioxide measurements made with a currently acceptable analytical
method that is also statistically adequate for the determination of an
annual mean was collected in Denver in 1972. The annual arithmetic mean
obtained from the 6759 1-hour observations made by an instrumental
calorimetric method during the year was 73
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The measured concentration is thus well below the national standard of
100 p.g/nr*. Hence, no reduction is necessary to initially meet the
standards.
Projected Emissions and Concentrations of Nitrogen Oxides - Nitrogen oxide
emissions from vehicular sources were calculated using the same techniques
as for other vehicular emissions. Little change in emission patterns was
predicted for the period of 1975 to 1980, but a substantial reduction in
emissions was forecasted for the 1980 to 1985 period, reflecting the emis-
sion controls to take effect in the late 1970's. No area was predicted to
experience significantly increasing emissions from the increased amount of
travel activity. Separately analyzing the contributions from vehicle types
showed that emissions from light duty vehicles will increase until 1977 and
then decrease, while emissions from heavy duty and diesel vehicles will in-
crease slowly. The maximum total emissions from vehicular sources were
calculated to be approximately the same as the 1972 emissions, when the
annual mean concentration of nitrogen oxides was only 73 percent of the
standard. These calculations therefore showed that a substantial increase
in emissions from other sources could be tolerated without exceeding the
standards. Emissions from non-vehicular sources could increase at a rate
of about 6.5 percent per year from 1972 to 1980, when vehicular emissions
were forecasted to begin to decline, without exceeding the calculated
allowable emissions. Emissions from non-vehicular sources are actually
expected to increase at a rate of only about 2 percent per year. Thus, no
violation of the nitrogen oxide standards was predicted for the maintenance
period.
SECTION V--CONTINGENCY ATTAINMENT STRATEGIES
The projections of concentrations in the previous section demonstrated
that, given previously quantified control regulations and air quality
trends, the primary and secondary standards for total suspended parti-
culates, carbon monoxide, and photochemical oxidants would not be achieved
by the specified attainment dates. Since the attainment of the desired
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air quality is an integral part of the Air Quality Maintenance Plan de-
veloped, it was necessary to investigate those measures which must be
implemented to ensure attainment of the standards.
This section discusses transportation control measures and fugitive dust
control measures as a contingency attainment strategy package. The
measures are presented as a means of ensuring the effectiveness and in-
tegrity of the Colorado SIP as well as the AQMP supplement to the plan.
For the State of Colorado, contingency attainment measures are intended
to reduce concentrations to the National Ambient Air Quality Standards
within the time frame of the 1977 deadline.
Transportation Control Measures
In response to the EPA-promulgated TCP, the Colorado Air Pollution Control
Commission recently promulgated Regulation No. 9 which deals with VMT re-
duction measures: exclusive bus-carpool lanes, park and ride facilities,
employer carpooling programs, and employer mass transit incentives. As
these control measures have only recently been promulgated, it was not
possible to quantify the emission reduction potential of the individual
measures. Instead, it was assumed that the maximum possible reductions in
VMT was 15 percent of travel by light duty vehicles in 1977.
This reduction in VMT still left another 30 percent reduction in light
duty VMT needed for sufficient control of hydrocarbons and 19 percent
reduction needed for carbon monoxide emissions, in 1977. The only mea-
sure available for increased reduction of emissions, considering the
constraints already imposed, was therefore a gasoline sales limitation.
As insufficient data was available for the quantification of the reductions
in gasoline sales that would be needed, no control strategy was spe-
cifically formulated for this contingency. It was also determined that no
further regulations were needed at this time to ensure later strategy for-
mulation since EPA had already promulgated regulations requiring the
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continuing review of the progress of the transportation control plan and
the determination of the measures needed to implement a gasoline sales
limitation program.
Fugitive Dust Control Measures
A review of the current regulations for the control of fugitive dust and
the study of the fugitive dust problem in Colorado identified some
areas where more stringent controls on fugitive dust could be applied.
Specifically, this entailed the extension of the current controls to the
entire AQMSA instead of just the Priority I area within that region. In
addition, control measures for dust from sand on paved roads were
suggested.
This strategy was shown to generally prevent future growth in fugitive
dust emissions in spite of increased source activity; however, this
strategy, by itself, did not bring about the attainment of the primary
standard for particulates throughout the AQMSA.
Other Area Source Attainment Measures for Particulates
As all reasonably available control technology (RACT) had already been
applied to the point and fugitive dust source sectors without attainment
of the particulate standards, a quick investigation of the possible con-
trol measures for area sources was conducted. Unfortunately, it was
shown that current information did not allow for the formulation of any
control measures which could satisfy the need for the attainment of the
standards. The use of lead-free gasoline was found to have a minimal
impact on the total air quality situation. A potentially powerful con-
trol measure on the use of bituminous coal was discarded due to data
base uncertainties.
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SECTION VI--MAINTENANCE STRATEGIES
The air quality projections generated by this report made use of population
and employment projections done by the Joint Regional Planning Program
(JRPP). These JRPP numbers reflected the expected growth given the JRPP
transportation, highway, and land use plans. As shown in Section IV, air
quality maintenance in the Denver AQMSA is no problem once attainment has
been accomplished. It was because of this fact that the key elements of
the JRPP plan were chosen as the maintenance measures for the region.
This section discusses the JRPP transportation, land use, and highway plans
as maintenance measures. Two implementation tools are discussed as means
of ensuring maintenance measure realization. These tools are air contami-
nant emission permits and use of land development permits. Included in the
discussion are descriptions of the measure or tool, its legal foundation,
as well as the roles played by involved agencies. A final section deals
with the social and economic impacts of the maintenance measures.
Maintenance Measures
The transportation plan features a rapid transit system and expansion of
bus service within the region. The rapid transit system itself is con-
ceived as 100 miles of two-way guideways with 58 stations interconnected
by automatically controlled twelve-passenger vehicles. It is recommended
that the transportation plan be incorporated into the official State Im-
plementation Plan. In addition certain regulations to be promulgated by
the Air Pollution Control Commission are proposed to provide a framework
for incorporating air quality considerations into the detailed planning
process and in subsequent changes.
A major feature of the JRPP land use plan is the development of 13 activ-
ity centers. These centers are described as aggregations of urban ac-
tivity large enough to be primary generators of large internal activity.
They are expected to be terminal locations for the rapid transit system.
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The evolution of these centers is dependent upon the construction of the
rapid transit system as well as the JRPP highway plan. Air contaminant
emission permits will also serve as a prime tool in activity center creation.
The third maintenance measure is the construction of the approved JRPP
highway plan. It is not the purpose here to encourage additional highway
construction, but instead to have construction which complements the JRPP
public transportation plan.
Implementation Tools
The two primary tools for ensuring the implementation of the maintenance
measures are the air contaminant emission permit and the land development
permit systems.
EPA regulations (40 CFT 51.18) require that new or modified sources of
air pollution be reviewed for their air quality impact before construction
or major modification. States must demonstrate that they have adequate
legal authority to prevent the construction or modification of new sources
of air pollution. Once Colorado has complied with the requirement for
indirect source controls it is recommended that the criteria for review
of new indirect sources in the JRPP area include the question of com-
pliance with the JRPP plan.
Land development permits are the second implementation tool. Existing
legislation requires the issuance of a permit before an area of state
interest can be developed. Since interchanges involving arterial highways
as well as rapid or mass transit terminals, stations, and fixed guideways
are designated as being areas of state interest, this permit system is an
important means of ensuring JRPP plan implementation.
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Social and Economic Impacts of the Maintenance Plan
The effects of the JRPP plan on social and economic parameters are dis-
cussed in order to gauge any negative impacts which air quality maintenance
might impose. Social areas analyzed include mobility of the population,
relocation caused by rapid transit construction, and reaction of the pop-
ulation to the system in general. Overall, it appears that the JRPP plan
through its proposed transportation system will increase mobility while
forcing little relocation. The social impact is generally positive.
The economic parameters considered were impacts on employment, income, and
business establishment activity. It was shown that employment in the con-
struction sector will increase with system construction and that once the
system is in operation labor mobility should improve the job choice of low
income residents. The impact on family income was shown to be minor.
Lower income families will end up paying as large a percentage of their
income to finance the system as upper income families. This is offset to
some degree, however, since lower income families are likely to gain most
in terms of mobility once the system is in operation. Business establish-
ments are not expected to suffer from the JRPP plan. Some may be forced
to relocate to activity centers, however, as spending locations change.
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SECTION I
INTRODUCTION
BACKGROUND TO PLAN DEVELOPMENT
This document contains a draft plan for the attainment and maintenance
of air quality standards in the Denver Front Range Air Quality Mainten-
ance Study Area, including Adams, Arapahoe, Boulder, Clear Creek, Denver,
Douglas, Gilpin, Jefferson, Larimer and Weld Counties and herein referred
to as the Denver AQMSA. Pollutants for which attainment and maintenance
activities may be necessary are identified as total suspended partic-
ulates, carbon monoxide, oxides of nitrogen and photochemical oxidants.
This plan was necessitated by the review of state plans conducted by
the Administrator of the United States Environmental Protection Agency.
All state implementation plans were disapproved because of their lack
of regulations or procedures for ensuring the maintenance of national
standards.
Pursuant to Section 51.12, paragraph (e), Part 40 of the Code of Federal
Regulations (40 CFR 51.12(e)) all states were required to identify areas
that have the potential for exceeding National Ambient Air Quality Stan-
dards due to present air quality or the projected growth over the sub-
sequent 10-year period, 1975 to 1985. The above-mentioned area and the
associated pollutants were so identified.
Attainment activities were initially outlined in the Air Quality Implemen-
tation Plan for the State of Colorado (often referred to as the State Im-
plementation Plan or SIP) for total suspended particulates, carbon monoxide,
-------
and photochemical oxidants, necessitating the need for maintenance activ-
ities for these pollutants upon the attainment of the National Ambient
Air Quality Standards (NAAQS). It was anticipated that nitrogen oxides
would also exceed the standards so this problem is also considered herein.
For this area, and any other area so identified, it is necessary to pre-
pare and submit the following (40 CFR 51.l2(g)):
"(1) An analysis of the impact on air quality of pro-
jected growth and development over the 10-year period
from the date of submittal.
"(2) A plan to prevent any national standards from being
exceeded over the 10-year period from the date of sub-
mittal. Such plan shall include, as necessary, control
strategy revisions and/or other measures to ensure that
projected growth and development will be compatible with
maintenance of the national standards throughout such
10-year period."
This document addresses these requirements for the Denver AQMSA.
Difficulties Encountered
As this report represents one of the first efforts directed at the crea-
tion of an air quality maintenance plan, it is useful to identify and
discuss some of the problems encountered. It is hoped that this will aid
future efforts in this area.
This discussion is general in nature. The problem areas mentioned are
felt to be those which are indigenous to such exercises.
The first phase in the preparation of an air quality maintenance plan
involves the compilation, coordination, and analysis of a variety of data
sources. Data problems include the lack of relevant data, discrepancies
between two or more independent sources of data, and data which is
deficient for one reason or another. The projection of population is one
area where such problems exist. For the Joint Regional Planning Program
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(JRPP) areas, Denver Regional Council of Governments (DRCOG) population
projections were available for the years 1980, 1990, and 2000 at various
levels of aggregation. Linear interpolation was used to calculate pro-
jections for intervening years.
Population estimates by county for all of Colorado were available from
the Colorado Division of planning. While these are the official state
projections, they have been completed only for the years 1975 and 1980.
Other population estimates included county planning commissions' data
and OBERS data ("OBJERS" is an acronym for joint economic projections by
several Federal agencies). It was found that significant discrepancies
exist between these two sources and the official state projections.
Travel activity data also presented some difficulty. Data on both present
and projected automobile travel was supplied by the Colorado Division of
Highways. Vehicle-miles traveled data is available by highway functional
classification (interstate, other principal arterials, minor arterials,
major collectors, minor collectors, and local streets) and by geographic
area. Average speeds are provided by functional classification, but were
not separately identified by geographic area. The major problem with the
data is that it is given only for the year 1968 and 1990 for non-JRPP
areas and for 1972 and 2000 in the case of the Denver metropolitan area.
A linear interpolation was used to generate traffic activity for inter-
vening years since there was no clear basis for any other form of inter-
polation.
An additional problem was the coordination of various types of data. Data
is often generated for specific geographic areas (JRPP super district,
AQCR boundaries, traffic zones, etc.) which are incongruous. Singificant
amounts of time could be saved if these deficiencies were rectified.
Suggested guidelines for standardization of data, which would help to
alleviate these problems in the future, include the following.
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1. Input should be encouraged to be based locally and the
projections (with confidence levels) should be made for
the smallest possible unit.
2. There should be requirements that all planning activi-
ties (Air Quality Maintenance, water quality planning)
and other infrastructures use this data to ensure com-
parability of projections.
3. A preferred method of automated data acquisition
should be indicated.
The second phase of the development of an air quality maintenance plan
involves the translation of socioeconomic data into emissions. Unfortu-
nately there exists no perfect way for projecting area or point source
emissions. For purposes of projecting point source emission rates, em-
ployment by industrial category was used. Area source emissions were
projected by population and employment growth rates. In both cases
linear relationships were assumed between the socioeconomic variable
and the emission. Work is currently being done in this area. Volume 7
of the EPA's Guidelines for Air Quality Maintenance Planning and Analysis
provides a "workbook" approach for calculating emissions using the best
available data sources. Work such as this should go far in alleviating
this problem area.
Phase three involves the modeling of air quality. A meaningful air qual-
ity projection procedure initially rests upon the ability to separate
the contribution from different source types to air quality at a par-
ticular point. This in turn depends upon knowledge of the magnitude
and distribution of point and area source emissions for a given base
year. The locations and emission characteristics of point sources are
usually much better known than those of area sources, whose emissions
are obtained on a county-wide basis and then must be allocated. Popula-
tion density was the sole allocation criterion employed by EPA in their
computerized emissions gridding procedure which generated the area source
emissions maps used in the study. This technique is probably valid for
emissions due to home heating but would not really apply for industrial
sources. Perhaps the least well understood emissions are those from
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fugitive dust sources. In addition to the rather obvious uncertainty
in the emission factors for these sources, their allocation was based
upon such criteria as agricultural land use and density of dirt roads.
The most detailed knowledge of area source emissions exists for CO, HC,
and NO emissions from mobile sources. This is the case because most
x
urban areas have rather detailed information concerning current and
projected traffic on a network of roadways which can be described in
terms of a coordinate system.
Given that the strength and distribution of the various sources are
well known, there still remains the problem of relating these emissions
to concentrations at various points. Fortunately for area source emis-
sions it is generally true that for primary pollutants the air quality
is due primarily to local emissions. This is the basis of the rollback
model used in connection with mobile source emissions. For elevated
point sources the analysis of air quality contributions requires the
application of an atmospheric diffusion model. The results from such
a model depend strongly upon the input frequency distributions of wind
speed, direction, and stability which are usually derived from measure-
ments taken at one location in the area of study.
Once the modeling analysis has been completed there remains the task of
calibrating the results with air quality measurements. For particulates,
this is complicated by the need to determine the magnitude of the back-
ground contribution, which is usually considered to be about 30 pig/m .
This background subtraction procedure still does not address the problem
of the contribution of localized sources (dirt roads, traffic, etc.) in
the immediate vicinity of the air sampler. This is particularly a
problem for locations with air samplers situated close to the ground.
This difficulty can be somewhat alleviated by carrying out a least
squares fit of the calculated values to the measurements and then using
the fitted values for projections and application of strategies, as
was done for this report.
-------
The extensive modeling and calibration activities provided projections of
air quality for the maintenance study period, 1975-1985. Unfortunately,
the data indicated that the air quality problem was not merely one of
maintenance of the standards but also one of attainment; i.e., current
regulations provide insufficient control to ensure meeting the National
Ambient Air Quality Standards by 1975 for particulates or by 1977 for
carbon monoxide and oxidants. This necessitated the consideration of
additional controls and the development of contingency attainment
measures.
The final steps in the plan preparation are the most important and per-
haps the most difficult. While the available "tools" for attainment and
maintenance are well known, the selection of the proper measures is
constrained by the legal, social, economic, and political realities of
the maintenance area. These constraint variables involve no small amount
of uncertainty. For example, while laws exist in Colorado for both air
quality and land use, their viability as far as air quality maintenance
is as yet untested. Social and economic constraints involve the accep-
tance of the plan by the business establishment and the community in
general. Uncertainties as to the total political and social acceptability
of the plan are bound to arise due to the lack of communication between
interested parties and agencies before the actual presentation of the
plan to be adopted. The poor definition of governmental agency respon-
sibilities also makes for increased difficulty in assigning roles for
the implementation of an air quality maintenance plan.
As a way of circumventing some of these problems, careful specifications
of the laws which apply, the hierarchy of the agencies involved, and in-
clusion of the public into the election process is necessary.
Report Contents
This document presents the information necessary for the development and
evaluation of the Air Quality Maintenance Plan, as well as the plan itself.
-------
The information is presented in a summarized form, in logical sequence,
with supporting technical data and expanded discussions of methodology
included in the appendices.
The subject matter covered by each of the major sections is briefly
described below:
Section II - This section provides the physical, socioeconomic,
and legal setting of the AQMSA.
Section III - A review of the emission allocation and projection
methodologies used for determining the air quality in
1975, 1980, and 1985 is given.
Section IV - An assessment of existing and future air quality is
then provided, forming the basis for the quantified
approach to the formulation of the Air Quality Main-
tenance Plan (AQMP).
Section V - A contingency air quality attainment strategy is pre-
sented in this section.
Section VI - This last section consists of the air quality main-
tenance strategy for the AQMSA. Descriptions of the
measures, their legal foundation (existing and
proposed), and the roles of agencies involved in the
strategy implementation are given. Cost estimates of
the measures as well as a timetable for additional
legal authority are also presented.
-------
SECTION II
DENVER AIR QUALITY MAINTENANCE STUDY AREA
REGIONAL SETTING
A fundamental requirement in development and assessment of air quality
maintenance measures is a thorough understanding of the regional and
urban settings to which they are to be applied. This includes a speci-
fication of the physical setting, including such features as topography,
climatology, meteorology, hydrology, land use and transportation infra-
structure; and socioeconomic parameters including demography, employ-
ment and residence patterns, institutional arrangements and related
characteristics. It is also necessary to have an understanding of the
current air quality control situation in the region: the agencies
currently involved or which are to be concerned with the maintenance of
air quality, the legal authority required and provided, and the degree of
regulation which sources are already undergoing.
This information is summarized and presented in this section.
PHYSICAL DESCRIPTION
Identification of Study Area
Colorado is the eighth largest state. It is rectangular, about 385
miles from east to west and 275 miles from north to south, and has an
area of 104,247 square miles. Roughly one-third of the State, known as
-------
the "western slope," lies west of the Continental Divide. The remaining
two-thirds of the State, lying east of the Divide, is referred to as the
"eastern slope." Approximately 50 mountains have peaks which reach a
height of 14,000 feet or more above sea level.
The State contains seven intrastate air quality control regions (AQCR's)
and a part of the Four Corners Interstate AQCR. The eight AQCR's are
identified by number in Figure 1. Regions 1, 2, 3, 4, and 5 lie prin-
cipally to the east of the Divide. This Air Quality Maintenance Plan
is concerned with conditions within the area designated as the Metro-
politan Denver AQCR (Region 2) and Larimer and Weld Counties of the
Pawnee AQCR (Region 1). It includes, in addition to the City of Denver,
the major urban centers of Boulder, Longmont and Broomfield in Boulder
County, Fort Collins and Loveland in Larimer County, Greeley in Weld
County, and Brighton in Adams County. These cities and other charac-
teristics of the region are displayed on the maps in Figures 2 and 3.
Topography
Principal topographical features of the Denver portion of the AQMSA
region are shown in Figure 4. The AQMSA extends eastward from the Con-
tinental Divide into the plains, with the major urban centers located
along the foothills of the Rockies. The greater Denver area lies within
the South Platte River drainage basin as shown in the figure. The City
of Denver, through which the river flows, has an elevation in excess of
5000 feet. Roughly 20 miles to the west the mountains reach elevations
of 10,000 to 14,000 feet; to the southwest the land rises more gradually
along the South Platte River valley.
Problems in developing appropriate transportation control strategies
for the AQMSA have been compounded by the high elevation of the region,
since operating parameters of internal combustion engines and the effec-
tiveness of control devices are functions of ambient air density. The
influence of topography upon climatological and meteorological features
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controlling the pollution characteristics of the area is developed in
the following two subsections.
Climatology of the Region
With a given set of emission sources, the degree of air pollution ex-
perienced within an urban area, including its spatial distribution and
the frequency and duration of its occurrence, depends largely upon
existing meteorological conditions. The principal controlling meteor-
ological parameters are the wind speed and direction, and the vertical
stability of the atmosphere within the first few hundred feet above the
ground. To a large extent the wind speed governs the rate of dilution
experienced by the pollutants upon emission, and the stability controls
the rate at which pollutants can be mixed vertically and the thickness
of the atmospheric layer through which this mixing occurs. It follows
that the pollution potential for a region is greatest during periods
of light winds and strong surface temperature inversions. Other param-
eters of importance are precipitation, which cleanses the air, and solar
radiation, which initiates photochemical reactions. This section pre-
sents climatological summaries of pertinent meteorological data.
The climates of local areas of Colorado are strongly influenced by dif-
ferences in terrain and elevation, and by the orientation of mountain
ranges and valleys relative to general air movements. Wide variations
occur within short distances. For example, the difference in annual
mean temperature (35 F) between Pikes Peak and Las Animas, 90 miles to
the southeast, is about the same as that between southern Florida and
Iceland. As a second example, the average annual snowfall at Cumbres
in the southern mountains is nearly 300 inches, while less than 30 miles
away at Manassa in the San Luis Valley, snowfall averages less than 25
inches. As noted previously, the Denver AQMSA extends from the mountain
areas in the west into the eastern plains. The principal areas of con-
cern for the development of the AQMP are the population centers along
the eastern foothills and, in particular, the City of Denver.
14
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Because of Denver's location on the eastern slope of the Rocky Mountains
in the belt of prevailing westerlies, the climate is generally mild and
dry. The greatest amount of precipitation occurs in spring when moist
air currents from the Gulf of Mexico meet weak polar outbreaks from the
north. Wide local variations in wind regimes along the foothills are
introduced by mountain and valley winds. Air drainage is generally good
in the canyons, but as these canyons emerge onto the plains the slope is
much less, and the air circulation may become very sluggish along the
wider river and creek valleys, resulting in a drastically increased pol-
lution potential. Other climatic effects of the mountains on this area
are reduced temperature variations and increased precipitation as com-
pared to those of the plains proper. Monthly climatological statistics
for the City of Denver are presented in Table 1, and monthly wind direc-
tion roses, showing prevailing south and southwesterly winds throughout
the year, are presented in Figure 5.
The maximum vertical depth of the atmosphere available in any day for
the mixing of polluted air usually occurs in the afternoon following the
period of maximum surface heating and is known as the maximum mixing
height. The minimum mixing height is associated with minimum surface
temperatures and usually occurs at or around sunrise. For any given
wind speed, the greater the mixing height, the greater the volume of
air available to dilute the pollutants and therefore to lower their con-
centrations. During a typical 24-hour cycle, the depth of the mixing
layer in Denver varies by nearly one order of magnitude as a result of
radiational cooling of the earth's surface at night and solar heating
of the earth's surface during the day. The generally clear skies and
low humidity of the area contributes markedly to the amplitude of this
diurnal cycle. Afternoon mixing heights are least in the fall and win-
ter and greatest in the spring and summer, ranging from a low of about
1300 meters in December to a high of about 3600 meters in May. The mean
morning mixing heights range from about 175 to 450 meters, with the
greatest heights again occurring in the spring and early summer. Monthly
variations of the mixing heights are shown graphically in Figure 6.
15
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JAN
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LEGEND
WIND ROSES SHOW PERCENTAGE
OF TIME WIND BLEW FROM THE
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« INDICATES LESS THAN 0 5% CALM
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17
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Figure 6.
Monthly mean mixing heights at Denver, Colorado
based on an 8-year period
18
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An inversion layer in the atmosphere is a layer through which the tem-
perature increases with altitude and within which vertical motions are
suppressed. The inversion may be ground-based, trapping pollutants
near ground level, or it may occur at some appreciable height above
ground where it serves as a lid to the mixing layer. On most nights
of the year in the Denver area, temperature inversions form at or near
the surface; these inversions range from a few degrees to 30 F or more
in extreme cases. In Table 2, the frequency of low-level inversions in
Denver is given by season for four times of the day. The high frequency
of early morning inversions in summer (84 percent at 5 a.m.) is not
necessarily associated with high pollution levels, since daytime heat-
ing rapidly breaks up the inversion as shown by the reduction in fre-
quency to 15 percent by 8 a.m.
Meteorology and Denver Pollution Levels
Periods of exceptionally high pollution levels in Denver have been
studied in detail by Riehl and Crow (1962) and Riehl and Herkhof (1970,
1972). An understanding of local meteorological conditions giving rise
to extreme pollution, and their prediction, is obviously requisite to
the successful development and application of episodic control strat-
egies. Perhaps the most important result of the initial work by Riehl
and Crow was documentation of a daily wind regime that occurs over the
metropolitan Denver area during light wind conditions, and the asso-
ciated movement of a coherent polluted air mass.
As shown in Figure 4, the South Platte River passes through the City
of Denver, flowing from southwest to northeast. Under light nighttime
wind conditions surface air, made relatively more dense by radiational
cooling, drains down the river valley toward the northeast and lower
elevations. This cold air drainage apparently stops just beyond the
suburbs and the shallow air mass, which has accumulated pollutants
from city sources, is frequently brought back by a sudden wind reversal
around noon. Although this change in wind direction probably reflects,
19
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Table 2. PERCENTAGE OF FREQUENCY OF LOW-LEVEL INVERSION"
(STAPLETON INTERNATIONAL AIRPORT)
Season
Fall
Winter
Spring
Summer
5 p.m.
22
54
5
8
8 p.m.
78
82
58
54
5 a.m.
80
83
65
84
8 a.m.
49
75
22
15
Hosier, Charles R. , 1961: Low-level inversion
frequency in the Contiguous United States.
Monthly Weather Review, vol. 89, Sept., 1961,
319-339
20
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in part, upslope winds produced by surface heating during the morning,
the driving mechanism for the reversal is not fully understood. Under
a light wind regime, crossing and re-crossing of the pollutant sources
by the same air mass may continue for several days, thus leading to an
excessive local accumulation of pollutants. The sketches in Figure 7,
taken from Riehl and Crow, show composite wind fields prior to, during,
and following such a wind reversal, and the southerly drift of the re-
turning edge of the polluted air mass on one such day.
Figure 8a shows the diurnal variation of the concentration of total oxi-
dants in downtown Denver averaged over two winter months and two summer
months in 1972. Clearly, maximum concentrations occur during midday
and during the summertime, a reflection of the part played by solar
radiation in their generation. Maximum 1-hour concentrations measured
during the two summer months were 0.13 and 0.18 ppm, substantially ex-
ceeding the allowable level of 0.08 ppm, while the maximum 1-hour con-
centrations measured during the two winter months were 0.08 and 0.03 ppm.
Figure 8b shows the diurnal variation of the concentration of carbon
monoxide for selected months at the same location in downtown Denver
in 1971. Although traffic data have not been plotted in this figure,
it is apparent that the diurnal variation in concentration closely re-
flects the morning and afternoon traffic peaks in all seasons. The
second feature of note is the seasonal change in average concentrations,
with the highest concentrations in the winter, and the lowest concen-
trations in the summer. Presumably these changes result primarily from
seasonal differences in the capacity of the atmosphere to disperse the
pollutants, as reviewed in the previous section.
Hydrology
The Denver AQMSA lies within the South Platte River Basin. The Basin
is characterized in the west by the eastern slopes of the Rocky Mountains
and in the east by the plains. The South Platte River, which flows
21
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Figure 7. Average wind during pollution episodes from 10 a.m.
to 2 p.m. (a, b, c). Length of arrow indicates one-
hour air movement. Curves in "d" indicate forward
edge of polluted mass at indicated times during
southward advance of polluted mass. (From Riehl
and Crow, 1962)
22
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(a) Total Oxidants
16
10 12 14 16
HOUR, ( local time)
18
20 22 24
0246
(b) Carbon Monoxide
8 10 12 14 16
HOUR, (local time)
18 20 22 24
Figure 8. Diurnal variations in total oxidants (a) and carbon
monoxide (b) at the CAMP station in Denver for selected
months. Plotted concentrations are for the succeeding
hour period.
23
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through the metropolitan area from southwest to northeast, originates
in the eastern slope of the Rockies and is fed by snowmelt, rainfall
runoff, groundwater and a number of man-controlled factors such as
sewage treatment plant effluents and trans-mountain diversion. In 1970,
trans-mountain water diversion was 300,500 acre-feet; this diversion is
to be increased to 559,000 acre-feet by the year 2010. This trans-
mountain diverted water affects the hydrology of the South Platte River
Basin through its discharge into the South Platte River after its use
for municipal and industrial purposes. Also, its use for lawn sprinkling
affects the hydrology of the Basin through recharge of groundwater which
feeds many creeks.
Although the Basin only receives an annual average of 14.8 inches of
rainfall, flooding is a fairly common occurrence, with the most recent
floods occurring in 1965 and 1973. Snowmelt, runoff, and rainstorms
are a predominant cause of flooding. Also, urbanization within the
Denver Metropolitan Area, with its resulting increase in impervious
area, increases the peak and volume of floods and increases the proba-
bility of flash floods. The Chatfield Dam on the South Platte and the
Cherry Creek Dam have been constructed to decrease the intensity and
frequency of flooding.
Influenced by regional factors, the South Platte River experiences a
wide range of flows. Sewage treatment plant effluents from Denver and
a few smaller communities contribute to the flow of the South Platte and
become a predominant fraction of the flow during low flow conditions.
The western portion of the Basin is tapped for water supply and in 1970
delivered 146,000 acre-feet which will increase to 223,800 acre-feet by
the year 2010. Once water reaches the main stem of the South Platte,
its major uses are for industrial (e.g. cooling) and irrigation purposes.
24
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The water supply situation is such that some parts of the AQMSA are
limited in growth. Water rights, some dating back over 100 years,
often mean that some areas have no authority to use the water during
periods of low flow. Therefore, certain sections of the AQMSA will
not see major development if water rights are not available.
Land Use
The distribution of land uses in the Denver AQMSA today is the result
of a large number of regional characteristics, very significant among
which are the transportation network and infrastructure. Land use
changes in Colorado parallel national trends, showing an increase in
urban land while agricultural land has declined.
The Metropolitan Denver AQCR covers a land area of 13,067 square kilo-
meters (5045 square miles), centered around the Denver Metropolitan Area,
occupying about 712 square kilometers (275 square miles) and Denver's
center city occupying approximately 5 square kilometers including a
Central Business District (CBD) of 1.4 square kilometers. General land
use trends for the Denver Standard Metropolitan Statistical Area (SMSA)
show agricultural and vacant land being transformed to single-family
residential use. Major portions of the urbanized areas in the region are
characterized by single-family tract housing, strip commercial develop-
ments and a substantial freeway network. The recent decades have shown
circumferential development in all directions from the Denver Metropoli-
tan Area, served by upgraded arterials and new highways. The influence
of transportation on land use choices interact through one or more of
the following factors: site opportunities for development; population
density; accessibility of facilities, services, employment, and community
amenities; travel time requirements and costs. Generally, for the Denver
region, land use patterns have developed in response to the automobile.
Nevertheless, the center of Denver, near the State Capitol, creates one
25
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of several high intensity development areas within the City. Others are
focused on universities. Federal employment areas, and shopping districts.
The major characteristic of the region, however, is its low growth den-
sity and dispersed development pattern. Current land use patterns,
therefore, result in a wide spatial separation between home, employment,
schools, shopping areas, recreational facilities and other activities.
At the present time the automobile dominates as a flexible and speedy
method of personal transportation to meet trip requirements of the
residents.
A recent inventory of zoning in the Denver SMSA shows 19 percent or
nearly one-fifth of the land zoned for residential use. Although 61 per-
cent of the land in the region is still zoned for agriculture, the trend
is for rezoning to higher use (residential, commercial, industrial, and
recreational). Figure 9 illustrates the existing and projected change
in various economic activities for the Denver region.
The distribution of land uses in the Denver CBD and urbanized regions of
the study area reflects the governmental, financial, service, and dis-
tribution functions that the urban centers perform for the metropolitan
area and the larger Rocky Mountain region. Downtown Denver is not a
manufacturing center, but rather the keystone of business and government,
devoted to the distribution and exchange of goods, money and ideas. In
decreasing order of importance, office space, hotels and motels, retail
activity, and governmental facilities are the primary land uses in the
Denver CBD, followed by residential, storage, commercial services, and
industrial uses.
For the Denver SMSA, as a whole, commercial and industrial land uses
have developed in a dispersion pattern around the urban centers. Com-
mercial growth is mainly attributable to the development of various
26
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AGRICULTURE
1964 - 1970
1970 - 1980
MINING
CONSTRUCTION
MANUFACTURING
TRANSPORTATION,
COMMUNICATIONS,
PUBLIC UTILITIES
WHOLESALE & RETAIL
TRADE
FINANCE, INSURANCE
& REAL ESTATE
SERVICES
GOVERNMENT
2 1
Minus
3 4
Plus
Figure 9. Annual growth rates for economic activity showing
land use development potential, Denver region*
t
Source: Denver Region Council of Governments
27
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neighborhood and regional shopping centers. There has been a con-
tinued dispersion of new industrial development, while diverse changes
are evident in the services, parks and public land uses. New develop-
ment and growth potential will depend upon available vacant space,
transportation accessibility, costs, availability of water resources
and related factors. Land use planning and zoning activities have
varied in the region's areas. Denver and Aurora, for example, have
aggressive annexation policies and promote higher use development of
vacant lands through their zoning regulations. Figures 10 and 11
illustrate the 1970 and projected 1980 land use development densities,
thereby mapping the pattern of change and areas with growth potential.
The land use in Larimer and Weld counties is principally cropland,
rangeland, and woodland. Centered in these two counties is the Poudre
Triangle, comprising about 87» of the total area of 18,021 square
kilometers (6,957 square miles) yet containing the major cities of
Fort Collins, Loveland, and Greeley. Even within this more urbanized
region, only a small portion of the land is assigned to residential,
commercial, or industrial uses.
Of the 1,334 square kilometers (515 square miles) surveyed in the
Poudre Triangle for determination of land use in 1970, seven categories
accounted for 96 percent of the total study area. These included un-
gated farming, dry-farming, pasture and grazing, vacant land, single-
family residential areas, water surfaces, and educational land. Of
these, the overwhelming single class is irrigated farming which comprised
two-thirds of all the land surveyed. Total residential land was 4.2
percent, commercial-institutional land comprised 0.5 percent, and
industrial land was 0.7 percent.
Two important controls on future development in this area currently
exist: zoning and water supply. Most of the mountain region and the
very northern portion of the flatland region in Larimer county is zoned
28
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1970 DEVELOPMENT AREAS
Spicul PurpoM Arm
DENVER REGIONAL COUNCIL OF GOVERNMENTS
Figure 10. Denver Region
29
-------
1980 DEVELOPMENT AREAS
SIMCII! Purpou Arm
DENVER REGIONAL COUNCIL OF GOVERNMENTS
Figure 11. Denver Region
30
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0-Open; i.e., the minimum lot size is ten acres. In addition, any
developer must show that he has enough water rights to, at least
legally, provide the amount of water that will be needed. In the near
term, it is expected that industrial and residential development will
continue to take place on the periphery of the cities and towns in the
area.
Transportation Infrastructure and Use
Most of the pollutants under investigation for the AQMP are a result
of motor vehicle emissions. At present in the Denver AQMSA, the auto-
mobile is the dominant mode of travel. A history of automobile domi-
nance in the region has been accompanied by the construction of a large
highway system comprised of urban freeways and major arteries travers-
ing the region. Current land use patterns exhibit a wide separation
between activity centers - residences, employment, commercial facilities,
recreational activities, schools, etc. - requiring a flexible transport
to meet trip requirements.
Summarizing the transportation facilities and public utilities, the
Denver SMSA is served by eleven major highways, five major railroads,
and eleven interstate airlines. The area also encompases six airports
for general aviation, and one military airport. Numerous interstate
and intrastate bus lines serve the area. A regional public mass
transportation system is currently being designed for the Denver region.
The Denver metropolitan area is characterized by a high growth rate of
motor vehicles (5.2 percent per year) and the highest per capita auto-
mobile registration in the nation, one automobile for every 1.5 persons.
On an average day in 1972 approximately 15 million vehicle-miles of
travel were produced in the Denver urbanized area. The Colorado
Highway Department estimates this figure will increase to 18 million
VMT per day by 1980.
31
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Within the County of Denver, comprising the core of the metropolitan
area, there are approximately 1631 miles of streets operated by the
State and local governments. Based on data supplied by the Transporta-
tion Division of the Denver Department of Public Works, the specific
pattern of highways and operational responsibility are as follows:
• 33.6 miles of freeways
• 32.9 miles under State control
• .7 miles under City control
• 253.8 miles of arterials
• 70.7 miles under State control
• 183.0 miles under City control
• 252.7 miles of collector streets
• All under City control
• 1631 total miles of highway in the
City and County of Denver.
For the Denver region, several statistics may be employed to characterize
the current demand for motor vehicle-based travel, and the stock of
vehicles present to meet this need:
• Regional population
• Denver SMSA (1970): 1,227,529
• Denver SMSA (1973): 1,416,800
• Number of licensed drivers (1970): 767,000
• Number of passenger vehicles (1972) ;
(automobiles, taxis, etc.)
• Denver SMSA: 740,160
• Denver AQCR: 751,256
• Number of trucks and buses (1972):
• Denver SMSA: 157,837
• Denver AQCR: 161,408
32
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• Total number of motor vehicles (1972):
• Denver SMSA: 933,306 (including motorcycles)
• Denver AQCR: 949,602 (including motorcycles)
Various transportation studies have been conducted in the Denver
metropolitan area to provide data input for a comprehensive Joint
Regional Planning Program (JRPP) involving the Colorado Division
of Highways, the Denver Region Council of Governments, and the
Regional Transportation District. The JRPP was formed to develop and
maintain a land development and transportation planning process for the
Denver region. Trip generation, origin-destination patterns, auto-
mobile occupancy rates, and related data have been tabulated to supply
input in the transportation planning process for all modes of travel.
For the Denver metropolitan area, studies by the Colorado Highway
Division reveal:
• Over 3,306,000 person trips are made each day
• These are made in 2,225,000 auto trips with an
average car occupancy of 1.6 persons per
vehicle trip
• Additionally there are approximately 217,000
truck trips used for business and cargo and
122,000 light trips used for private reasons.
Further details on the origin-destination analysis conducted by the
Colorado Division of Highways related to the distribution of private
vehicle trips by purpose and automobile occupancy are provided in
Table 3.
*
Data based on State of Colorado, Motor Vehicle Division, Registration
and Receipts Records, January 1, 1972 to December 31, 1972.
33
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Table 3. MOTOR VEHICLE USAGE IN THE DENVER METROPOLITAN
AREA: DISTRIBUTION OF TRIPS BY PURPOSE, AND
AUTOMOBILE OCCUPANCY
Trip purpose
Home based work trips
Home based shopping trips
Home based personal business trips
Home based recreation trips
Home based passenger service trips
Truck trips (business and cargo)
Non-home based trips
Trips leaving the area
Other3
Percent of
total trips
21.3
11.5
10.0
9.6
9.3
8.9
24.0
3.6
1.8
Automobile occupancy
(persons per car)
1.1
1.8
1.6
2.1
2.1
-
-
-
-
School trips and other minor trip purposes made up the remainder of
reasons for travel.
Bus transit, the primary intra-region mass transit service in the
Denver region, is now only used by a small portion of the region's
population. Estimates range from 2-5 percent of all trips in the
Denver region are presently accounted for by the bus system. A number
of both public and private bus lines operate in the Denver AQMSA, with
the largest system being the Denver Metro Transit (DMT) operated by
the City and County of Denver. In 1971, DMT consisted of 214 buses
while today 242 vehicles are operated during peak demand periods.
Since the City and County of Denver began public operation of the bus
transit system in 1971, ridership has steadily increased, as shown
in Table 4. For the entire County region, DMT satisfies about 75,000
of the estimated 3.3 million daily person trips, but in the Denver
CBD the bus system carries a significant portion of all trips. DMT
reports estimate that more than one-fifth of all CBD-oriented work trips
34
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Table 4. ANNUAL TRANSIT PASSENGERS IN THE,
DENVER METROPOLITAN AREA 1969-74£
Year
1969
1970
1971
1972
1973 (estimated)
1974 (estimated)
Annual passengers
17,951,747
16,264,598
15,784,945
19,174,161
22,000,000
24,000,000
Percent charge over
previous year
-
-9.4
-3.0
21.4
14.7 (estimated)
9.1 (estimated)
Source: Denver Metro Transit
35
-------
are carried on the public transit system. Thus the public takeover and
operation of the bus system in 1971 has resulted in a reversal of the
decline in bus ridership that had been occurring in the previous decade,
and DMT officials estimate that the bus system is absorbing the equiv-
alent of 50 percent of all new Denver CBD-oriented work trips. Further
evidence of transportation system change in the Denver region affecting
future patterns of travel, modal mix, and environmental impacts is evi-
denced by the public acceptance of a greatly expanded public transit
system for the region as proposed by the Regional Transportation Dis-
trict.
In 1969 the State of Colorado created legislation establishing a Regional
Transportation District, charged with developing long range highway and
mass transit plans for transportation to serve the seven-county Denver
region. A regional transportation plan was subsequently developed for
the seven-county District (Denver, Adams, Arapahoe, Douglas, Jefferson,
Boulder and Weld). The proposed system consists of a coordinated com-
bination of several kinds of public transit throughout the region, in-
cluding a Personal Rapid Transit (PRT) rail system, local bus, express
bus, and regional bus service. Public acceptance of the proposed RTD
$1.06 billion plan was demonstrated on 7 September 1973, in a public
referendum approving a sales tax to finance the plan.
The two primary elements of the RTD transit plan include an "Early
Action Program" (EAP) interim component and a 100-mile network of
guideway "Personal Rapid Transit" routes in the most heavily traveled
areas of Denver, Boulder and Greeley to be completed by 1984. The
Early Action Program, relying on bus service, is planned to provide
improved transit service at the earliest possible date following the
successful 7 September referendum, by adding new routes and increasing
the frequency on existing routes. In addition to acquiring the exist-
ing Denver Metro Transit bus system, 115 new buses will be purchased.
The EAP is proposed to provide an increase of about 270 route miles
36
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within the district, representing an increase of about 60 percent in
bus service. Daily bus miles will increase by some 33 percent, to
about 32,000 miles. The RTD plan recognizes the interrelationships
of the various modes of travel in the region and the continued impor-
tance of the automobile as an important means of access to public
transportation. Analysis and development of region wide parking facil-
ities to serve at convenient auto-intercepts and peripheral locations
to the central business areas are integral components of the approved
public transportation plan.
With the private automobile as the dominant mode of travel, parking
facilities have been an important part in the total Denver CBD land use
pattern as shown in Figure 12. In general, the availability of parking
plays a significant role in travel patterns and travel modes, partic-
ularly in highly developed employment and commercial centers. In a
1970 study conducted in the Denver CBD, titled Denver Center City Trans-
portation Project (DCCTP), it was estimated that 17 percent, or ap-
proximately one-fifth, of the total square footage of all land in
the CBD was devoted to off-street parking spaces. A complete parking
inventory contained in this report is provided in Table 5. In more
recent inventory counts of parking in the CBD, the Denver Planning Of-
fices estimate a total of 30,043 spaces in off-street facilities exist
and the Denver Highway Division places the count of on-street metered
spaces at 3800, for a total of 33,843 spaces available to the public.
The Denver Planning Office, in a draft report titled Parking Availability
Within the Central Business District and Peripheral Areas, concludes
that the existing supply of parking appears to be adequate as to both
amount and location. Some deficiencies, however, are noted regarding
the type of facilities and the rate structure as related to the avail-
ability of short-term parking spaces. The Denver Planning Office draft
report, the DCCTR and other recent assessments concur that the existing
adequacy and future parking supply needs are strongly dependent upon
37
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1500 2OOO
FEET
50 NUMBER OF SPACES
PUBLIC LOT
PUBLIC GARAGE
PRIVATE LOT
PRIVATE GARAGE
Source: Arthur D. Little, Inc., et al., Denver Center City Transporta-
tion Project, September 1970
Figure 12. Off-street parking inventory in the Denver Central Business
District, January 1970
38
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the expansion and success of the public transit system. Improved pub-
lic transit both reduces future parking supply needs in the CBD, and
may alter the spatial pattern of need, and the proportion of short and
long term parking available to the public.
In summary, this review of the existing transportation system and short
term development trends has outlined the stock of private vehicles,
modal mix, travel patterns, highway networks, public transit system
evolution and development plans, and availability of support facilities,
such as parking, in the Denver metropolitan area. These factors inter-
act in directing the pattern of transport use and in shaping the mag-
nitude of travel demand in the Denver region. Identification of these
various transportation system components is crucial in blueprinting
transportation control measures designed to maintain air quality in
the Denver AQMSA, and in evaluating control measure trade-offs, com-
munity impacts, potential adjustment patterns that may be induced, and
alternative implementation procedures that may be effectively employed.
SOCIOECONOMIC DESCRIPTION
Transportation control and land use plan measures are designed to re-
duce overall air pollution emissions, thereby enabling the attainment
and maintenance of regional ambient air quality protection of human
health and welfare. Socioeconomic characteristics in regions requir-
ing air quality maintenance plans provide important criteria in eval-
uating the potential effectiveness and applicability of control mea-
sures, and in selection of measures for final plan development. In
addition, these community social, economic, institutional and related
patterns play a dominant role in developing pragmatic procedures for
control plan implementation, and in the continual monitoring of the
cross section of direct and indirect impacts produced by the regula-
tory actions over time.
40
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Socioeconomic data for the Denver AQMSA are presented at this stage
to provide a basis for assessing the magnitude and distribution of
potential impacts emanating from the control plan. This involves a
performance impact evaluation of the control plan actions on air qual-
ity improvement, and assessment of the broader set of social and
economic community impacts that occur irrespective of intended im-
pacts on air quality.
In obtaining the primary air pollution reduction objective, some con-
trol measures act directly to reduce vehicular and stationary source
emissions, while other control measures are designed to alter community
behavior patterns, institutional arrangements and lifestyles that in
turn contribute to air pollution emission reductions. (Transportation
control measures designed to reduce VMT are primarily dependent for
their success upon favorable behavioral modifications, which in turn
are dependent upon a sound understanding of community socioeconomic
conditions and trends.)
From a broader perspective the socioeconomic data compiled on the Den-
ver region is needed to evaluate unintended impacts of maintenance
measures proposed for the Denver AQMSA. These potential impacts may
be classified as follows:
• Primary impacts; Social, economic and institution
effects resulting from the outlay of physical and
human resources in control measure implementation.
• Secondary impacts; Social, economic and institutional
effects stemming from or induced by the control mea-
sures, i.e., adjustments made in response to the reg-
ulatory actions.
A broad environmental impact assessment, therefore, identifies the mag-
nitude and distribution of social costs associated with the proposed
regulatory action and provides input criteria for developing implemen-
tation procedures to attain air quality control objectives, minimize
undesirable impacts and promote an equitable distribution of costs
among control plan beneficiaries and pollutant emission sources.
41
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This subsection contains a cross-sectional analysis of the following
socioeconomic conditions that are either directly or indirectly affected
by, and in turn affect the development of a feasible Air Quality Main-
tenance Plan for the Denver AQMSA: population size and spatial dis-
tribution, housing, employment, income, transit dependence, political
structure and related demographic features.
Population
Colorado is ranked as the nation's fifth fastest growing State, with a
statewide population increase of 25.8 percent in the 1960-1970 decade
(annual growth of 2.3 percent). The Denver region's population has
grown at a faster pace in the past three decades, ranging from 3 to
4.6 percent per year, with over one-half of Colorado's total population
residing in the five county Denver SMSA. The Denver SMSA, encompassing
Adams, Arapahoe, Boulder, Denver and Jefferson Counties, had a 1970 pop-
ulation of 1,227,529. Based on population gains through mid-1973, the
Denver Regional Council of Governments (DRCOG) estimates the current SMSA
population to be approximately 1,416,800.
Denver County contained over 50 percent of the total metropolitan Den-
ver population in 1960, but it is estimated that by the year 2000
it will only retain about 25 percent of the total. Population is de-
creasing in the central city as urban sprawl moves to the north and
south along the front range (Figure 13). The suburban communities
accounted for approximately 80 percent of the area's population in-
crease between 1950 and 1970. Based on estimates of the Colorado State
Planning Office, Figure 14 shows the proportion of the Colorado popula-
tion increase expected to be attributable to the Denver Metropolitan
area and the Colorado Front Range Corridor east of the Rocky Mountains
from Wyoming to New Mexico through the year 2000. While the Front
Range area and metropolitan Denver are projected to experience explo-
sive growth, the rest of the State's population may stabilize or de-
cline.
42
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The major components of population change for the Denver urbanized
area include natural increase through increased births, and net mi-
gration. Of the two, net migration, or the difference between those
coming into the area and those leaving, has been the most important.
Both rural-urban migration and the relative stability of Denver's
economy are cited as primary contributing factors for the large flux
of the residents.
Density of population in the Denver central city, in 1970, was 7,602
per square mile and 198 beyond the central city. In general, this is
a low suburban density and is partially because Denver is relatively
isolated from other major cities. Additionally, people have shown a
preference for open space in the metropolitan area, supported by the
high mobility afforded by the automotive-dominant transportation sys-
tem and extensive highway network. The overriding characteristic of
the region is this low population density and dispersed growth pattern.
The current patterns of sprawling low density suburban areas have con-
tributed to planning difficulties in mass transit system development
and regional dependence on private automobile travel.
Growth in Larimer and Weld Counties has been made more dramatic, es-
pecially for their major cities. While the growth rate has been fairly
consistent in the past, the recent trend has been an acceleration of
growth. Between I960 and 1970 Fort Collins had a 73.2 percent rate
of increase, Loveland had a 66.6 percent increase, and Greeley had an
increase of 47.8 percent. It should be noted that the two cities that
increased the most between 1960 and 1970 were both located in Larimer
County, which itself underwent a growth of 68.5 percent over the pre-
vious decade. Weld County, as a whole, only had a growth rate of
23.4 percent during the same time period, which is less than that for
the entire State and indicates a slow rate of increase in population
in the rural districts. Data relating to the past growth of population
in these two counties is presented in Table 6.
45
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Table 6. POPULATION IN LARIMER AND WELD COUNTIES, 1940-1970C
County
Larimer
Weld
Area
Urban
Rural
Fort Collins
Love land
Urban
Rural
Greeley
1940
N/A
N/A
N/A
12,251
6,145
N/A
N/A
N/A
15,995
1950
43,554
21,710
21,844
14,937
6,773
67,504
20,354
47,150
20,354
1960
53,343
34,761
18,582
25,027
9,734
72,344
26,314
46,030
26,314
1970
89,900
59,557
30,343
43,337
16,220
89,297
41,472
47,825
38,902
Growth rate
1960-1970
1.685
1.713
1.633
1.732
1.666
1.234
1.576
1.039
1.478
N/A - Data not available
Source: MacPhail, D.D., "Land Use Patterns, Practices, and Prob-
lems in the Poudre Triangle of Northern Colorado," University of
Colorado.
Projections of population for Larimer and Weld Counties have been made
to the year 2,000, based on migration and natural increase. These
projections are given in Table 7. These projections indicate a de-
creased population growth rate for Larimer County but an increase in
the growth rate of Weld County. A major factor influencing the
growth in Weld County after 1970 is an expected increased migration
of persons to the area as a result of increased employment potentials
in the City of Windsor.
Housing
The Denver SMSA has a strong single-family housing structure tradition,
with single-family homes comprising from 65 percent of all housing
units in Denver County to 88 percent in Adams County in 1970, or an
urbanized area average of 75 percent. Projections of housing stock
for Denver indicate that single-family homes will continue to capture
approximately half the new housing units with an increased trend toward
46
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Table 7. PROJECTED POPULATION IN LARIMER AND WELD COUNTIES 1970-2000'
County
Larimer
Weld
Area
Ft. Collins
(Ft. Collins Area)
Love land
(Loveland Area)
Unincorporated
and rural areas
Greeley
(Greeley Area)
Windsor
Unincorporated
and rural areas
1970
89,900
43,337
(48,000)
16,220
(20,000)
16,086
89,297
38,902
42,000
1,564
28,760
1980
135,000
65,000
(70,000)
25,000
(28,000)
24,800
125,000
55,000
60,000
8,000
31,685
1985b
167,500
77,500
(85,000)
31,500
34,000
29,775
152,500
65,000
70,000
12,500
31,500
1990
200,000
90,000
(100,000)
38 ,000
(40 ,000)
34,750
180 ,000
75 ,000
80,000
17,000
31,315
Source: Larimer-Weld Regional Planning Commission
1985 data is derived on a linear interpolation between the population
in 1980 and 1990
47
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low-rise, multiple-unit complexes and cluster-type developments. This
development breakdown is sensitive to a wide range of economic, social
and service related factors including transportation accessibility.
Low density and dispersed residential development patterns character-
izing the regions are expected to continue with circumferential growth
occurring from city centers and radial growth along transportation cor-
ridors. Other housing trends, such as a declining number of persons
per housing unit and popularity of low density residences, are expected
to continue based on existing trends, economic forces and social atti-
tudes. These residence patterns are crucial in regional development
planning, public transit system development and selecting transporta-
tion control measures designed to alter travel patterns to attain a
shift in modal mix that both meets transit needs and minimizes air
pollution and other environmental degradation.
Employment
The metropolitan Denver region has shown relatively healthy economic
performance in the past decade, with total employment in the region
increasing by 30 percent between 1964 and 1970. This represents an
annual compound growth rate of 4.5 percent per year. The 1970 labor
force for the area was approximately 550,000,with 26,000 employed by
the Federal Government. In addition to the large Federal labor force,
the Denver region also contains large State and local government
labor forces (City and County employees) since Denver is the principal
governmental and political center in Colorado. This large work force,
under direct government control, characterizing the Denver region may
be an important feature influencing the applicability and potential
effectiveness of various control measures such as staggered work hours
and carpooling that require transport system user cooperation.
48
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Based on analysis of industrial groups and employment trends, the Den-
ver Regional Council of Governments (DRCOG) has projected employment
growth trends by industry group to the year 2000 for the metropolitan
Denver area. Figure 15 displays the present industrial group employ-
ment mix and projected growth trends by DRCOG. Table 8 provides the
forecasted annual rates of employment growth for the Denver region by
industrial type. These employment growth projections show that higher
than average total employment growth will be experienced by three in-
dustries: (1) finance, insurance and real estate, (2) services, and
(3) government. Approximately average growth will occur in industries:
(1) construction, and (2) wholesale and retail trade. Employment
growth rates of two industrial groups will be consistently below the
rate of growth in total employment: (1) manufacturing, and (2) trans-
portation, communications and utilities. One industry, agriculture,
however, is projected to have a negative growth rate.
Approximately two-thirds of the employment growth between 1964 and
1970 occurred in Denver County, while about 95 percent of the popula-
tion growth was in surrounding counties. This indicates an inward
work trip transportation flow for the region. Figures 18 and 19 show
the 1970 and projected 1980 employment density mapping for the Denver
region. The density pattern illustrates that employment will not dis-
perse significantly through the region, but will continue to be con-
centrated in the core region, thus requiring continued commuter traffic.
Some services have followed the residential development in the suburbs,
but as yet no clear proliferation of industrial development is apparent.
Based on a census week in 1970, only 4.2 percent of the workers in the
Denver SMSA traveled to work on public transportation. The majority
of the workers, 74.8 percent, drove private automobiles while 10.4 per-
cent were passengers in private autos, and 8.5 percent walked to or
from their place of work. Table 9 summarizes this census data on
means of transportation to place of work.
49
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Table 8. FORECASTED ANNUAL RATES OF EMPLOYMENT
GROWTH, METROPOLITAN DENVER 1970-2000
Industry category
Agriculture
Mining
Contract construction
Manufacturing
Transportation, communication
and public utilities
Wholesale and retail trade
Finance, insurance and real
estate
Services
Government
Total
Forecasted annual rate of growth
1970-1980
(%)
-0.8
0.2
3.2
2.8
2.7
3.0
3.8
3.4
3.6
3.1
1980-1990
f/\
\ lo)
-1.1
0.4
2.4
2.2
2.7
2.3
2.8
2.6
2.7
2.4
1990-2000
(%)
-1.6
0.4
1.9
1.7
1.6
1.8
2.1
2.2
2.4
2.0
Source: The Denver Regional Council of Governments
51
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1970 TOTAL EMPLOYMENT
0 - 1,499
1,500 - 3,999
4,000 - 7,499
7,500- IOO.OOO
DENVER REGIONAL COUHOL OF GOVERNMENTS
Figure 16. 1970 Employment density per acre
52
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1980 TOTAL EMPLOYMENT
0 - 1,499
1,500 - 3,999
4,000-7,499
7,500- KX>,OOO
DENVER REGIONAL COUNCIL OF GOVERNMENTS
Figure 17. 1980 Employment density per acre
53
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Table 9. MEANS OF TRANSPORTATION TO PLACE OF WORK IN
THE DENVER SMSA
Transit mode
Private auto (driver)
Private auto (passenger)
Bus, streetcar, or rail
Walked to work/and home
Other
Worker
responses
369,130
51,418
20,675
41,919
10,424
7» of
Total
74.8
10.4
4.2
8.5
2.1
Employment in the Denver CBD is primarily "white-collar" managers,
executives, professionals, and clerical workers from the governmental,
finance, service, and distributive type industries. The larger manu-
facturing complexes are away from the central area. "Blue collar"
employment centers are dispersed throughout the Metropolitan area with
medium and small-size firms within the central city. Many blue collar
and unskilled jobs are relatively near to trans it-dependent areas in
actual miles, but are beyond normal commuting distances of the existing
public transit services or are served by an indirect system of
circuitous and time-consuming transfers.
Other Socio-Economic Characteristics
Numerous factors affect an individual's choice of travel mode, frequency
of trip generation and origin-destination patterns. Age distribution,
race, and income are important variables in assessing the impact of
control measures on transportation demand behavior patterns, and in
identifying the distribution of social and economic impacts implied by
alternative control plan measures. These demographic characteristics
are summarized for the Denver SMSA population in Table 10 and are
briefly discussed below.
54
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Table 10. DEMOGRAPHIC CHARACTERISTICS FOR THE DENVER
STANDARD METROPOLITAN STATISTICAL AREA,
1970
Income
($) Family income class
< 3,743 (poverty)
< 4,999
5 - 14,999
>15,000
MEDIAN FAMILY INCOME = 10,777
Family total
20,572
43,172
185,713
75,580
Percent of total
6.8
14.2
61.0
25.0
Population age distribution
Age class
<15
<19
20-54
>55
>65
Number of persons
362,195
477,904
564,078
185,547
95,046
Percent of total
29.5
38.9
46.0
15.1
7.7
Population with minority groups
Group category
White3
Spanish Surname
Black
Other
Total
Number of persons
1,021,447
138,928
50,164
16,990
1,227,529
Percent of total
83.2
11.3
4.1
1.4
100.0
Without Spanish surname
55
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Income and Economic Stability - In 1969 the median income within the
Denver Central City was $9,654 and $10,777 for the metropolitan area as
a whole. Households in the Denver SMSA with income over $15,000
included 25 percent of the total, while 6.8 percent of the SMSA families
had income below the poverty level in 1969. Of those families below
the poverty level, 24.6 percent were receiving public assistance income.
The rural areas of the State of Colorado are less well off. The per
capita adjusted gross income in 1970 was $3,129 in the Denver metropoli-
tan communities, while it was $2,152 for the rest of the state. The
percent of families below the poverty level in Larimer and Weld Counties
was 9.4 and 11.9, respectively, and the median incomes were less than
the average for the state.
Age Distribution - The 1970 Denver SMSA population age distribution shows
a large and growing proportion of the residents in the younger age
groups. In the younger age category, 29.5 percent of the population is
less than 15 years of age. At the opposite end of the age spectrum 15.1
percent of the Denver population is older than 55, with 7.7 percent
being older than 65 years. While the younger age groups are not so
dominant in Larimer and Weld Counties, they still comprise over 25
percent of the population.
Minority Group Population Trends - For the five county Denver Metropoli-
tan region, 4.1 percent of the 1970 population base was black and 11.3
percent had Spanish surnames in 1970. The growth trend from 1960 to 1970
shows a 23 percent increase in the white population, 59 percent increase
in persons of the Negro race, and 132.5 percent increase in persons
with Spanish surnames. Larimer and Weld Counties have less than 2 per-
cent non-white population. Figure 18 illustrates the geographic dis-
tribution of minority groups in the metropolitan area, with highest
densities occurring in the central city regions.
56
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;,;.:::.;::".:l *Source: Denver Regional Council
-"
-
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Transit-Dependent Population - The transit-dependent population is
generally composed of individuals from the following interrelated
sectors: low income, minorities, elderly, young, and students. In
the Denver region, transit-dependent groups include people too old
or too young to drive cars or too poor to maintain an automobile or
provide enough car service to meet all of the household's transit
needs.
The greatest concentration of transit-dependent people in the Denver
region is in a 28 square mile area including the Denver CBD, the area
to the north, and the Five Points area, housing nearly 170,000 people.
Travel via present public transit to employment is, on an average,
3.5 times longer than the same trip by car according to RTD studies.
In addition, public transit provides minimal off-peak service. Pro-
posed improvement in the public transportation services will there-
fore incur differential impacts in the Denver AQMSA based on local
economic conditions, the composition and spatial distribution of pop-
ulation subgroups, and behavioral responses to changes in travel
opportunities.
AIR QUALITY AND PLANNING AGENCIES
There are many agencies in the State of Colorado which are directly or
indirectly concerned with the maintenance of air quality. These agen-
cies range from the state's Air Pollution Control Division to local
planning boards. Those which are most actively involved in the devel-
opment, implementation, and enforcement of air pollution maintenance
strategies in the Denver AQMSA are briefly discussed below.
Colorado Air Pollution Control Commission
The Colorado Air Pollution Control Act of 1970 (Appendix B) created the
nine-member Colorado Air Pollution Control Commission to develop an ef-
fective air pollution control program and promulgate such regulations as
58
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may be necessary or desirable to "achieve the maximum practical degree
of air purity in every portion of the state." Eight members of the Com-
mission are appointed by the governor with the consent of the Senate for
a term of three years and the other member is from the State Board of
Health.
The duties of the Air Pollution Control Commission include the develop-
ment and maintenance of a comprehensive program for prevention, control,
and abatement of air pollution throughout the entire state, including a
program for control of emissions from all significant sources of air pol-
lution; the promulgation of ambient air goals for every portion of the
state; the adoption and promulgation of ambient air quality standards and
emission control regulations; the receipt and, at its discretion, the
hearing and determination of violations and applications for the granting
of variances; and, at its discretion, the review of any variance order or
determination of the variance board to which such applications may have
been transmitted. The Commission must also hold a joint meeting with the
State Board of Health during the month of October of each year in order to
hear public comment on air pollution problems within the state and to
answer questions from the public concerning the administration and enforce-
ment of promulgated rules and regulations.
The Air Pollution Control Commission currently has on its staff a technical
secretary, a health educator, and a principal clerk-stenographer. The
budget (FY 1974) for the Commission, its staff, and the Variance Board, is
$84,898.
Colorado Air Pollution Control Division
The Colorado Air Pollution Control Act of 1970 also established a division
within the Department of Health to administer and enforce the air pollution
control programs adopted by the Commission. Specifically, the Division is
empowered to conduct studies and research with respect to air pollution,
including the control, abatement, or prevention thereof; determine if the
59
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ambient air standards are being violated in any area of the state;
enter and inspect any property, premise, or place for the purpose of
investigating any actual, suspected, or potential source of air pollu-
tion; furnish technical advice and services; notify any affected juris-
diction of standards which are not being met; and to issue contaminant
emission notices. The Division also has the authority to enforce com-
pliance with the promulgated emission control regulations.
The Department of Health, within which the Air Pollution Control Divi-
sion was established, is designated as the "state agency" for all pur-
poses of the Federal Glean Air Act, as amended, and regulations pro-
mulgated under that act. The Department of Health accepts and super-
vises the administration of loans and grants from the Federal government
(and from other sources, public or private) which are received by the
state for air pollution control purposes.
An organizational chart for the Air Pollution Control Division is pre-
sented in Figure 19. Current staffing levels and the budget (FY 1974)
are presented in Table 11.
Colorado Division of Planning
The Division of Planning serves as an advisory and coordinating agency
with no regulatory authority. It was created within the Department of
Local Affairs to, among other things, prepare planning "for meeting prob-
lems in the areas of highways, air and water pollution, water supplies,
sewage disposal, recreation, urban and nonurban growth, transportation,
education; industrial and commercial development, and related matters."
The duties of the Division of Planning are primarily those of assistance
in the gathering and using of data. It also helps to coordinate the
planning activities of other departments or agencies, at the state and
local level, to ensure a degree of harmony. The population statistics,
estimates, and projections prepared, maintained, and interpretated by the
60
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Division of Planning are designated as the official data. Besides the
compilation of such demographic data, it must also prepare and periodi-
cally revise an inventory of the public and private natural resources,
major public and private works, and other facilities and information
deemed to be important for the planning and development activities of the
state.
The Division of Planning's primary input to the development and implementa-
tion of an air quality maintenance plan, aside from the use of its data,
is the use of its function as the A-95 clearinghouse. It therefore has
the responsibility of identifying appropriate state and local environ-
mental agencies which should be made aware of a proposed project for which
a Federal grant is being requested and regulating their input. This
Project Notification and Review System focuses on coordination at the
beginning of a project application process and provides an early warning
before positions and viewpoints have been solidified. Its significance
for air quality maintenance planning is that it provides a structure for
improving comprehensive planning and strengthens the communication be-
tween agencies and different government levels.
All master or zoning plans, prepared by any region, county, or district
planning commission, must be submitted to the Division of Planning before
their adoption or certification. The Division of Planning reviews each
plan and presents its advice or criticism; however, the planning com-
mission submitting such plan is not bound by the advice or criticism,
which is considered to be advisory only.
Colorado Land Use Commission
The Colorado Land Use Act established, within the Office of the Governor,
the Colorado Land Use Commission in order to provide the leadership
necessary to encourage planned and orderly land use development. To
fulfill this responsibility, for the past three years the Land Use Com-
mission has been working to identify a program that will provide a
63
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framework and a process whereby the State of Colorado and its various
political subdivisions can guide future development. This has cul-
minated in a report entitled, "A Land Use Program for Colorado", which is
discussed, as it relates to air quality maintenance planning, below.
In fulfilling its mandate, the Commission identified five regions con-
sisting of groups of counties which demonstrate similar dominant charac-
teristics and problems. Of particular interest to this AQMP is the Front
Range Land Use Planning Region which includes the AQMSA and Teller, El
Paso, and Pueblo Counties. The Commission also identified four sub-
stantive arenas which are inseparable from land-use questions--environ-
ment, economics and population, natural resources, and social concerns;
defined goals and targets in each of these arenas, working in consulta-
tion with various interest groups all over the State; agreed upon general
policies to guide the land-use program; developed programs in each of the
four broad arenas, for each of the five regions and for the State as a
whole; and considered what legislation, organizational mechanisms, and
implementation actions are needed to carry out the Commission's land-use
program recommendations.
Given the diversity of regional needs, the Commission had to formulate a
set of goals for the State, reflecting regional diversity yet providing a
focus for a statewide land-use policy. The Commission first formulated
broad goals, and then outlined targets (what ought to be done, where and
by when) and policies (who ought to do what, and how). Next came the
consideration and adoption of program elements (the tools for carrying out
the policies), and finally the development of an organizational structure
and a set of short- and long-term strategies. The Commission adopted
goals for four of the major arenas related to land use.
64
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Land-use goals relating to the environment were identified as follows:
1. Control development to conserve natural environmental
amenities, including air and water.
2. Control development in hazardous or environmentally
fragile areas.
3. Provide adequate recreation opportunities.
4. Conserve areas of scenic beauty or special interest.
With respect to economic development and population in the Front Range
Land Use Planning Region a goal of encouraging moderate growth was
established. To moderate economic and population growth in the Front
Range Land Use Planning Region and to attract new growth to other parts
of the State, the Commission recommends a combination of incentives and
disincentives, to be introduced in connection with the "growth centers"
concept. Growth centers would be designated by the regions in consul-
tation with the State Land Use Agency, the Division of Commerce and
Development, and other agencies that will play a key role in their
development (e.g., Highways and Budget).
The goals for the environment and for economic and population growth are
considered to be the mainspring of State land-use policy while goals for
natural resources and social concerns support the two primary sets of
goals. Principal goals for natural resources are to:
1. Establish a State energy policy with respect to mining and
energy-using development.
2. Develop fuel and non-fuel minerals in a manner which is
compatible with environmental goals and which furthers
economic growth (particularly in the Northwest).
3. Initiate measures to inhibit land uses which result in the
unnecessary conversion of prime agricultural land.
4. Establish a State forest policy.
5. Encourage effective and rational use of the State's water
resources.
65
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Land-use related social goals are to:
1. Provide for explicit analysis of social implications and
impacts of public or major private land-use decisions,
as in provision of and access to health, educational,
recreational, housing, and employment opportunity.
2. Provide adequate access to services and provision of
housing and employment for indigenous and/or disadvantaged
populations impacted by public or private land-use decisions.
3. Ensure opportunity for preservation of cultural heritage
where threatened by public or major private land-use
decisions.
Each goal is further supported by one or more targets which express inter-
mediate goals of highest priority, with greater specificity and a time
frame for implementation.
The development and adoption of these types of land-use-related goals and
targets is the first step in defining a land-use planning program for air
quality maintenance planning. The statement of goals in these broad
areas--environment, economic and population development, natural resources,
and social concerns—becomes the initial guidance for developing programs
at the State, regional, and local levels.
Of particular interest to the development of an air quality maintenance
plan is the program outlined for the environment. The Commission recom-
mended a three-pronged approach to the achievement of environmental goals.
As a first element, environmental inventories would be prepared and plans
made that reflect the location of significant natural amenities and
ecosystems, as well as scenic, cultural, and historic resources. The iden-
tification of these critical environmental areas will, in turn, guide the
administration of land-use and environmental regulatory programs, including
a new development permit system.
A development permit system would apply to all developments located in
areas of critical environmental concern and to proposed activities of
66
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regional or State significance. The granting of a permit will be the
function of regional permit boards within the five regions of the State,
with appeals to a State Permit Review Board. The criteria for determining
when a permit is needed, whether it should be granted and what restrictions
or conditions should be attached to it will thus be responsive to regional
differences. Permit decisions will reflect a comprehensive review of the
proposed development's effects on the environment, public services, and
existing public infrastructure. Public hearings on permits will be con-
ducted at the regional level, with an opportunity for citizen participa-
tion. This permit system, along with strengthening of local land-use
controls, and improvements in state regulation of environmental quality,
make up the second element in the recommended environmental strategy.
The third element looks toward the creation of a Special Land Agency, a
state-owned corporation empowered to acquire environmentally critical
lands, or partial interests in these lands, such as scenic easements, and
to help provide accessible recreational opportunities for Coloradans. In
urban and urbanizing areas, the Commission suggests the creation of linear
parks along rivers and streams or other environmental corridors. Such
parks would preserve both shorelines and other environmental qualities.
They would also provide a variety of recreational opportunities closer to
major population centers. The concept of linear parks could also be ap-
plied on a larger scale to control strip development, especially in
mountain valleys, so as to preserve or restore the environment while pro-
moting access to public recreational lands. The Special Land Agency,
besides pursuing these important environmental goals, could begin to inter-
vene in the land market to provide inducements for orderly growth. The
Special Land Agency could also exchange or transfer land that the federal
government decides to dispose of.
67
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Joint Regional Planning Program - Denver SMSA
The Denver Metropolitan region is Colorado's major urbanized area. The
Denver Standard Metropolitan Statistical Area (SMSA) consists of more than
200 political entities, located in, and including, the counties of Adams,
Arapahoe, Boulder, Denver, and Jefferson. Included are municipalities,
school districts, sewage districts, water districts, park and recreation
districts, fire districts, and other special purpose districts. The re-
sponsible agency for comprehensive planning in the Denver SMSA is the
Denver Regional Council of Governments. The responsibility for continuing,
comprehensive, and cooperative transportation planning rests with the Joint
Regional Planning Program (JRPP). The JRPP is a cooperative transportation
planning effort carried out jointly by the Denver Regional Council of
Governments (DRCOG), the Regional Transportation District (RTD), and the
Colorado Division of Highways (CDH).
Consistent with its role as intergovernmental coordinator for the SMSA
region, the Council of Governments coordinates the joint planning effort
with federal, state and local units and agencies of governments. In
carrying out this role, the Council makes application for federal assis-
tance to the planning program, coordinates the planning program with
planning for all modes of transportation, coordinates the needs and
findings of the planning program with units of local government, co-
ordinates with state planning efforts, and, upon adoption, certifies the
land use and public transportation plans to the federal government. Gen-
eral policy guidelines are established cooperatively by the policy bodies
of each agency. The staffs of the Council of Governments, the Regional
Transportation District, and the Colorado Division of Highways have re-
sponsibility for management and control of the planning elements and tasks
assigned to their respective agencies. Specific planning responsibilities
of the agencies are outlined below.
68
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Denver Regional Council of Governments Activities - Those activities of
the Denver Regional Council of Governments which are instrumental in the
Joint Regional Planning Program are detailed below:
Comprehensive Planning Information - Preparation of regional
goals and objectives, estimates and projections of population
counts and characteristics, socioeconomic/employment informa-
tion, land use, identification of natural and man-made physical
characteristics influencing regional development, identifica-
tion and projection of community facilities and service re-
quirements, and preparation of land development criteria and
standards.
Urban Development Plans - Preparation, analysis, and evalua-
tion of regional development plans based upon alternative
development policies.
Joint Development with RTD and CDH of Transportation Plans -
Preparation of transportation information, development of
travel pattern data, preparation and evaluation of transporta-
tion models, preparation of transportation system criteria
and standards, forecasts of regional travel demand, prepara-
tion and testing of alternative transportation corridors, and
evaluation and selection of highway and public transportation
plans.
Continuing Development of Short and Long Range Plans and
Planning Information - Continuing development and analysis of
indicators of regional growth and change; coordination of
planning program findings with public transportation operators
and with the Colorado Division of Highways; monitoring of public
action programs which may affect the planning program and de-
velopment of short-range highway transportation plans which,
combined with short-range public transportation improvements,
will tend to raise the overall level of transportation service
in the region.
Regional Transportation District Activities - These activities are listed
below:
Joint Development with DRCOG and CDH of Transportation Plans -
Preparation of public transportation information, development
of travel pattern data, preparation and evaluation of trans-
portation models, preparation of transportation system criteria
and standards, forecasts of regional travel demand, preparation
and testing of alternative transportation corridors, and evalua-
tion and selection of public transportation plans.
69
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Detailed Long-Range Public Transportation System Plans -
Estimates of system usage, line and station location studies,
preliminary vehicle design, preparation of operating plans,
preliminary engineering studies, detailed cost-benefit analy-
sis, preparation of capital and operating cost estimates, and
architectural and urban design studies.
Implementation Program - Preparation of financial program,
preparation of construction phasing, examination of organiza-
tional and legislative programs, and preparation of a step-
by-step implementation program.
Short Range Improvement Programs - Analysis of present bus
ridership pattern, analysis of present route structure, iden-
tification of proper role for local transit service, analyzing
deficiencies in present service, and preparation of a short-
range public transportation improvement program.
Demonstration Programs - Identification, development and im-
plementation of public transportation demonstration programs
which will aid in ultimate development of the long-range
public transportation plan and serve to demonstrate that modern
public transportation is a viable alternative to automobile
travel.
Public Education Program - Development and implementation of
a community interaction and public information program designed
to insure that any new public transportation plan is responsive
to the needs and desires of the entire community and to provide
for effective citizen participation in the public transportation
planning process.
Community Approval - Sponsorship of public hearings, modifica-
tion of public transportation plans as required, and submission
of a plan for the development, maintenance, and operation of a
public transportation system to the voters of the District.
Implementation of Plan - Upon favorable approval of the electorate
and sale of authorized bonds, unification and operation of exist-
ing public transportation systems as well as construction of new
facilities in accordance with the plan.
Continuing Development of Short and Long Range Plans - Together
with the Council of Governments, continuing preparation of short
and long range plans to meet public transportation needs and re-
quirements of the region.
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Colorado Division of Highways Activities - The activities of the Colorado
Division of Highways related to the Joint Regional Planning Program are
given below:
Joint Development with DRCOG and RTD of Transportation Plans -
Preparation of highway transportation information, development
of travel pattern data, preparation and evaluation of transpor-
tation models, preparation of transportation system criteria
and standards, forecasts of regional travel demand, preparation
and testing of alternative transportation corridors, and evalua-
tion and selection of highway transportation plans.
Continuing Development of Short and Long Range Plans - Together
with the Council of Governments and RTD, continuing preparation
of short and long range plans to meet highway transportation
needs and requirements of the region.
Implementation of Highway Plans - Budgeting, engineering and con-
struction of highway improvements resulting from the cooperative
planning program.
Mechanism for Planning Coordination - There exists a Memorandum of Agree-
ment between the Denver Regional Council of Governments, the Regional
Transportation District and the Colorado Division of Highways, signed on
April 16, 1971, and currently in effect. The Denver Regional Council of
Governments, as the designated areawide planning agency and coordinating
member of the Joint Regional Planning Program, has the capability to
administer and coordinate all transit planning funds. The DRCOG also has
the authority to contract with other agencies to provide and administer
planning monies.
The organizational mechanism for accomplishment of the continuing, com-
prehensive, and coordinated intermodal planning process is illustrated in
Figure 20. Policy for the planning process is established by adoptive
actions of the Denver Regional Council of Governments, the Regional Trans-
portation District Board of Directors, and the Colorado State Highway
Commission. The composition of these policy bodies are as follows:
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RTD BOARD
OF DIRECTORS
DENVER REGIONAI
COUNCIL OF
GOVERNMENTS
HWY. COMM.
AGENCY
DIRECTORS
TECHNICAL
COORDINATION
TEAM
REGIONAL PLAN-
NING ADVISORY
COMMITTEE
JRPP STAFF
RTD
DRCOG
CDH
Figure 20. JRPP: transportation and land use planning structure
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Denver Regional Council of Governments - One county commissioner
from each of the four counties in the region, the mayor and a
city council member from the City and County of Denver, and the
mayor or member of the city council from each of the twenty-eight
incorporated cities and towns within the region.
The Regional Transportation District Board of Directors - Ten
members appointed by the mayor of the City and County of Denver,
and confirmed by the Denver City Council. Two members appointed
from Boulder, Adams, Arapahoe, and Jefferson Counties and con-
firmed by a majority of the municipalities within each county,
one member appointed by the county commissioners of Douglas and
Weld Counties and confirmed by a majority of the municipalities
within these counties, and one "at-large" member selected by the
twenty appointed members of the Board of Directors.
Colorado State Highway Commission - One member from each of eight
districts throughout the state, and one at-large member appointed
by the Governor of the State of Colorado.
These policy boards meet on a regularly scheduled basis. The Denver Re-
gional Council of Governments and the Regional Transportation District
Board of Directors meet monthly, and the Colorado State Highway Commis-
sion meet quarterly.
The highest level of staff involvement in the Joint Regional Planning Pro-
gram is the Committee of Agency Directors. It is composed of the Executive
Directors of the Denver Regional Council of Governments and the Regional
Transportation District, together with the Chief Engineer of the Colorado
Division of Highways. This group meets as frequently as is necessary, but
at least monthly for the purpose of monitoring the planning process,
assuring that the work of the three agencies is carried out effectively,
resolving interagency problems, and preparing policy and plan recom-
mendations .
The Joint Regional Planning Program recognizes that the staff of each
participating agency is responsible to its own agency's policy body; i.e.,
Council of Governments, RTD Board, and the State Highway Commission.
These bodies determine policy within the scope of authority granted them
under State statutes. It is expressly intended that each agency director
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seeks guidance from his own governing body and serves as a link between
his governing body and the cooperative Joint Regional Planning Program.
When conflicts between agencies occur, the Agency Directors, with the
advice of their respective policy bodies, attempt to establish mutually
satisfactory solutions. The Agency Directors are responsible individually
for their agency's activities in support of the Joint Regional Planning
Program, and collectively responsible for assuring that the Joint Regional
Planning Program objectives are met.
Directing the day-to-day staff activities of the Joint Regional Planning
Program is the responsibility of the Technical Coordination Team (TCT).
The Technical Coordination Team is composed of the Program Director for
Transportation and Land Development of the Denver Regional Council of
Governments, the Senior Transportation Planner of the. Regional Transporta-
tion District, and the Transportation Studies Engineer for the Colorado
Division of Highways. It is the responsibility of this team to provide
continuing coordination and liaison between the staffs of the participating
agencies and to maintain the technical competence of the Joint Regional
Planning Program. The TCT meets as frequently as necessary, but at least
weekly throughout the program. Specific functions of the Technical Co-
ordination Team are: making technical decisions, coordinating the ac-
tivities of the three agencies toward accomplishment of objectives, re-
viewing and modifying schedules, preparation and review of work programs,
preparation of periodic progress reports, and resolution of problems.
In order to provide continuing liaison between federal, state, and local
agencies, and provide for effective input of their expertise, concerns,
and desires, the Joint Regional Planning Program has designated the Council
of Governments' Regional Planning Advisory Committee as a technical advisory
committee to the transportation planning process. Voting members of the
Regional Planning Advisory Committee represent the cities and counties of
the region. While membership is not limited to particular professional
disciplines, members are usually city planners or engineers. Also in-
cluded on the committee, in a non-voting, associate capacity, are
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representatives of the Colorado State Planning Division, the State Land
Use Commission, the Division of Highways, the Regional Transportation
District, the Federal Highway Administration, the Department of Housing
and Urban Development, the Bureau of Outdoor Recreation, and the Federal
Aviation Administration. Meetings of the Regional Planning Advisory
Committee are held at least monthly. While the transit operating agencies
of the region are not directly represented on the Regional Planning Ad-
visory Committee, representation is provided through the Committee's two
members from the City and County of Denver.
Local Pollution Control Authorities
Colorado has a very strong interest in maintaining control over local
problems in the jurisdiction of interest. As much as possible, initial
regulatory control is placed in the local authorities with final control
by the state only if necessary. The Colorado Air Pollution Control Act
delegates to the local governmental agencies the authority to enforce the
rules and regulations adopted by the Air Pollution Control Commission.
The local air pollution control authorities in the Denver Air Quality
Maintenance Study Area are listed below:
County Agency Title Location
Adams Tri-County District Health Dept. Englewood
Arapahoe Tri-County District Health Dept. Englewood
Boulder Boulder City-County Health Dept. Boulder
Clear Creek
Denver Denver Dept. of Health and Hospitals Denver
Denver Building Dept. Denver
Douglas Tri-County District Health Dept. Englewood
Gilpin
Jefferson Jefferson County Health Dept. Lakewood
Larimer Larimer County Health Dept. Fort Collins
Weld Weld County Health Dept. Greeley
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Local Planning Commissions
All counties in Colorado must have, and any municipality may have, a
planning commission. Any such planning commission must prepare a com-
prehensive plan (master plan) for its jurisdiction. These plans are then
officially adopted (after public hearings), and must be considered when
decisions are made about certain types of facilities. Generally, however,
the master plan has little legal effect on private actions as there is no
requirement that zoning be in accordance with the community master plan.
In Weld County, however, it is currently the policy to rely on the com-
prehensive plan in zoning decisions. Municipal, but not county, plan-
ning commissions must also review the locations of public thoroughfares,
utilities, and open spaces.
The only regional planning commission which has been created in the
Denver Air Quality Maintenance Study Area, other than the Denver Regional
Council of Governments, is the Larimer-Weld Regional Planning Commission.
The current status of county master plans is summarized in Table 12.
REGIONAL LEGAL AUTHORITY FOR AIR QUALITY CONTROL
As stated in Part 51 of Chapter 40 of the Code of Federal Regulations
(40 CFR 51) under section 51.11 which deals with the legal authority re-
quirements for air quality implementation plan development:
(a) Each plan shall show that the state has legal authority
to carry out the plan, including authority to:
(1) Adopt emission standards and limitations and other
measures necessary for attainment and maintenance
of national standards.
The Colorado State Air Pollution Control Act of 1970 (Appendix B) created
the nine-member Colorado Air Pollution Control Commission. The Act
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Table 12. COUNTY MASTER PLANS
County
Status of plan
Comments
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
In effect - urban portion only
Not yet developed
In effect - some portions of county
Not yet developed
In effect - 1968
Not yet developed
Not yet developed
In effect - some portions of county
Not yet developed
In effect - 1973
About to update,
extend
Boulder City has
own plan
About to start
Parts updated
since
In progress
Old
About to start
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designates the Colorado Department of Health to serve the State for all
purposes of the Federal Clean Air Act, as amended, and to accept and
supervise the administration of loans and grants from the Federal Govern-
ment and other sources received for air pollution purposes. The Com-
mission has the authority to develop and maintain a comprehensive program
for prevention, control, and abatement of air pollution throughout the
entire state including a program for control of all significant sources of
air pollution and authority to promulgate ambient air control plans for
every portion of the state.
(2) Enforce applicable laws, regulations, and standards,
and seek injunctive relief.
Injunctive powers are expressly provided as an enforcement tool and heavy
civil penalties ($2,500 per day for each day of offense) may be levied
upon violation of any final cease or desist order not under judicial review
or failure to file the required air contamination emission notice.
The Division of Administration of the Colorado Department of Health is the
enforcement authority for the emission control regulations promulgated by
the Commission and an Air Pollution Control Division is established.
Local air pollution control agencies are provided with review and enforce-
ment powers.
(3) Abate pollutant emission on an emergency basis
to prevent substantial endangerment to the
health of persons, i.e., authority comparable
to that available to the Administrator under
section 303 of the Act.
The Governor is empowered to declare a state of air pollution emergency
whenever a situation develops that endangers the public health, to curtail
movement of motor vehicles or order a halt or curtail all operations,
activities, processes or conditions that he reasonably believes to be con-
tributing to such an emergency. Injunctive action is also authorized if
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cease and desist orders issued by the division of administration are not
complied with.
(4) Prevent construction, modification, or operation
of a facility, building, structure, or installation,
or combination thereof, which directly or indirectly
results or may result in emission of any air pol-
lutant at any location which will prevent the attain-
ment or maintenance of a national standard.
It is recommended, as part of the Air Quality Maintenance Plan, that the
Colorado Air Pollution Control Act be amended so as to provide the Division
of Air Pollution Control the legal authority necessary to comply with this
*
requirement. Such amendment shall be enacted no later than six months
after the acceptance of this Air Quality Maintenance Plan by the Admin-
instrator of the United States Environmental Protection Agency.
(5) Obtain information necessary to determine whether
air pollution sources are in compliance with ap-
plicable laws, regulations, and standards, in-
cluding authority to require record keeping and
to make inspections and conduct tests of air pol-
lution sources.
The Air Pollution Control Act requires an "air contamination emission
notice" to be filed with the Colorado Department of Health prior to the
emission of an air contaminant from any facility, process, or activity,
except residential structures. An "air contamination emission notice"
must also be filed for any facility, process, or activity which is altered
and results in an increase in emissions of air pollutants.
The division has the duty to enter and inspect any property, premise, or
place, for the purpose of investigating either an actual or a suspected
source of air pollution or air contamination or ascertaining compliance
or noncompliance with any emission standard or any order under this
article.
^Colorado has enacted an amendment providing for control of indirect
sources but it is evidently not sufficient. See Section VI.
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(6) Require owners or operators of stationary sources
to install, maintain, and use emission monitoring
devices and to make periodic reports to the State
on the nature and amounts of emissions from such
stationary sources; also authority for the State
to make such data available to the public as re-
ported and as correlated with any applicable emis-
sion standards or limitations.
The Administrator has delegated to Colorado the authority under Section 114
(a)(l)(B) and (C) of the Clean Air Act to require sources within the State
to install and maintain monitoring equipment and to report periodically
on the nature and amount of their emissions.
LEGAL AUTHORITY FOR LAND USE PLANNING
Recently enacted legislation in Colorado, House Bill No. 1041 (Appen-
dix C), provides for State involvement in matters of State interest re-
garding land use. This law provides that local governments may designate
certain areas (mineral resource areas, natural hazard areas, historical-
archaeological-natural interest areas, or areas around key facilities) or
certain activities (water and sewage treatment systems, solid waste
disposal sites, airports, mass transit facilities, arterial highways and
interchanges, new communities, water projects, and nuclear test sites) as
being of state interest. Such areas or activities must then be adminis-
tered by the local government in accordance with either guidelines pro-
vided by the legislation or by certain state agencies. Detailed guidelines
for administration are to be developed by the local governments. While
this law is limited in scope, it has several features of potential im-
portance to air quality maintenance.
The Colorado Land Use Commission may initiate the process of identifica-
tion, designation, and promulgation of guidelines for matters of state
interest. Normally, local agencies must initiate this process, but the
Land Use Commission may request the local agency to act. The Land Use
Commission also has the power to seek judicial review of local
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designation actions or guidelines. During such proceedings, development
on the area involved is forbidden by statute.
Once a matter of state development is designated, no development involving
that area or activity may occur until guidelines are promulgated and until
a permit is granted by the local government involved. To grant a permit
requires an application and a public hearing. Decisions to grant permits
are subject to judicial review. The Land Use Commission or the local
government may enjoin actions without proper permits.
The Colorado Department of Local Affairs is to conduct a program to en-
courage the preparation of inventories of matters of state interest within
each county and municipality, by 30 June 1976, as part of comprehensive
community plans. Funds have been provided for this planning, and the De-
partment of Local Affairs is authorized to establish standards for the
scope, detail and accuracy of the planning. The Land Use Commission is
also authorized to assist the counties and municipalities in planning for
designation of matters of state interest.
The items to be considered as matters of state interest include several
which can markedly influence development patterns and therefore air quality,
namely: mineral resource areas, public utilities (water supply systems,
sewerage, major facilities for telephone, gas, or electric systems), air-
ports and their surroundings, public transportation facilities and their
surroundings, arterial highways and interchanges and areas around them,
and new communities.
Some of the legislative guidelines for these matters of state interest
will encourage the consideration of air quality in administering them.
For areas around key facilities (which includes airports, utility facil-
ities, highway interchanges, and mass transportation facilities) the
legislation calls for developing them in a manner that will discourage
traffic congestion and will not impose "burdens or deprivation on . . .a
region ..." with only local benefits. Areas around mass transportation
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facilities are to be developed in conformance with the community master
plan. Arterial highways and interchanges and collector highways, and
major facilities of public utilities, are to be located in a manner which
avoids conflicts with master plans.
In addition, House Bill No. 1041 limits uncontrolled growth patterns by
requiring that major extensions of domestic water and sewage treatment
systems be permitted only in those areas in which the anticipated growth
and development can be accommodated within the "environmental capacity"
of the area.
CURRENT EMISSION CONTROL REGULATIONS
As required by Section 66-31-8 of the Colorado Air Pollution Control Act
of 1970, the Colorado Air Pollution Control Commission has adopted a
number of regulations which stipulate control measures for emission and
other measures which help provide for the attainment of the NAAQS. In
addition, the Commission has also adopted ambient air standards for
suspended particulate matter and sulfur dioxide for the Metropolitan
Denver AQCR and the State of Colorado which are more stringent than those
promulgated by EPA. A summary of these standards is given in Table 13.
The intent and purpose of these regulations are stated by the Commission
to be:
To achieve and maintain levels of air quality which will
protect human health and safety, prevent injury to plant
and animal life, prevent damage to property, prevent un-
reasonable interference with the public welfare, preserve
visibility and protect scenic, aesthetic and historic
values of Colorado.
To require the use of all available practical methods to
reduce, prevent, and control air pollution for the pro-
tection of the health, safety, and general welfare of
the people of the State of Colorado. In order to achieve
air purity consistent with this intent it is necessary,
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Table 13. COLORADO AMBIENT AIR STANDARDS FOR SUSPENDED PARTICULATE
MATTER AND SULFUR DIOXIDE (MICROGRAMS PER CUBIC METER -
l-ig/m3)
Pollutant
Suspended particulate
Matter
Short term
Long term"
Sulfur dioxide
One hour level
d
Short term
b
Long term
Non-
designated
areas
150
45
15
(0.0050)
Metro-Denver Air Quality
Control Region, and
designated state areas
1973
200
70
800
(0.28)
300
(0.10)
60
(0.020)
1976
180
55
300
(0.10) -
150
(0.050)
25
(0.0090)
1980
150
45
55
(0.020)
10
(0.0040)
A 24-hour maximum of any 24-hour period and must not be exceeded more
than once in a 12-month period.
An annual arithmetic mean of all 24-hour concentrations.
Q
A 1-hour maximum arithmetic mean in any 24-hour period, and must not
be exceeded more than once in any 1-month period.
A 24-hour maximum arithmetic mean of any 24-hour period, and must
not be exceeded more than once in a 12-month period.
Note: ( ) = Equivalent values in parts per million.
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ultimately, to control air contaminant emissions to such
a degree of opacity so that the emissions are no longer
visible.
3. To prevent significant degradation of Colorado's air
resource.
4. To prevent odors and other air pollution problems which
interfere with the comfortable enjoyment of life.
5. To apply the major resources of the Colorado air pollution
control programs toward solving priority air pollution
problems.
The problem of maintenance of air quality and general environmental
degradation is one which has been called by the Colorado Air Pollution
Control Commission as an area in which comprehensive, coordinative
planning needs to be employed:
The Commission recognizes that the growth in the amount and
complexity of air pollution in Colorado is brought about by
and incident to population growth, mobility, increased af-
fluence, industrial development and changing social values in
said State. The Commission believes that the air pollution
problem is likely to be aggravated and compounded by addi-
tional population growth, mobility, affluence, industrial de-
velopment, and changing social values in the future, which
are likely to result in serious potential danger to the public
and the environment. Therefore, the Commission intends to
pursue solutions, in conjunction with other appropriate agencies
and interests, which have a direct interest and capability in
solving a growing air pollution problem in relation to the
broader environmental degradation problem. It is the intent
of the Commission to coordinate with industrial, commercial,
agricultural and transportation planning organizations, land
use and other environmental organizations, the public, the
legislature, educational organizations, and other major inter-
ests in such a manner as to prevent air pollution in Colorado.
The regulations on emissions of contaminants to the air vary as to their
level of technicality. The control stipulations range from banning of
emissions (e.g., open burning) to opacity to process rates. Some of the
regulations apply generally to control of particular pollutants from
many sources while others apply to specific processes. As one means of
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ensuring compliance with regulations, a permit system is also provided
as well as the regulations for indirect source review promulgated by EPA.
All current regulations are provided in Appendix E and they are briefly
summarized and discussed, as they relate to the pollutants of interest,
below. Some regulations recently proposed by the Colorado Air Pollution
Control Commission are given in Appendix E.
General Review Requirements
Under the Regulation Governing Authority to Construct and Permit to Operate,
Regulation No. 3, "no person shall discharge, or cause to be discharged,
into the atmosphere any air contaminant if an 'air contaminant notice' "
has not been filed. Such air contaminant emission notices specify the lo-
cation at which the proposed emission will occur, the name and address of
the person operating or owning such facility, process, or activity, and an
estimate of the quantity and composition of the expected emission.
Regulation No. 3 also requires that any person planning to construct or
modify any new air contamination source, either with basic process equip-
ment or air pollution control equipment, receive written authorization
from the Air Pollution Control Division. The Division will grant such
authorization if:
a. The new air contamination source is so designed and
will be constructed or modified to operate without
causing a violation of the emission control regula-
tions of the Commission, and any applicable national
or local air pollution emission control ordinances
and regulations.
b. The new air contamination source is designed, built,
and equipped in accordance with the best available
practical methods to reduce, prevent, and control air
pollution.
c. The new air contamination source, as designed or
modified}does not significantly endanger maintenance
or attainment of any ambient air quality standards
of the Commission, and any more stringent national
or local ambient air quality standards.
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In addition, a permit to operate any such new air contamination source
is required to be granted by the Division before the operation of the
equipment. Before a permit to operate is granted, the applicant, if re-
quired by the Division, must conduct performance tests in accordance with
methods approved by the Division with the tests being made at the expense
of the applicant. The Division may monitor such required performance
tests conducted by the applicant and may also conduct performance tests.
Standards for the granting of a permit to operate are:
The emissions of the air contamination source will
satisfy the requirements of the emission control reg-
ulations of the Commission or any applicable national
or local air pollution control ordinances and regula-
tions and has been constructed, installed, or modified
in accordance with the requirements and conditions
contained in the authority to construct or modify.
After January 1, 1975 no existing air contamination
source shall be granted a permit to operate unless
the Division has determined to its satisfaction that
said air contamination source will operate in such a
manner so as not to significantly endanger maintenance
or attainment of any ambient air quality standards of
the Commission, and any more stringent national or
local ambient air quality standards.
The Division may impose conditions upon the applicant in the permit to
operate which require the owners or operators of air contamination sources
to install, maintain, and use instrumentation to monitor and record emis-
sion data as a basis for periodic reports to the Division.
Other review requirements have been assumed by EPA due to the disapproval
of the state plans. As published in the Code of Federal Regulations
(40 CFR 52.22(b)), no construction or modification of designated indirect
sources may be commenced after December 31, 1974, unless approval has
first been obtained from the Administrator of EPA. Approval will not be
given if it is determined that the indirect source will:
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(a) Cause a violation of the control strategy of any ap-
plicable state implementation plan; or
(b) Delay the attainment of the national standards,
for specified pollutants, in any region beyond
the specified attainment date; or
(c) Cause a violation of the national standards,
for specified pollutants, in any region where
the attainment date specified for any such re-
gion will have passed at the time of completion
of the indirect source.
The Colorado Air Pollution Control Commission, while having no direct
regulations for the review of indirect sources, adopted a policy state-
ment on April 26, 1973, resolving:
1. That there be a postponement of the approval of the
construction of new freeways in the Denver area (and
the enlargement of existing freeways) until it has
been demonstrated in environmental impact statements
for such freeways that such freeways will not adversely
affect air quality (both on a short and long term basis)
2. That any new construction of freeways and other "com-
plex air pollution sources" in the Denver metropolitan
area and in other Colorado areas be allowed only when
construction of said sources is not likely to endanger
the achievement or maintenance of ambient air quality
standards.
3. In order to meet Federal ambient air quality standards
on schedule, the Commission estimates that a signifi-
cant decrease of projected vehicle miles traveled will
be necessary in the Denver area. The Commission feels
that automobile traffic should be discouraged while at
the same time less polluting alternate forms of trans-
portation should be encouraged.
4. That the Colorado Legislature recognize the importance
of and pass legislation mandating the joint use of
Land Use and Transportation planning as necessary tools
for the attainment and maintenance of publicly ac-
ceptable levels of air quality by granting sufficient
powers to appropriate agencies for this purpose.
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In addition to these review requirements for construction of indirect
sources, the Commission has adopted, as Regulation No. 6, the Standards
of Performance for New Stationary Sources (40 CFR 60) as set forth and
published in Volume 36, Number 247, Part II of the Federal Register, dated
December 23, 1971.
Current Regulations for Particulate Emissions
The Air Quality Implementation Plan for the State of Colorado based its
control strategy development for suspended particulates on the highest
o
reported annual geometric mean of 122 |ig/m , which occurred in Denver.
This value determined required emission reductions of 51 percent and 67
percent to meet the primary and secondary standards, respectively. The
reduction of 51 percent was to be achieved in part by the application of
Regulation No. 1 with the balance being met by the application of Federal
particulate emission control regulations on automobiles and aircraft.
Federal regulations directed at controlling particulate emissions from
automobiles have not yet been promulgated.
Regulation No. 1, as presented in the SIP, was projected to decrease
stationary source particulate emissions in the Metropolitan Denver AQCR
(the example region) from 18,096 tons/year in 1970 to 8,425 tons/year in
1975, or a reduction of 46 percent. The control measures imposed to
receive this reduction included a general requirement that emissions could
not obscure vision to a degree greater than 20 percent opacity, a ban on
open burning without a permit, and process rate based regulations for
major fuel-burning equipment, refuse-burning equipment, and manufacturing
processes. Control of fugitive dust, at the time of the SIP, was based on
the 20 percent opacity regulation and the need for five or more complaints.
This regulation for fugitive dust has been recently amended and is dis-
cussed below.
The reduction of 67 percent to attain the secondary standard was assumed
to require emission reductions exceeding those which can be achieved
through the application of reasonably available control technology (RACT).
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An 18-month extension was therefore requested, and granted by EPA, in
order to formulate and submit that portion of the SIP.
In searching for particulate emission sources where additional emission
reductions could be demonstrated as part of the plan to achieve the
secondary standard, the Colorado Air Pollution Control Commission identified
fugitive dust from unpaved roads and other sources as contributors to par-
ticulate pollution which were amenable to control. The agency next drafted
regulations designed to provide the best control feasible for the fugitive
dust sources that they had identified. However, due to lack of available
data on (1) emission rates from these sources and (2) the effectiveness of
the proposed regulations in reducing particulate emissions, the Commission
was unable to quantitatively demonstrate that the fugitive dust controls
would result in the necessary reduction in emissions.
To compound this problem of presentation, measured particulate levels at
some sampling sites were increasing with time, rather than decreasing ac-
cording to the projections of the initial implementation plan. This
divergence of actual measurements from projections indicated that the
emission inventory on which the control strategy was based did not account
for all emission sources affecting the samplers.
A study was thus undertaken to quantify the reduction in fugitive dust
emissions that can be expected from enforcement of the proposed regula-
tions and to estimate the resulting air quality in three Colorado Air
Quality Control Regions with these regulations in addition to existing
control regulations.
The emission inventory showed that unpaved roads were the largest source
of particulate, with agriculture being the second largest, these two
sources accounting for 36 and 34 percent, respectively, of the particulate
emissions inventoried. The other seven fugitive dust categories--sanded
paved roads (for snow control), land development, building construction,
highway construction, quarrying/mining, aggregate storage, and cattle
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feedlots--also contributed significant emissions on a regional basis, so
that fugitive dust was responsible for 70 percent of particulate emissions
in the Metro-Denver AQCR and 97 percent in the Pawnee AQCR.
Existing Colorado control regulations for particulate emissions from fuel
combustion, processes, and other sources were reviewed to determine
whether additional emission reductions could be obtained from these sources.
Generally, it was concluded that these regulations represent the best avail-
able technology, and no significant improvements could be epxected over
these allowable emission rates.
Three recommendations were made in an effort to increase the emission re-
ductions attributable to the proposed fugitive dust regulations:
1. Control plans should be required for all unpaved road
segments with traffic densities greater than
20 vehicles/hour, instead of the proposed 30 vehicles/
hour on road segments greater than one-half mile long;
2. The requirements for submitting a control plan should
be modified to insure that all land developments
with unpaved roads must submit a plan; and
3. A program should be instituted for the more rapid and
more complete removal of sand from streets and high-
ways following its application for snow control.
In response to these recommendations, the Colorado Air Pollution Control
Commission has adopted the following measures for unpaved roads in all
problem areas:
1. Dust control of all roads in new developments and
all new parking lots of over 165 vehicles per day
traffic.
2. Paving of existing roads under a plan and time
schedule prepared by County and City authorities
with maximum available funds for that purpose, the
plans to be approved by the Division; and
3. Maximum traffic counts to serve as a guide in
determining paving priorities.
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Road paving is expensive, amounting to about $20,000 a mile for minimum
width two-lane roads. Much testimony has been collected by the Commission
on the limitation of highway user funds and other revenues to pave the
thousands of miles of roads in Colorado air basins. The Commission's plan
calls for maximum possible paving with available funds. The Commission
also recognizes increasing difficulty to acquire asphalt for paving with
the recent shortages in petroleum products.
The regulations of the Commission require, on a case-by-case basis, review
of all development plans of over 5 acres in the critical air pollution
areas. Additionally, the Commission will consider smaller increments of
road cutting, and requirements for road surfacing, and revegetation and
surface treatment. Watering for dust suppression will be required where
water is available. Inherently, earth-moving activities are dusty,
especially where subsurface moisture content is low as in much of the
southwest United States. Control beyond that adopted by the Commission
would most likely severely inhibit land development and construction
activities, an alternative having serious economic implications. It is
the Commission's intent to deny permits only to those development and con-
struction plans which fail to employ all reasonably available air pollution
controls as provided from time to time in Commission regulations and
policy.
Regarding the sand on paved roads, the Commission seriously doubts the
estimate that a 25% reduction of emissions is possible by picking up sand
sooner. The state Department of Highways and Denver County Department of
Highways have informed the Colorado Air Pollution Control Division that,
in their opinion:
1. The sands used are 1/4 inch diameter material on down
in size to very fine material;
2. The sands are mostly comprised of river-run material
and decomposed granite and that;
3. Road crews are removing sand off the streets as soon
as possible now without endangering the flow of traffic.
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Assuming this information to be correct, eliminating or significantly
reducing street sanding would appear to risk human injury and cause
property damage problems, out of proportion to the air pollution benefits.
The recently promulgated regulation regarding control of fugitive dust
(amended Section II-D, Regulation No. 1) is provided in Appendix E and
summarized, with control efficiencies discussed, in Section III.
However, even with these additional provisions, it is still doubtful that
the secondary standards will be achieved in the AQMSA. The major prob-
lems in achieving the standards are the large contribution of fugitive
dust to total particulate emissions in the regions and the low control
efficiencies attainable for most fugitive dust sources. In fact the
3
Federal secondary particulate standard of 150 (ig/m (24 hour) is exceeded
on almost completely undeveloped areas. The high winds in these semi-
arid areas of sparse vegetation are the cause of the violation of stan-
dards due to their uplifting action on the dusty ground cover.
Therefore, the Commission recommended to EPA, in the Colorado Plan for
Federal Secondary Ambient Air Quality Standards, that when wind speeds
exceed 30 mph those situations be exempt from meeting the secondary par-
ticulate matter standard. The Commission concurred with the use of an-
nual geometric mean data as a more reasonable basis for a control plan,
but nevertheless felt meeting the Federal Secondary Standard would have
a devastating effect upon the state.
Current Regulations for Carbon Monoxide Emissions
The discussion of control strategies for carbon monoxide in the Colorado
SIP was based on the second highest 8-hour concentration, measured at the
3
Denver CAMP station and reported as 21.0 mg/m (18.3 ppm), which implied
an emission reduction of 52 percent would be required in order to meet
the national primary and secondary ambient air quality standard of
3
10 mg/m (9 ppm) carbon monoxide (8-hour average). Application of the
92
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Federal emission control regulations for carbon monoxide was assumed to
provide a 23 percent reduction by 1975. Nonmotor vehicle emissions
amounted to 3 percent and were not considered to help achieve the re-
duction required. Since the additional 29 percent reduction was deter-
mined to be achievable only with extreme hardships, as per section
420.30 of the Federal Register, Volume 36, No. 158, a 2-year extension
was requested in order to benefit from the additional degree of Federal
automotive control during the period 1975 to 1977.* The expected im-
provement in air quality in 1977 as the result of Federal automotive
controls was 44 percent. Because this was still insufficient for the
attainment of the standard, it was proposed to promote the formation
of carpools and reserved bus lanes and to have the State Air Pollution
Control Commission publicly oppose any additional large scale parking
facilities in the downtown Denver area. In addition, the implementa-
tion of an annual emission testing program was planned. Such a combin-
ation of strategies appeared at that time to provide a 63 percent emis-
sion reduction for carbon monoxide; however, it was necessary to do
further evaluation of possible control measures.
On January 31, 1973, the U.S. Court of Appeals for the District of
Columbia Circuit ordered EPA to approve or disapprove state transporta-
tion control plans no later than June 15, 1973. Further, a period of
public comment was required after receiving the plan before EPA could
approve a state's plan. Since the Governor of the State of Colorado
originally submitted the "State of Colorado Air Pollution Control Trans-
portation and Land Use Plan" on June 4, 1973, EPA had to publish notice
of disapproval of the plan in the June 22, 1973, Federal Register. This
disapproval was based only upon the lack of timely submittal.
EPA granted a 2-year extension for meeting the CO standard, in the
Denver AQCR only. See 40 CFR 52.322.
93
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A review of the Colorado plan revealed several deficiencies and EPA re-
quested supplemental information. This supplemental information was sub-
mitted by the Governor on July 16, 1973. The plan as finally submitted
was comprised of the following strategies:
1. Semiannual inspection and maintenance program using
the idle test mode to be fully implemented by
December 1, 1975.
2. Air bleed retrofit for pre-1968 vehicles to be fully
implemented by July 1, 1976.
3. High altitude modification and tuning specifications
for 1968-1975 vehicles to be fully implemented by
July 1, 1976.
as well as the following strategies to be implemented by December 1, 1974:
4. Designation of mandatory bus/carpool lanes.
5. Limitation on the construction of future parking
facilities.
6. Removal of on-street parking in the Central
Business District (CBD).
The state also included improvements in public transit and expanded bike-
way development and use to reduce the number of vehicle miles traveled.
EPA's review of this plan showed that additional measures were necessary
to achieve the national ambient air quality standards for carbon monoxide
and photochemical oxidants, and the following measures were proposed in
the August 2, 1973, Federal Register to meet this requirement:
7. A limitation on gasoline sales at fiscal year 1973
levels to be effective on July 1, 1974.
8. A further limitation on gasoline sales beginning
May 31, 1977 adequate to ensure achievement of
the standards, the extent of this additional
limitation to be estimated by the State by
January 1, 1977.
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EPA held a public hearing on September 10 and 11, 1973, in Denver on
the proposed regulations, and also evaluated written comments and sup-
plemental information. On November 7, 1973, the Administrator published
his approval and promulgation of a Colorado Transportation Control Plan
(TCP) in the Federal Register (Appendix C). Summarizing this action,
• Strategies 1 through 6 were approved as submitted.
• The regulations proposed by the State of Colorado for
the control of hydrocarbon emissions from stationary
sources were disapproved and the regulations on sta-
tionary hydrocarbon sources proposed in the August 2,
1973 Federal Register were promulgated.
• Gasoline sales limitations were promulgated on a con-
tingency basis, adequate to ensure attainment of the
standards by May 31, 1977.
The administrator also granted at that time the extension of time until
May 31, 1977 to achieve the ambient air quality standards, as requested
by the Governor of Colorado.
In the course of preparation of the TCP, the Colorado APCC determined
that the actual reduction in CO emissions from the 1971 levels needed
to attain the National Ambient Air Quality Standard for carbon monoxide
was 64 percent. The TCP, as promulgated by EPA, was expected to reduce
CO emissions by an additional 33 percent compared to 1971 emissions be-
yond the 31 percent reduction determined by EPA to be due to the Federal
Motor Vehicle Control Program. This reduction was due, in part, to the
assumption of a 15 percent reduction in VMT in the metropolitan area in
1977; however, without gasoline restrictions these VMT-reduction strat-
egies accounted for only a 6 percent reduction from the 1971 emissions
of carbon monoxide.
Regulations have not yet been issued by the Colorado Air Pollution Con-
trol Commission for complete implementation of the mobile source control
measures in the TCP. Work is at present underway to finalize the in-
spection, maintenance, and retrofit programs. Regulations have been
95
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passed and planning is in progress for the bus/carpool lanes, parking
facility limitations, and employer programs to encourage use of transit
and bicycles. Expansion of transit service is underway, with a major
bus acquisition by the Regional Transportation District (RTD) being sup-
ported by the U.S. Urban Mass Transportation Administration. To monitor
the effectiveness of the TCP at reducing VMT, Colorado has also prepared
and submitted to EPA on June 17, 1974, a program for continuous, remote
monitoring of traffic in the Denver area. This monitoring plan was re-
quired by EPA.
The Federal Motor Vehicle Control Program (FMVCP) - As the FMVCP emission
standards for all new motor vehicles are being relied upon heavily in this,
and other, transportation control plans, it deserves some discussion at
this point.
The Clean Air Act as amended requires that new light-duty 1977 model-
year motor vehicles achieve 90 percent reduction of carbon monoxide and
hydrocarbon emissions compared to 1970 model-year vehicles and that 1978
model-year vehicles achieve, in addition, a 90 percent reduction of nitro-
gen oxides compared to 1971 vehicle emissions. The driving cycle for
testing the 1972 through 1974 model-year vehicles has been modified for
1975-1976 certification to include hot as well as cold starts to better
represent driving patterns in areas where high pollution levels occur.
These deadlines for 1977-1978 standards may be extended by one year by
the Administrator of EPA if needed technology is deemed not to be avail-
able for a sufficient time to meet production deadlines. Federal emis-
sion standards for heavy duty vehicles (greater than 6,000 pounds gross
vehicle weight) were first implemented for the 1970 model year. Heavy-
duty gasoline engines were limited to 275 ppm hydrocarbons and 1.5 per-
cent carbon monoxide, and heavy-duty diesel smoke plume emissions were
limited. Beginning with the 1974 model year, all heavy-duty vehicle
engines (both gasoline and diesel) are limited to 16 grams per brake
horsepower-hour of hydrocarbons plus nitrogen oxides and 40 grams per
96
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brake horsepower-hour of carbon monoxide. In addition, diesel heavy-
duty engines are limited to certain smoke opacities. (More restrictive
emission standards have not yet been established for later model years
of heavy-duty engines.)
EPA estimated that almost one-half the total emission reduction over 1971
base year levels in Denver required to meet ambient air quality standards
in 1977 will be achieved through FMVCP (31 percent out of the required
64 percent reduction for CO, and 23 percent out of the required 60 per-
cent reduction for HC). The assumptions implicit to these estimates are
that required control technology will be available and in adequate supply
for mass production, and a replacement of existing, relatively high-
polluting vehicles by newer, lower-polluting vehicles through normal
attrition will occur, gradually reducing the average emission rate of
the passenger car population. The potential physical environmental ef-
fect of the FMVCP, therefore, is to substantially reduce air pollutant
emissions thereby enhancing air quality, but not to the degree necessary
to meet ambient health and welfare standards by 1977. Therefore the other
control measures presented must also be implemented,
Current Regulations for Hydrocarbon Emissions
The required hydrocarbon emission reduction, a function of photochemical
oxidant concentration, as determined in the Colorado SIP, was based on the
maximum measured 1-hour photochemical oxidant concentration at the Denver
CAMP station of 294 ug/m^. This implied a needed reduction of 48 percent
in hydrocarbon emissions would be required in order to meet the national
primary and secondary ambient air quality standard of 160 ug/m^ photo-
chemical oxidant. Application of the Federal emission control regulations
for hydrocarbons was expected to provide a 44 percent reduction by 1977.
An additional reduction of 13 percent was expected by the establishment
and operation of an emission testing program. Later review of the air
quality data determined that a 60 percent reduction in hydrocarbon
97
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emissions from the 1971 level was actually necessary for the attainment
of the photochemical oxidant standard by 1977.
At the time that the transportation control plan was being evaluated, EPA
proposed a comprehensive set of regulations for the control of hydrocarbon
emissions from stationary sources (to replace those proposed by the state).
These are also given in Appendix C. These regulations, along with the
other components of the TCP discussed above, are expected to reduce hydro-
carbon emissions in 1977 to 40 percent below the 1971 level. An addi-
tional reduction of 23 percent is assumed by EPA to occur as the result of
the FMVCP. Out of the 40 percent reduction, the VMT-reduction measures
account for 5 percent and the stationary hydrocarbon controls provide a
24 percent reduction; the remainder comes from tailpipe controls and
gasoline restrictions.
The Colorado Air Pollution Control Commission adopted, September 13, 1973,
Regulation No. 7 to control the emissions of hydrocarbon vapors from sta-
tionary sources, effective November 28, 1973. These regulations require
controls for petroleum product storage, petroleum distillate loading,
water separation from petroleum products, pumps and compressors, waste
gas disposal, organic solvents, disposal and evaporation of solvents, dry
cleaning solvents, and degreasing operations. This regulation has not yet
been reviewed by EPA to determine whether it is approvable.
Current Regulations for Nitrogen Oxide Emissions
The Air Quality Implementation Plan demonstrated that, given the current
concentration of nitrogen oxides, measured in the Denver area at the
o
National Air Sampling Network (NASN) station to be 68 ^ig/m (annual arith-
metric mean), no controls are needed for the attainment of the primary
and secondary standard of 100 ug/m (0.055 ppm). Any projected reduction
in nitrogen oxide emissions due to the TCP or the FMVCP is discussed in
Section IV.
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Current Regulations for Sulfur Dioxide Emissions
The Federal Register of September 14, 1973 (Vol. 38, No. 178), sets forth
the revised secondary ambient air standard for sulfur dioxide. The
amendments revoke the annual National Secondary Ambient Air Quality Stan-
dard for sulfur dioxide, which was 60 micrograms per cubic meter (0.02
ppm) . In addition, the amendments delete the maximum 24-hour concentra-
tion of 260 micrograms per cubic meter (0.1 ppm). The secondary 3-hour
standard, a maximum concentration of 1300 micrograms per cubic meter
(0.5 ppm) not to be exceeded more than once per year, remains in effect.
In the Denver Air Quality Control Region, sulfur dioxide as measured at
CAMP station since January, 1969, has not exceeded 0.30 ppm in any 3-hour
average--well below the secondary 3-hour standard. There is therefore no
current need for control regulations to ensure attainment of standards.
However, Regulation No. 1 does contain a section on the control of sulfur
dioxide emissions. Section III sets limits on the concentration of sulfur
dioxide in the emissions from process units. For the purpose of this
regulation, all oxidized forms of sulfur (including, but not restricted to,
863, SOC12, and I^SO^ mist) are considered as sulfur dioxide. This reg-
ulation provides some aid in the maintenance of air quality as it relates
to sulfur dioxide.
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REFERENCES
1. Arthur D. Little, Inc., et. al. Denver Center City Transportation
Project. Prepared for the U.S. Department of Transportation,
September 1970.
2. Colorado Department of Health, Air Pollution Control Division. Air
Quality Implementation Plan for the State of Colorado. Submitted
January 1972.
3. Colorado Department of Highways, Division of Highways. Colorado
Traffic Volume Study, 1970. Prepared in Cooperation with the U.S.
Department of Transportation, 1971.
4. Colorado Environmental Commission. Colorado: Options for the
Future. March 1972.
5. Colorado Motor Vehicle Division. Registration and Receipts Records.
January 1, 1972 to December 31, 1972.
6. Denver Metro Transit. Denver Metro Transit Comments on Environmental
Protection Agency Plan of July 24, 1973. Submitted August 15, 1973.
7. Denver Planning Office. Parking Availability Within the Central
Business District and Peripheral Areas for the 16th Street Mall.
Draft Report, 1973.
8. Denver Regional Council of Governments. Draft: Regional Land Use,
Highway and Public Transportation Plans, Denver Region, Denver,
Colorado. October 17, 1973.
9. Denver Regional Council of Governments. Land Use Information. 2nd
Edition, Denver, Colorado, DRCOG-72-022, 1972.
10. Denver Regional Council of Governments. Joint Regional Planning
Program: Transportation System Report. Denver, Colorado,
June 11, 1973.
11. Denver Regional Council of Governments. Population Pace Still Under
'72 Rates. COG Notes, August 1973.
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12. Denver Regional Council of Governments and the Urban Drainage and
Flood Control District. Urban Storm Drainage and Flood Control in
the Denver Region. Final Report, Urban Systems Demonstration
Program (Project Reuse), Denver, Colorado, August 1972.
13. Denver Regional Council of Governments. A Regional Housing Plan and
Their Implementation. Denver, Colorado, December 1972.
14. Denver Regional Council of Governments. Profile of the Denver
Region 1960 - 1970. Urban Planning Grant No. P-105, May 1973.
15. Development Research Associates, Inc., and Wallace, McHarg, Roberts
and Todd, Inc. Interim Report: Projections. Report prepared for
the Regional Transportation District. Denver, Colorado, January
1972.
16. Development Research Associates, Inc., and Wallace, McHarg, Roberts
and Todd, Inc. Regional Growth, Report Prepared for the Regional
Transportation District. Denver, Colorado, January 1972.
17. Hosier, Charles R. Low-Level Inversion Frequency in the Contiguous
United States. Monthly Weather Review, Vol. 89, pp. 319-339,
September 1961.
18. National Environmental Policy Act of 1969. Public Law 91 - 190,
Congress of the United States, January 1, 1970.
19. Plan Metro Denver. An Interim Transportation Plan. Denver, Colorado,
March 1972.
20. Peat, Marwick, Mitchell, and Co. Final Report: Empiric Activity
Allocation Model Application to the Denver Region. Prepared for the
Denver Regional Council of Governments, December 1972.
21. Personal Communications. Mr. R. C. Thomas, Department of Public
Works, Transportation Division, City and County of Denver, October
1973.
22. Personal Communications. Mr. A. Foster and Mr. E. J. Smith,
Division of Highways, State of Colorado, Denver, August'- October
1973.
23. Personal Communications. Mr. B. M. Pell and Mr. W. J. Walker,
Planning Office, City and County of Denver, October 1973.
24. Personal Communications. Mr. C. Bigenwald, Mr. D. Pampon, and
Mr. R. Friis, Denver Regional Council of Governments, Denver,
Colorado, October 1973.
25. Regional Transportation District. A Public Transportation Plan.
Summary Report, Denver, Colorado, 1973.
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26. Regional Transportation District. Phase One - A Concept. Denver,
Colorado, 1971.
27. Riehl, H. and L. W. Crow. 1962: A Study of Denver Air Pollution.
Dept. Atmos. Sci., Colorado State University, Tech. Kept. No. 33.
28. Reihl, H. and D. Herkhof. 1970: Meterological Aspects of Denver
Air Pollution. Dept. of Atmos. Sci., Colorado State University,
Atmos. Sci. Paper No. 158, 41 pp.
29. Riehl, H. and D. Herkhof. 1972: Some Aspects of Denver Air Pol-
lution Meteorology. J. Appl. Meteor., Vol. 11, No. 7, 1040-1047.
30. U.S. Department of Commerce, Bureau of the Census. Census Tracts:
Denver, Colorado Standard Metropolitan Statistical Area. March
1972.
31. U.S. Department of Commerce. Climate Atlas of the United States.
Environmental Science Services Administration, Environmental Data
Service, Washington, D.C.
32. U.S. Environmental Protection Agency. The Clean Air Act. Washing-
ton, D.C., U.S. Government Printing Office, December 1970.
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SECTION III
EMISSION ALLOCATION AND PROJECTION METHODOLOGY
PROJECTION BASIS
This section summarizes those procedures used for the allocation and pro-
jection of emissions in the Denver AQMSA. A more detailed discussion of
these methodologies can be found in the appendices. The only pollutant
for which allocation (beyond that obtained from readily available sources)
needed to be performed was particulate matter; and, among the sources of
particulate matter, fugitive dust sources received appreciable attention.
Growth rates were derived for point and area sources.
The basis for the data used for the projection of air quality is
crucial to the determination of air quality attainment and maintenance
measures. Unfortunately, no standard criteria exist for data selection.
Since the creation of any set of projections entails certain assumptions
as to future conditions, it is essential to investigate these assump-
tions to determine their degree of reasonableness and to call out these
assumptions as the foundation of the air quality maintenance plan upon
which any additional restrictions are to be built. These assumptions
must be integrated into the maintenance plan which is presented in
Section VI.
For the Denver metropolitan area, the best available basis for projecting
emissions was the Denver Regional Council of Governments' projections of
socioeconomic growth for the Joint Regional Planning Program area. These
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growth projections provided the most detailed data base and compilation
of growth of various population, employment, land-use, and transportation
parameters.
The use of this data is a reasonable approach to the determination of the
growth of the Denver region as the Denver Regional Council of Govern-
ments is the development commission for this area and will be instru-
mental in directing the growth of the region along these lines if no
additional controls are imposed due to the need for air quality main-
tenance. The implication of the use of this data is that in the esti-
mates there are certain implicit assumptions concerning transportation
facilities, population size and distribution, and the existence of cer-
tain highway networks.
For areas outside of the JRPP, official state projections were available
up to 1980, and linear extrapolation was performed to estimate 1985
parameters.
POINT SOURCE EMISSIONS
As point soUrce emissions coordinates are already given in the National
Emissions Data System (NEDS), it is not necessary to do any significant
further allocation of point sources; however, some generalized allocation
assumptions are made in the development of projection parameters. These
are summarized below and detailed in Appendix G. Sufficient information
is not immediately available to allow for any allocation of projected
emissions so projections are assumed to apply to the location of exist-
ing sources.
Projections of particulate emissions from point sources are derived from
a review of regulations controlling these emissions, as given in the Air
Quality Implementation Plan for the State of Colorado, and regional
forecasts of economic growth during the period of interest. Initial pro-
jection of the 1972 NEDS emissions data to 1975 emission levels is
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accomplished by applying the regulations to the process rates (for all
sources producing more than 100 tons per year). This provides the max-
imum estimated level of emissions under existing control constraints and
sets 1975 as the base year for projections.
Within the Denver metropolitan and surrounding areas, data is available
for sub-county areas (Figure 21), called super districts by the Joint
Regional Planning Program (JRPP); the data includes past, current, and
expected employment by major industry types. It is assumed that the
percentage of pollution from each industry type which occurs in each
super district is directly proportional to the percentage of employment
for that industry type within that super district and that the growth
of pollution from each industry is equal to the economic growth or, in
this case, the employment growth rates.
Urder these assumptions, through the use of the employment data, it is
possible to allocate emissions from the county-wide area to the smaller
super districts. The emission allocations for point sources are, at the
same time, divided into commercial-institutional and industrial sectors
within each super district, using the JRPP data. Employment growth rate
factors are calculated for each super district, on the same basis, and
applied to the emissions to give expected emissions in 1980, 1985, and
1990. Then, combining the emissions from each source sector, for each
year, and dividing by the total point source emissions from these sectors
in the base year, a weighted average growth factor for the point source
emissions within each super district is determined. No additional con-
trols, such as New Source Performance Standards, are assumed in these
projections due to the high level of control for existing sources under
state regulations in the base year and the fact that new source contribu-
tions will be minimal.
Growth rate factors for non-urban areas of each county, portions of which
are in the JRPP area, are determined by assuming a slightly higher growth
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BOUL
Legend:
County Line
JRPP super
district
boundaries
Figure 21 . Six county JRPP area - by super districts
106
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rate than found in the most rural of the JRPP super districts within
each county. Such an assumption provides a liberal estimate of growth
for a small percentage of the economic activity within that county.
Counties within the metropolitan Denver AQCR, but not containing any
JRPP areas, are assigned emission growth rates equal to the OBERS eco-
nomic growth rates projected for the whole AQCR. Larimer and Weld Coun-
ties are assigned emission growth rates slightly higher than projected
by OBERS for the Pawnee AQCR. All of these growth rates are presented
in Table 14.
Point source emissions of carbon monoxide are negligible in comparison
with those from motor vehicles and are therefore assumed to be constant
throughout this period. Hydrocarbon emissions from point sources are,
however, significant within the area of interest. Some reductions in
emission levels do occur at point sources due to Federal regulations
(40 CFR 52, Subpart G - see Appendix C) and these are considered in
the discussion of these regulations given under the heading of hydro-
carbons in Section IV.
The growth rate for nitrogen oxides is broken down by power plant, in-
dustrial, commercial-institutional and residential sectors and is only
calculated for the metropolitan Denver area as a whole. The growth rates
derived are simply those of employment or population increase in the
various sectors. For 1975 to 1985, the growth rate is assumed to be 1.0
for power plants, 1.4 for industrial sources, 1.35 for commercial-
institutional sources, and 1.4 for residential related sources. The
intervening years were assumed to have emissions based on a linear
interpolation.
MOBILE SOURCE EMISSIONS
Emission densities for CO, HC, and NO were derived from the projected
X
traffic data for 1975, 1980, and 1985. In addition CO emissions were
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Table 14. POINT SOURCE GROWTH RATES FOR PARTICIPATE
EMISSIONS (BASEYEAR 1975)3
County
Denver
Jefferson
Adams
Arapahoe
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
Rural
SD16
SD17
SD18
SD19
SD20
SD29
Rural
SD21
SD22
SD23
SD24
Rural
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
Rural
1980
0.997
1.078
1.090
1.131
1.130
1.004
1.067
1.075
1.144
1.099
1.206
1.159
1.001
1.282
1.558
1.565
1.138
1.224
1.382
1.220
1.159
1.992
1.348
1.237
1.538
1.745
1.223
1.546
1.182
1.133
1.191
1.190
1.217
1.291
1.186
1.640
1.586
1985
0.924
1.085
1.156
1.258
1.363
1.006
1.114
1.121
1.266
1.168
1.439
1.314
1.024
1.563
2.081
2.087
1.264
1.197
1.521
1.459
1.520
2.093
1.478
1.425
1.786
1.143
1.474
1.772
1.359
1.271
1.302
1.267
1.449
1.360
1.339
1.940
1.897
1990
0.850
1.167
1.223
1.386
1.597
1.018
1.161
1.169
1.391
1.237
1.673
1.469
1.047
1.843
2.604
2.565
1.390
1.170
1.660
1.697
1.306
2.194
1.609
1.613
2.034
1.199
1.726
2.046
1.592
1.409
1.413
1.345
1.682
1.430
1.492
2.240
2.172
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Table 14 (continued). POINT SOURCE GROWTH RATES FOR
PARTICIPATE EMISSIONS
(BASEYEAR 1975)a
County
Larimer
Weld
Gilpin
Clear Creek
Douglas
Area
1980
1.194
1.194
1.208
1.208
1.208
1985
1.748
1.748
1.5
1.5
1.5
1990
1.824
1.824
1.833
1.833
1.833
Based on calculations in Appendix G.
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calculated on a yearly basis from 1971 through 1990 for the core and
central areas mentioned in the TRW report. As defined in the TRW study,
the "Central Area" is a 12 square mile analysis area which lies to the
south of 52nd Avenue, one-half mile north of interstate 70 and to the east
of interstate 25 as far as Colorado Boulevard. The "Core Area" consists
of three square miles and is bounded by Larimer Street on the northwest,
20th Street and 20th Avenue on the north, Logan Street on the east, 13th
Avenue on the south, and Speed Boulevard on the west. HC and NO emis-
X
sions for the entire 960 mi^ Air Pollution Research Advisory Committee
(APRAC) Denver Metropolitan Area2 were also computed for each year for
comparison with stationary source emissions within the same region.
The Research and Special Studies Branch of the Colorado Division of
Highways provided average values of vehicle-miles traveled (VMT) per day
for an array of 240 grid squares each two miles on a side covering the
Denver metropolitan area. This information was originally in the form of
link data suitable for input to the APRAC-lA program for hourly calcula-
tion of CO concentrations at different points within the city for various
meteorological conditions. The transformation of vehicle-miles traveled
(VMT) from the link format to the grid cell basis was carried out by the
Division of Highways so that the data would be more suitable for the ap-
plication of a rollback technique. For each cell the VMT data was broken
down according to the following road type classification and corresponding
vehicle speed:
Road Classification Speed (mi/hr)
Freeway 4-0
Expressway 34
Primary Arterial 26
Minor Arterial 23
Collector 21
Centroid Connector 20
Ramps 20
Major Arterial 23
110
-------
The speeds for the Centroid Connector and Ramp road types are rough esti-
mates because these two classes were allocated solely to the secondary
emissions category in the APRAC-lA data set.
The basis for the traffic data used in the emission calculations is an
3
origin-destination survey and travel forecast carried out under the
Joint Regional Planning Program (JRPP). The output of this study was an
estimate of traffic volumes for the current highway network (1972) and
projection of traffic and new roads for the year 2000. The VMT data for
the intervening years was found by simple linear interpolation.
The emissions of CO, HC, and NO for each grid square were then calculated
X 4
by use of the Kircher and Armstrong emission factors along with diesel
emission estimates from AP-42. ' This procedure involves a summation
over low mileage emission factors, emission control deterioration,
weighted annual travel, and different speed types. Evaporative hydro-
carbon emissions were also accounted for in the calculation. Modifications
were made in the emission and deterioration factors to account for the
fact that high altitude emissions standards will first apply to 1977 model
year vehicles and that the interim standards are assumed to be extended
through the 1977 model year. The model year distribution and breakdown by
vehicle type (light duty, heavy duty, and diesel) were taken from the TRW
transportation study for the Denver area.
Projections of mobile source emissions were also carried out for Boulder,
Ft. Collins, and Greeley based upon 1968 and 1990 VMT data as a function
of road type as listed in the Classification, Needs, and Fiscal Study
prepared for the Department of Highways by Wilbur Smith and Associates.
To obtain a reasonably accurate measure of the emission density the ef-
fective emission areas for these cities were chosen so as to include a
significant fraction of the heavily traveled streets but omit the largely
rural sections included within the urban boundaries.
Ill
-------
Emission density maps were generated and are used for projecting the air
quality. These maps are presented in Section IV under the discussion of
the corresponding pollutant.
NEDS AREA SOURCE EMISSIONS
Area source emissions of particulates, provided by the NEDS, are pro-
jected to 1975, 1980, and 1985 on much the same basis as particulate
point sources; however, no regulations can be applied to these sources
to provide an initial decrease in emissions. Therefore, a base year of
1972 (the base for the NEDS) is used for projecting particulate emissions
from this sector.
In addition to employment statistics, population is used to allocate
and project emissions from the residential sector. The employment and
population percentages are, again, applied to allocate emissions to super
districts and rural regions. Employment and population growth rates are
then applied to give projected emissions which are recombined to give
total emissions and therefore the growth rate for particulate emissions
from stationary sources.
As the percentage contribution from motor vehicles to the total particu-
lates due to the area source sectors is not small, ranging from 13
percent in Denver to 21 percent in Adams and Arapahoe, it is necessary
to consider increased emissions from motor vehicles separately. However,
since this is still not the majority of particulate emissions, for the
purpose of projecting particulates, motor vehicles are included under
area sources. (For hydrocarbons, carbon monoxide, and nitrogen oxides,
motor vehicles are considered as discussed in the previous subsection.)
Projections of increased particulate emissions as a result of motor
vehicles are made by assuming that the total emissions from the motor
vehicles grow with the increased VMT. While this would normally be a
direct proportion, the installation of catalytic mufflers in new cars
decreases the emissions from motor vehicles exhaust so that the increase
112
-------
is correspondingly less until all cars are assumed to have catalytic
converters. These growth rates for emissions from motor vehicles are
then combined with those from the stationary area sources to provide the
estimated growth rates for particulate emissions due to all area sources.
These rates are presented in Table 15 and developed in more detail in
Appendix H.
Projections of increased emissions of carbon monoxide and nitrogen oxides
due to stationary sources are not considered due to the minimal impact
which area sources are known to have on the ambient concentration.
Hydrocarbon emissions from all stationary sources are assumed to decrease
as projected under the Federal regulation cited earlier. This is dis-
cussed in more detail in Section IV.
FUGITIVE DUST EMISSIONS
Fugitive dust is defined as those particulate emissions arising from
certain manmade sources during arid or windy conditions. These
Q
sources, as identified in the PEDCo report, include the following:
1. unpaved roads
2. sand on paved roads
3. agriculture
4. land development
5. residential, industrial, and commercial construction
6. highway construction
7. quarrying, mining, and tailings
8. aggregate storage
9. cattle feedlots.
The PEDCo study provided fugitive dust totals by county for Colorado.
These figures are here disaggregated into county subunits, or zones.
State land use maps were used as a guide in determining zones, so that
each zone represents a specific land use. Most of the allocation is di-
rected toward separating agricultural sources and the contributions from
113
-------
sanding of paved roads. Fugitive dust from agricultural operations for
a given county is assigned to crop-lands. A similar methodology is
applied to the emissions from the sanding of paved roads, with the
fugitive dust being distributed to urban areas only. The remaining
fugitive dust, principally from dirt roads and construction, is uni-
formly allocated throughout each county. The specific zones are shown
on the maps in Figures 22 and 23 and the corresponding emission den-
sities are given in Table 16. Primary data and calculations for the
allocation of fugitive dust are given in Appendix I.
The fugitive dust emissions are projected to 1975, 1980, and 1985 by ap-
plying the regulation recently promulgated by the Colorado Air Pollution
Control Commission, and projected travel and socioeconomic activity. The
regulation, Section II-D of Regulation Number 1, is provided in full in
Appendix E and is summarized below.
1. A general statewide requirement is that no fugitive dust
be emitted which exceeds 20 percent visible opacity or
which is visible after it leaves the property of the
owner of the emission source. Certain activities, such
as agriculture, are exempted.
2. Within the Priority I portions of Air Quality Control
Regions only (see Figure 24), which includes only a
portion of the AQMSA, specific requirements are estab-
lished for control of dust from:
a. All new unpaved roads and parking areas with traffic
volumes of 165 vehicles per day (vpd) or more.
b. Existing privately owned roads and parking areas
with 165 vpd or more.
c. Existing publicly owned roads and parking areas with
165 vpd or more, but with controls only to the ex-
tent allowed by financial resources.
d. Land development, construction, demolition, and
related activities.
3. Specific control requirements, statewide, on open mining
activities.
4. Where specific requirements for controls are provided, a
requirement that permits be obtained and a requirement
that specified types of abatement and preventive measures
be identified in the permit and utilized.
114
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Table 15. AREA SOURCE GROWTH RATES FOR PARTICULATE
EMISSIONS (BASEYEAR 1972)a
County
Denver
Jefferson
Adams
Arapahoe
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
Rural
SD16
SD17
SD18
SD19
SD20
SD29
Rural
SD21
SD22
SD23
SD24
Rural
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
Rural
1975
1.049
1.071
1.184
1.102
1.104
1.055
1.088
1.082
1.102
1.087
1.145
1.124
1.055
1.187
1.428
1.458
1.110
1.248
1.278
1.122
1.122
2.083
1.364
1.149
1.380
1.069
1.115
1.513
1.154
1.092
1.213
1.129
1.133
1.216
1.117
1.499
1.539
1980
1.100
1.179
1.185
1.241
1.240
1.113
1.198
1.180
1.238
1.194
1.331
1.278
1.102
1.438
2.055
2.067
1.229
1.579
1.564
1.259
1.238
3.029
1.584
1.326
1.911
1.124
1.242
2.250
1.355
1.197
1.170
1.290
1.301
1.514
1.259
2.238
2.216
1985
1.114
1.248
1.281
1.368
1.408
1.177
1.294
1.267
1.343
1.289
1.549
1.409
1.170
1.668
2.703
2.676
1.338
1.922
1.660
1.414
1.391
3.776
1.673
1.485
2.163
1.175
1.375
2.361
1.591
1.315
1.282
1.374
1.494
1.595
1.395
2.581
2.530
1990
1.138
1.320
1.386
1.512
1.584
1.257
1.401
1.364
1.463
1.395
1.794
1.563
1.261
1.928
3.394
3.329
1.493
1.922
1.819
1.609
1.582
3.975
1.742
1.686
2.476
1.261
1.549
2.542
1.887
1.458
1.418
1.485
1.715
1.696
1.554
2.969
2.892
115
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Table 15 (continued). AREA SOURCE GROWTH RATES FOR PARTICIPATE
EMISSIONS (BASEYEAR 1972)a
County
Larimer
Weld
Gilpin
Clear Creek
Douglas
Area
1975
1.165
1.132
1.133
1.120
1.230
1980
1.485
1.382
1.390
1.591
1.738
1985
1.851
1.695
1.683
2.043
2.382
1990
2.617
2.008
1.976
2.494
3.026
aBased on calculation in Appendix H.
116
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118
-------
Table 16. FUGITIVE DUST EMISSION DENSITIES BY ZONES'
(TONS/YEAR/4 kra2)
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Zone
1.
2.
1.
2.
3.
1.
2.
3.
1.
2.
3.
1.
2.
3.
1.
2.
Cropland
Range land
Cropland
Range land
Range land
Cropland
Range land
Woodland
Predominately
woodland
Urban
Range land and
wood land
Predominately
woodland
Urban
Rangeland
Woodland
Cropland
Woodland
Recreation
land
Cropland
Rangeland
Emissions
(tons/yr)
19,360
6,698
5,680
4,430
5,002
9,848
2,718
7,611
7,437
8,018
5,629
18,228
4,255
5,632
7,915
20,804
12,526
2,424
88,863
25,749
Area
(sq km)
2025
1050
691
624
700
468
390
1073
1000
201
2268
340
230
735
1044
1773
4275
822
3470
7681
Emission density
(tons/yr/4 km^)
38.26
25.47
32.88
28.40
28.58
84.17
27.88
28.40
29.75
159.56
9.93
214.45
74.00
30.65
30.33
46.96
11.72
11.49
102.38
13.41
Calculation, based upon PEDCo data, is given in Appendix I.
119
-------
LEGEND
COUNTY BOUNDARY
PRIORITY ONE BOUNDARY
Figure 24. Priority I area in the Denver AQMSA
120
-------
The actual methodologies for the calculation of emission reductions, due
to the above regulation, and for the projection of the fugitive dust emis-
sions to 1985 are detailed in Appendix J. A short discussion of the ap-
proach is given below.
Initially, dust emission reductions are calculated for the 1972 emissions
inventory (PEDCo study), based on a similar estimate performed by PEDCo
of the effect of a draft version of the same regulation. These reduc-
tions are determined for emissions from unpaved roads, land development
and construction activities, and mining and storage operations.
For unpaved roads, it is necessary to determine what fraction of total
travel on unpaved roads would come under the regulation. The procedure
assumes that the high volume roads are more likely to be in the Priority
I portion of the AQMSA, rather than the less developed areas. The frac-
tion of total daily travel on those unpaved roads with 165 vpd, based on
average daily travel on unpaved roads in each county (supplied to PEDCo
by the Colorado Division of Highways), is estimated using the method
described in the PEDCo study. It is further assumed that all such roads
falling under the regulation will be controlled (i.e., no financial con-
straints) to the control efficiency of 60 percent as stated in the PEDCo
study.
Emissions from land development, residential and commercial construction,
and highway construction are reduced according to the control efficien-
cies estimated by PEDCo for the fraction of each county's activity esti-
mated to be in the Priority I area. These control efficiencies are 60
percent for land development and 50 percent for construction activities.
Quarrying, mining, tailings, and aggregate storage are assumed to be con-
trolled throughout the counties to the extent estimated in the PEDCo study
(75 percent for mining activities; 25 percent for storage). No controls
on cattle feedlots or sand from snow control are assumed.
121
-------
Total reduced emissions are then re-allocated among the portions of the
county previously designated for the allocation of fugitive dust so that
a general control factor can be estimated for these zones. These new
emission rates then serve as a base line for projecting growth of fugitive
source emissions. Given the current timetable for implementation of the
regulation, the base line year is assumed to be 1975.
Projections of the emissions of fugitive dust in 1980 and 1985 are esti-
mated by using information on projected travel and social and economic
activity and by assuming that several source categories will remain con-
stant: unpaved roads; agriculture; quarrying, mining, and tailings;
aggregate storage; and cattle feedlots. It is expected that control mea-
sures on an increasing number of unpaved roads would be offset by increased
traffic on present low-volume unpaved roads or by new unpaved roads with
incomplete control of dust. The other categories are seen as unlikely to
greatly change in activity.
Sand on paved roads is expected to increase in direct proportion to total
vehicle-miles of travel. The travel data used for this forecast is the
travel forecast, by county, supplied by the Colorado Division of Highways.
Land development, residential-commercial construction, and highway con-
struction are assumed to increase in proportion to population, employment,
and earnings. In the Denver metropolitan area, forecasts (by the Denver
Regional Council of Governments) of land use, by county, by year, have
been used to calculate the rate of land conversion and construction.
Future activity is then compared to present activity to develop growth
factors for emissions. Highway construction activity is estimated
directly from DRCOG estimates of land use for roadways. In areas outside
the Denver metropolitan areas, land development and construction emissions
are also assumed to increase in the same manner as socioeconomic activity.
For these areas, the general growth factors for particulates area sources,
described earlier in this section, are used to forecast growth in these
fugitive dust sources.
122
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Table 17. FUGITIVE DUST EMISSIONS GROWTH RATES BY ZONES'
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Zone
1.
2.
1.
2.
3.
1.
2.
3.
1.
2.
3.
1.
2.
3.
1.
2.
Cropland
Range land
Cropland
Range land
Range land
Cropland
Range land
Woodland
Predominately
woodland
Urban
Rang el and and
woodland
Predominately
woodland
Urban
Rang el and
Woodland
Cropland
Woodland
Recreation
land
Cropland
Rangeland
1972-1975
0.86
0.80
0.81
0.78
0.78
0.90
0.70
0.70
0.86
0.89
0.96
1.0
0.85
0.63
0.63
0.95
0.78
0.78
0.98
0.87
1975-1980
1.04
1.07
0.99
0.99
0.96
1.00
1.00
1.00
1.47
1.12
1.50
1.01
1.18
1.07
1.07
1.01
1.05
1.05
1.00
1.02
1975-1985
1.01
1.02
0.97
0.96
0.96
1.00
0.99
0.99
1.82
1.25
2.01
1.02
1.30
0.95
0.95
1.02
1.08
1.08
1.00
1.03
eased on calculations in Appendix J.
123
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Forecasted fugitive dust is then re-allocated to the zones in the same
manner as described earlier and growth rates for these zones are deter-
mined. These are presented in Table 17.
124
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REFERENCES
1. TRW Transportation and Environmental Operations, 7600 Colshire
Drive, McLean, Virginia 22101. Transportation Control Strategy
Development for the Denver Metropolitan Area» Prepared for the
Environmental Protection Agency, Office of Air and Water Programs,
Office of Air Quality Planning and Standards, Research Triangle
Park, North Carolina 27711, Contract No. 68-02-0048, Publication
Number APTD-1368, December 1972.
2. Stanford Research Institute. User's Manual for the APRAC-lA Urban
Diffusion Model Computer Program. Prepared for the Coordinating
Research Council and the United States Environmental Protection
Agency, Division of Meteorology, September, 1972.
3. Denver Regional Council of Governments. Transportation System
Report. December 1973.
4. Kircher, D. S. and D. P. Armstrong. An Interim Report on Motor
Vehicle Emission Estimation. Environmental Protection Agency,
Office of Air and Water Programs, Office of Air Quality Planning
and Standards, Research Triangle Park, North Carolina 27711.
Publication Number EPA-450/2-73-003, October 1973.
5. U.S. Environmental Protection Agency, Office of Air and Water
Programs, Office of Air Quality Planning and Standards. Com-
pilation of Air Pollutant Emission Factors. Table 3.1.5-1
(Second Edition). Research Triangle Park, North Carolina,
Publication Number AP-42, April 1973.
6. U.S. Environmental Protection Agency, Office of Air and Water
Programs, Office of Air Quality Planning and Standards. Supplement
No. 2 for Compilation of Air Pollutant Emission Factors. Research
Triangle Park, North Carolina, Publication Number AP-42,
September 1973.
7. Wilbur Smith and Associates. Highway Classification, Needs, and
Fiscal Study (1970-1990). Prepared for the Colorado Department of
Highways, August 1972.
125
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PEDCo - Environmental Specialists, Inc. Investigation of Fugitive
Dust - Sources, Emissions, and Control - For Attainment of Secondary
Ambient Air Quality Standards, Colorado. Prepared for the U.S.
Environmental Protection Agency, Office of Air Quality Planning and
Standards, Research Triangle Park, North Carolina.
126
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SECTION IV
ASSESSMENT OF EXISTING AND FUTURE AIR QUALITY
Table 18, published by EPA, includes the national ambient air quality
standards for the four pollutants to be addressed in the Denver AQMP,
namely, total suspended particulates, carbon monoxide, nitrogen dioxide,
and photochemical oxidants. In this section, an assessment of the
existing and future air quality is made by comparing measured and pro-
jected air quality with these standards.
TOTAL SUSPENDED PARTICULATES
Summary of Observed Concentrations
Annual average and 24-hour average total suspended particulate concen-
trations were reported in the National Aerometric Data Bank for 34
sampling locations within the Denver Front Range AQMSA during the
3-year period from 1970 to 1972. The annual geometric means at each
of these stations are listed in Table 19. Inspection of the data for
stations with means for all 3 years shows that the highest mean for
the 3-year period occurred in 1970 at seven stations, in 1971 at 17
stations, and in 1972 at six stations. Annual geometric mean data
for 1973, made available by the Colorado Department of Health and also
listed in Table 19, include values for 28 of the 34 stations. The
1973 annual means at 15 of the 24 stations exceeded the maximum value
observed during the previous years. Also, when all stations within
the AQMSA having four years of data are averaged, the following annual
averages are obtained: 1970 - 83.2 (ig/m3; 1971 - 86.9 |j.g/m3; 1972 -
127
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128
-------
Table 19. DENVER FRONT RANGE AQMSA AIR QUALITY DATA;
ANNUAL GEOMETRIC MEANS, PARTICULATE MATTER
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Location
Westminster
Aurora
Brighton
Adams City
Cherry Creek Dam
Englewood
Littleton
Boulder
Longmont
Idaho Springs
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Sewer Plant
Sch. Admin. Bldg. (State)
Gates Building
Sch. Admin. Bldg. (EPA)
2105 Broadway
Castle Rock
Concentration, ^ig/nP
19703
73
88
95
42
95
95
63
92
--
67
80
84
135
108
121
122
173
56
Black Hawk
Rocky Flats
Golden
Lakewood
Edgewater
Arvada
La Porte
Fort Collins
Loveland
Greely
Ft. Lufton
Greely
Johnstown
Windsor
47
60
60
88
110
51
88
75
75
85
90
96
100
a
1971
70
74
86
89
!
106
113
65
105
74
69
84
82
112
124
123
118
186
65
52
52
71
71
102
110
46
76
83
92
82
99
100
103
a
1972
I
79
! 89
87
89
102
109
64
96
66
64
74
84
~~
108
127
125
151
152
66
80
38
61
71
98
107
50
69
82
67
80
88
88
92
1 b
] 1973
i
81
j 94
| 107
103
45
L10
; 69
129
89
73
80
133
126
130
82
62
44
70
75
86
111
51
71
85
95
91
80
107
from National Aerometric Data Bank.
Data from Colorado Department of Health.
129
-------
82.9 p.g/m3; and 1973 - 91.7 ug/m^. Thus it appears that no overall trend
in particulate concentrations occurred during the period, although the pos-
sibility of increasing concentrations beginning in 1973 can not be ruled
out.
Although it is possible that individual sites may be experiencing sig-
nificant trends, the period of record is too short to validate such
changes. A suggested procedure for trend detection outlined in the EPA
2
Guideline Series, for example, recommends the use of a 3-year running
average to smooth out year-to-year variations caused by such factors as
transient meteorological phenomena and sampling errors. In view of the
above, it is assumed that no trend in particulate concentrations occurred
during this period within the AQMSA, and that the best estimate of exist-
ing concentrations at the various sites can consequently be obtained by
averaging the geometric means for the period in question. However, since
the individual 24-hour concentrations were not yet available for 1973,
and the annual data had not yet appeared in SAROAD, the development of
base line data was restricted to the 3 years 1970, 1971, and 1972. The
selection of a no-trend option does not differ substantially from the re-
sults of the EPA Plan Revision Management System for the Metropolitan Denver
3
Intrastate AQCR which, in summary, states that "Although some progress
has been made in controlling TSP, the average air quality change in the
past year (year ending with the first quarter of 1973) has been an in-
3 3
crease of 3.4 |j.g/m with a 24 \±g/m increase at one site."
Table 20 presents the arithmetic average of the annual geometric means
observed at each station during this 3-year period (1970-1972). Within
each county, sites have been arranged in order of increasing concentra-
tion. The percent of 24-hour average concentrations above the primary
and secondary standards at the stations are also given for each station.
In columns 3, 4, and 5, the location of the monitor is described in
terms of surrounding land use, local population and sampling height.
130
-------
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Denver
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3
Table 20 shows that the annual secondary standard of 60 g.g/m (a guide
for assessing implementation plans to achieve the 24-hour standard) was
exceeded at all sites except the predominately rural or remote sites:
Cherry Creek Dam in Arapahoe County, Rocky Flats in Jefferson County,
3
and LaPorte in Larimer County. The primary annual standard of 75 ug/m
was exceeded at 23 of the 34 stations. Highest concentrations were ob-
served in the commercial areas of downtown Denver where the secondary
standard was exceeded about one-third of the time. The highest 3-year
3
average concentration of 170 |j.g/m , observed at the 2105 Broadway site,
presumably reflects the low sampling height of 9 feet at this measure-
4
ment station. Figure 25 illustrates the spatial distribution of
annual concentration levels by means of isopleths of concentration
3
equal to 60, 75, 100, and 125 ug/m . The concentrations shown in the
figure are the 3-year mean values given in Table 20. It should be
recognized that nearly all monitoring locations are in business or
3
residential areas and that the 60 and 75 |_ig/m isopleths, therefore,
indicate the bounds within which in-town concentrations are likely to
have exceeded the standards rather than that all locations within these
isopleths did so.
Table 21 has been prepared as an aid in developing effective strategies
for the attainment and maintenance of the total suspended particulate
ambient standards. It presents by month, for each of the 34 sampling
stations, the percentage of the 24-hour observations during the 3-year
period that exceeded the secondary standards. Average values for all
sites and for Weld County sites only are given at the bottom of the
table. The results show that concentrations exceeding the secondary
standards occur most frequently during the months from October through
April and least frequently during June and July. However,
this seasonal trend appears to be much less evident in Weld County,
where summertime concentrations also frequently exceed the secondary
standards. This may be a reflection of summertime dusty conditions
132
-------
LARIMER
WELD
\
\
\
\
\
\
\
•70 ^ GOLDEN
IDAHO I
SPRINGS! 67
L
= SAMPLING SITE
Figure 25. Average annual suspended particulate concentrations mea-
sured within the Denver AQMSA during 1970-1972. Units
are |_ig/m .
133
-------
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Longmont
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All Stations
Weld County O
134
-------
resulting from fugitive sources, as was found to be the case in two
cities in Idaho.
Figure 26, prepared from Table 20, shows the relationship between the
annual geometric mean and the percentage of the 24-hour average con-
centrations that were above the secondary standard. The Weld County
data, which show a greater percentage of observations above the stan-
dard than the observations from the remaining counties for a given
annual mean, have been treated separately in the figure.
To estimate the percentage of reduction in man-made emissions required
to achieve and maintain air quality, annual averages are used, and a
3
background level of 30 (j.g/m is assumed in agreement with the State
Implementation Plan calculations. The emission reductions required,
using proportional rollback, are given by the equation
R •
where A = annual geometric mean
B = background concentration
C = national ambient standard
Before selecting the annual geometric mean to be used to calculate the
required reduction in emissions affecting downtown Denver, the data in
Tables 19 and 20 were considered in detail. If one accepts in principle
the assumption that the best available estimate of existing air quality
at each site is obtained by averaging the annual means for the 3 years,
and if one further eliminates from consideration data obtained at heights
below 15 feet in line with the philosophy given in the draft Guideline
4
Series document OAQPS No. 1.2-012, the use of an annual mean of 130
3
iag/m is indicated for the rollback calculations. On the other hand,
135
-------
40
60 80 100 120 140
ANNUAL GEOMETRIC MEAN;>ig/n»3
160
Figure 26 Relationship between the annual geometric mean of total
suspended particulate concentration and the percentage
of 24-hour average concentrations above the secondary
standard. Weld County data are indicated by X*s; data
from all other sites are indicated by t's.
136
-------
this mean was obtained from 77 observations made at the School Admin-
istration Building, whereas 248 observations during the same period by
a different agency at this building gave a mean of 120 ug/m for the
same 3-year period. A second approach is to examine the means for the
3 separate years, again omitting observations made below 15 feet. The
3
highest annual geometric mean of 151 jig/m was calculated from 26 ob-
servations at the School Administration Building in 1972, while the
annual mean from the other set of measurements at this site in 1972,
3
consisting of 79 observations, was 127 |ig/m . Thus, justification
exists for the selection of a baseline concentration from below 130
3 3
ug/m to the use of one as high as 151 ug/m . For the development of
3
the AQMP, a value of 130 ug/m will be used. The use of the propor-
tional rollback equation with this value gives the reduction that would
be required to meet the primary standard in Denver County as
R = ^Q _ 3Q x 100 = 55 percent
and the reduction required to meet the secondary standard as
R = TJn ?n x 10° = 70 percent
3
It must be recognized, however, that the use of 151 ug/m as the base-
line value would result in required reductions of 63 and 75 percent to
meet the primary and secondary standards, respectively.
It also is apparent that emissions affecting many of the smaller cities
in the AQMSA will have to be reduced substantially before the standards
can be achieved and maintained. As an indication of the maximum reduction
required, the 3-year average of the annual geometric means in both Long-
mont and Windsor is 98 ug/nP (see Table 20 or Figure 27).
137
-------
This leads to the following required reductions:
To meet the primary standard
98 - 7 5
R = 98 - 30 x 10° = 34 Percent
and, to meet the secondary standard
QQ _ r f\
R = 98 - 30 x 10° = 56 Percent
Reductions required in other cities in the AQMSA can be similarly esti-
mated from the data presented in Table 20.
Modeling of Particulate Air Quality
Atmospheric modeling is used to help provide projections of partic-
ulate air quality. First, the technique helps to analyze the spatial
concentration pattern of a pollutant and secondly, it describes changes
in this pattern due to variations in source strengths during the period
of interest. The models are also calibrated with actual air quality
measurements so that the air quality may be projected over a much
larger area than that covered by the network of stations.
There are several ingredients which must be present as input to a
meaningful air quality modeling analysis. Due to the general propor-
tionality between concentration and source strength, the most impor-
tant requisite is a rather detailed knowledge of the magnitude and
spatial distribution of the emissions. Area source boundaries should
be arranged so that the variation of emissions across a given grid
square is kept to a minimum. Point sources should be characterized
according to height, flow rate, and stack gas temperature. The meteor-
ological parameters that control the spread of a pollutant after emis-
sion include wind speed, wind direction, atmospheric stability, and
mixing height.
For this study, the point source locations, emissions, and character-
istics were obtained from the National Emissions Data System (NEDS)
138
-------
for the 10 counties in the AQMSA. This data is available upon request
from Monitoring and Data Analysis Division, Office of Air Quality
Planning and Standards, (OAQPS), Research Triangle Park, North Carolina.
The area source emissions were taken from EPA computer-generated maps
from OAQPS that give the emissions in hundreds of tons per year for
grid squares 2 km on a side. These area source particulate emissions
were originally in the form of county totals which were then allocated
according to population density by a version of the Computer Assisted
Q
Area Source Emissions (CAASE) allocation procedure. Fugitive source
9
emissions were taken from the PEDCo Report and allocated as to land use
category. The annual frequency of wind speed, direction, and stability
occurrences were obtained for the Denver area from the National Climatic
Center in Asheville, North Carolina.
For purposes of air quality projection, it was decided to apply the
Climatological Dispersion Model (CDM) to calculate average annual
ground level air pollutant concentrations due to point sources. Area
source contributions were evaluated by means of the Hanna-Gifford Area
11 12
Source Model. ' These two different approaches were utilized since
the CDM predictions of concentrations due to area source emissions
seemed unrealistically low and required excessive amounts of computer
time. The CDM was chosen, however, for point sources with buoyant
plumes since it can account in more detail for the distribution of
wind speeds and stabilities in addition to the presence of a mixing
layer.
The Hanna-Gifford model has the advantage that the air quality within
a particular grid square may be related directly to the emission den-
sity within that square and those immediately adjacent. The concen-
tration within a cell may be calculated according to the following
expression which results from an integration of the receptor-oriented
Gaussian plume (with lateral diffusion neglected) over upwind area
sources.
139
-------
X
where:
2
a(l - b) u
N
1-b
(1)
X = ground level air concentration (/xg/m )
u = average wind speed (m/sec)
2
Q. = source strength for cell i (/xg/m /sec)
Ax = cell width (m)
a,b = power law parameters for (Q- -ax), where a., is the plume
dispersion in meters
f, = frequency of wind speed from direction k
(k = 1 to 16)
An example calculation and results illustrating the application of
this model are presented in Figure 27. For this computation the wind
direction frequency distribution (Figure 28) for Denver was used along
with an average wind speed of 4.15 m/sec. The emission rate of 0.72
2 2
pg/m /sec corresponds to a source strength of 100 tons/yr/4 km which
is rather common for the Denver area. The coefficients a and b were
chosen as 0.15 and 0.75, respectively, to approximate Pasquill's
slightly stable (D) condition which, according to Gifford is most
appropriate to average urban conditions. The resultant concentrations
from this sample calculation indicate that the contribution from neigh-
boring squares is likely to be rather negligible compared with the
emissions from the square under consideration. By treating only this
central square and summing over f, the resulting expression becomes
K.
y /* xl-b
JI
T it
x = ' *; *' —* (2)
a(l - b) u
The requirement of a grid spacing of 2 km and a neutral stability con-
dition yields the following simple result.
Q
X= 120 -£ (3)
140
-------
0
0
0
-— 2km -*•
0
0.72
0
0
0
0
(a)
0.3
1.0
0.5
1.3
20.8
1.4
1.0
0.7
0.4
(b)
Figure 27. (a) Source strengths in ng/m /sec
(b) Resultant concentrations in ug/m
141
-------
t
NORTH
DENVER
WINDROSE
ANNUAL
Figure 28. Frequency of wind directions after summa-
tion over wind speeds and stabilities
One inch equals ten percent.
142
-------
Since the particulate area source emissions were allocated by popula-
tion over a system of 2-km grids, the concentration at a given recep-
tor is found by applying equation (3) to the area source strength for
the cell in which the receptor is located. While this procedure is
straightforward, its accuracy is somewhat limited because the
receptor might not be located near the center of a square. In
several cases during the modeling study it was appropriate to inter-
polate between emission strengths of adjacent squares. There is also
the difficulty that the allocation-gridding procedure required (due
2
to format restrictions) that the area source emissions for a 4 km
cell are rounded off to the nearest 100 tons/yr, thereby reducing the
spatial resolution. Since the fugitive source emissions represented
areas of varying size, equation (2) was employed to calculate their
contribution to a receptor. For this case the approximation is made
that Ax is equal to the square root of the fugitive source emission
zone area. A more detailed description of the CDM and Hanna-Gifford
model is given in Appendix K.
By use of these techniques average annual ground level air concentra-
tions of particulates were calculated for the air sampling stations
mentioned earlier. The results of this calculation, broken down into
point, area, and fugitive dust source contributions, are given in Table 22
No background contribution has been added to the source contributions.
Table 23 gives the total calculated, measured, and fitted concentra-
tions plus background for the same 34 sampler locations. The correla-
tion coefficient between the calculated concentrations and measured
values shown in Table 23 is 0.61. This rather low value for the cor-
relation coefficient is probably due to several factors. The air
quality models employed in the study depend upon meteorological param-
eters which are measured at one location and may not be representative
of the entire area of interest. Also, there is currently no simple
way of accounting for the effects of topography in pollutant dispersal.
The area source emission rates used for the Denver AQMSA were only
143
-------
Table 22. CALCULATED PARTICIPATE CONCENTRATIONS (ug/m
3, a
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
GilpjLn
Jefferson
Larimer
Weld
Location and
UTM coordinates (km)
Westminster (496.5,4408.2)
Aurora (511.0,4398.9)
Brighton (515.5,4426.2)
Adams City (505.5,4408.4)
Cherry Creek Dam (515.9,
4388.5)
Englewood (501.0,4386.3)
Littleton (498.4,4384.6)
Boulder (476.3,4429.6)
Longmont (491.4,4445.9)
Idaho Springs (456.3,
4399.0)
State Health Dept.(506.6,
4397.8)
Hull Photo (506.2,4402.1)
Julian Street (497.3,
4399.7)
Sloans Lake (495.9,4400.0)
Sewer Plant (502.3,4404.1)
Sch. Admin. Bldg. (500.6,
4398.8)
Gates Building (501.1,
4394.0)
Sch. Admin. Bldg. (500.6,
4398.8)
2105 Broadway (501.1,4399.9)
Castle Rock (512.1.4357.9)
Black Hawk (457.5,4405.6)
Rocky Flats (483.6,4415.4)
Golden (480.8,4400.5)
Lakewood (490.7,4395.5)
Edgewater (494.8,4400.1)
Arvada (493.0,4405.2)
La Porte (487.8,4497.1)
Fort Collins (493.3,4492.5)
Loveland (494.0,4471.8)
Greely (526.0,4474.9)
Ft. Lufton (516.1,4436.7)
Greely (527.4,4474.4)
Johnstown (507.6,4464.8)
Windsor (508.1,4480.9)
Point
9
3
7
17
2
8
13
1
2
1
5
6
12
22
14
22
22
22
18
1
1
4
5
9
56
6
2
3
3
13
4
9
2
3
Area
21
0
0
10
0
21
10
42
21
0
21
31
42
31
10
42
31
42
31
0
0
0
0
0
21
10
0
21
21
10
0
10
0
0
Fugitive
17
17
17
17
11
11
11
10
32
12
54
54
54
54
54
54
54
54
54
5
78
12
12
26
26
26
6
21
21
50
50
50
50
50
Total
47
20
24
44
13
40
34
53
55
13
80
91
108
107
78
118
107
118
103
6
79
16
17
35
103
42
8
45
45
73
54
69
52
53
aBased on NEDS and PEDCo emissions inventory.
144
-------
Table 23. FITTED PARTICULATE CONCENTRATIONS (|ig/m )
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Location
Westminster
Aurora
Brighton
Adams City
Cherry Creek Dam
Englewood
Littleton
Boulder
Longmont
Idaho Springs
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Sewer Plant
Sch. Admin. Bldg.
(State)
Gates Building
Sch. Admin. Bldg.
(EPA)
2105 Broadway
Castle Rock
Black Hawk
Rocky Flats
Golden
Lakewood
Edgewater
Arvada
La Porte
Fort Collins
Love land
Greely
Ft. Lufton
Greely
Johnstown
Windsor
Calculated
47
20
24
44
13
40
34
53
55
13
80
91
108
107
78
118
107
118
103
6
79
16
17
35
103
42
8
45
45
73
54
69
52
53
Measured
74
79
87
91
42
101
106
64
98
70
67
79
83
84
118
120
123
120
170
62
66
46
64
67
96
109
49
78
80
78
82
92
95
98
Fitted
plus
background
70
47
51
68
41
64
59
75
77
41
98
108
122
122
97
131
122
131
118
35
98
44
45
60
118
66
37
69
69
92
76
89
75
75
145
-------
approximate due to the roundoff problem for the gridding procedure
mentioned earlier and the fact that the fugitive dust allocation tech-
nique lacked necessary resolution.
The fitted concentration values, which are used in the subsequent air
quality projections and strategies, were calculated by means of a one
parameter linear least squares fit to the measured concentration after
3
subtraction of a background of 30 jjg/m recommended in the Colorado
State Implementation Plan. The following relationship then holds be-
tween the calculated concentration X > the fitted concentration X ,
and the fitted concentration plus background X , :
Xf = 0.856 Xc (4)
Xfb = Xf + 30 (5)
Fitted values for air quality were used to smooth out the irregulari-
ties in the measured air quality data which might be due to localized
nearby sources particularly for those air samplers located close to
the ground. An alternate procedure would be to choose the fitted value
3
to be the measured value minus the 30 fig/m background for those sta-
tions whose measurements were not highly influenced by sources in the
immediate vicinity of the sampler. Since this approach would have re-
quired a detailed analysis of each sampler location which was beyond
the scope of this effort, the former procedure was chosen.
Projected Concentrations
The modeling described above, coupled with the growth rates presented
in the previous section, allows for projections of the total air qual-
ity to 1975, 1980, and 1985 while maintaining an understanding of the
contribution from the different types of sources of particulate matter:
fugitive dust, point sources, area sources. The percentage contribu-
tion of each of these sources to the increase in concentration (Adj.
146
-------
o
AQ minus the background contribution of 30 ug/m ) is given in Table 24
for 1972. The current air quality is basically assumed to change di-
rectly with the changes projected by the emission growth rates. Under
the model used for area and point sources, this provides the exact
changes; however, for the point sources, some inaccuracy occurs.
While the projected growth rates (base year 1975) for particulates are
quite small, meaning any inaccuracy due the above assumptions is mini-
mal, the reduction between 1972 and 1975 as a result of emission regu-
lations is appreciable, allowing much more chance for error. To pre-
clude this occurrence, the CDM model was run for the projected 1975
emissions inventory, which was derived by applying the State regula-
tions to all point sources over 100 tons/year (see Appendix G). This pro-
vides a new projected set of concentrations, adjusted to 1975. The
change in concentration between before and after the regulations are
applied is calculated (Table 25) and used as the growth rate for point
sources between 1972 and 1975.
Applying the various growth rates to the contributions from each source
sector and adjusting for the background levels, percentage contribu-
tions and projected total fitted plus background concentrations for
1975, 1980 and 1985 are calculated. These values are given in
Tables 26, 27, and 28. The projected total fitted plus background
concentrations for the years 1972, 1975, 1980 and 1985 are again pre-
sented in Table 29.
In spite of the SIP attainment strategies, the concentration of sus-
3
pended particulates for 1975 will still be above the primary (75 p.g/m )
3
and secondary (60 p.g/m ) air quality standards at several stations,
especially in Denver County. The measurement locations in Adams,
Arapahoe, Boulder, Clear Creek, Douglas, Jefferson, and Larimer Coun-
ties are projected to be at or below the primary standard. Gilpin
County should really be included in this list since the 1972 average
147
-------
Table 24. PERCENTAGE CONTRIBUTION OF PARTICIPATE SOURCE SECTORS
1972
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Location
Westminster
Aurora
Brighton
Adams City
Cherry Creek Dam
Englewood
Littleton
Boulder
Longmont
Idaho Springs
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Sewer Plant
Sch. Admin. Bldg. (State)
Gates Building
Sch. Admin. Bldg. (EPA)
2105 Broadway
Castle Rock
Black Hawk
Rocky Flats
Golden
Lakewood
Edgewater
Arvada
La Porte
Fort Collins
Loveland
Greely
Ft. Lufton
Greely
Johnstown
Windsor
% Contribution
a
Point
19
15
29
39
15
20
38
2
4
8
6
7
10
Area
45
--
—
22
__
53
30
79
38
--
26
34
40
21. 29
18
19
21
19
17
17
1
25
29
26
54
14
25
6
6
18
7
13
4
6
13
35
29
35
30
--
--
—
--
--
20
24
__
47
47
14
—
14
--
--
Fug.
Adj. AQ
36 70
85
71
39
35
27
32
19
58
92
68
59
50
50
69
46
50
46
53
83
99
75
71
74
25
62
75
47
47
68
93
73
96
94
47
51
68
41
64
59
75
77
41
98
108
122
122
97
131
122
131
118
35
98
44
45
60
118
66
37
69
69
89
76
89
75
75
j*Based on 1972 NEDS.
Adj. AQ is the fitted air quality adjusted for background contributions
in
148
-------
Table 25.
CALCULATED PARTICULATE CONCENTRATIONS DUE TO POINT
SOURCESa - 1972 AND 197 5b
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Location
Westminster
Aurora
Brighton
Adams City
Cherry Creek Dam
Englewood
Littleton
Boulder
Longmont
Idaho Springs
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Sewer Plant
Sch. Admin. Bldg. (State)
Gates Building
Sch. Admin. Bldg. (EPA)
2105 Broadway
Castle Rock
Black Hawk
Rocky Flats
Golden
Lakewood
Edgewater
Arvada
La Porte
Fort Collins
Loveland
Greely
Ft. Lufton
Greely
Johns town
Windsor
Concentration
°/ T»r-,r1l-«r-i+-*1-i
1972
9
3
7
17
2
8
13
1
2
1
5
6
12
22
14
22
22
22
18
1
1
4
5
9
56
6
2
3
3
13
4
9
2
3
1975b
1
\ /O i.XC ^-i \JL\~- L, J.UL1
89
1 67
3 57
8 53
0 | 100
1 88
3 77
0 100
1
0
! 50
100
1 80
2
2
67
83
3 86
6
4
3
4
5
0
0
2
57
82
86
82
72
100
100
50
2 60
1 89
4
1
0
-«
1
2
1
1
0
0
93
83
100
67
67
85
75
89
100
100
Calculated with the Climatological Dispersion Model.
""1972 NEDS data with Colorado regulations applied to all point sources
over 100 tons/year.
149
-------
Table 26. PERCENTAGE CONTRIBUTION OF PARTICULATE SOURCE SECTORS'
1975
County j
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Location
Westminster
Aurora
Brighton
Adams City
Cherry Creek Dam
Englewood
Littleton
Boulder
Longmont
Idaho Springs
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Sewer Plant
Sch. Admin. Bldg. (State)
Gates Building
Sch. Admin. Bldg. (EPA)
2105 Broadway
Castle Rock
Black Hawk
Rocky Flats
Golden
Lakewood
Edgewater
Arvada
La Porte
Fort Collins
Loveland
Greely
Ft. Lufton
Greely
Johnstown
Windsor
% Contribution
Point
3
6
12
19
— —
3
9
--
2
--
1
2
2
3
8
4
3
4
5
--
--
12
11
4
4
3
_-
2
2
3
2
2
2
2
Area
60
--
--
35
. —
71
52
87
44
--
32
40
47
39
17
47
40
47
39
--
--
— ~
--
--
48
33
__
54
54
19
--
18
--
--
h
Fug. jAdj. AQ~
37
94
88
46
100
26
39
13
54
100
67
58
51
58
75
49
57
49
56
100
100
88
89
96
48
64
100
44
44
78
98
80
98
98
63
43
45
57
37
58
48
75
75
39
92
101
110
101
85
114
102
114
103
34
97
37
38
50
69
59
34
70
70
83
73
82
73
72
Based on application of current regulations.
Adj. AQ is the fitted air quality adjusted for background con-
tributions in
150
-------
Table 27. PERCENTAGE CONTRIBUTION OF PARTICULATE SOURCE SECTORS3
1980
1
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
1
Location
Westminster
Aurora
Brighton
Adams City
Cherry Creek Dam
Englewood
Littleton
Boulder
Longmont
Idaho Springs
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Sewer Plant
Sch. Admin. Bldg. (State)
Gates Building
Sch. Admin. Bldg. (EPA)
2105 Broadway
Castle Rock
Black Hawk
Rocky Flats
Golden
Lakewood
Edgewater
Arvada
La Porte
Fort Collins
Loveland
Greely
Ft. Lufton
Greely
Johns town
Windsor
7o Contribution |
Point
3
1
15
19
_ _
3
10
_ _
2
--
1
2
Area
62
—
j . Fu§- iAdi. AQ
35 67
93 44
1 85 46
36 45 59
» „
73
54
88
47
--
32
39
100
37
i 24 60
36 49
12 78
51 | 78
100 43
67 99
59 109
2 45 53 117
3 38
7
4
3
4
4
--
--
13
11
5
4
3
_ ..
2
2
4
18
2
2
2
16
46
39
46
38
--
--
_ _
—
—
45
32
_ _
60
60
22
--
21
—
--
59 i 108
77
50
58
77
58
100
100
87
89
95
51
65
100
38
38
74
82
77
98
98
90
123
110
123
111
36
98
38
39
53
73
64
34
76
76
85
81
85
73
72
i5ased on application of current regulations.
Adj. AQ is the fitted air quality adjusted for background con-
tributions in
151
-------
Table 28. PERCENTAGE CONTRIBUTION OF PARTICULATE SOURCE SECTORS'
1985
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Location
Westminster
Aurora
Brighton
Adams City
Cherry Creek Dam
Englewood
Littleton
Boulder
Longmont
Idaho Springs
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Sewer Plant
Sch. Admin. Bldg. (State)
Gates Building
Sch. Admin. Bldg. (EPA)
2105 Broadway
Castle Rock
Black Hawk
Rocky Flats
Golden
Lakewood
Edgewater
Arvada
La Porte
Fort Collins
Loveland
Greely
Ft. Lufton
Greely
Johnstown
Windsor
7o Contribution
Point
3
9
17
21
•. —
4
12
__
2
--
1
2
2
3
7
4
3
4
4
--
—
17
16
5
3
3
_ -
3
3
5
3
2
3
4
Area
65
— «
. .
37
Fug.
Adj. AQb
32 68
91 44
83 I 46
42
!
100
76 20
55
88
50
--
32
39
45
37
16
46
39
46
38
--
--
_ _
33
86
37
63
51
12 83
48
100
67
59
53
60
77
50
58
50
58
100
100
83
84
95
45
33
__
64
64
25
--
24
--
—
52
64
100
33
33
70
97
74
97
96
80
46
107
117
125
115
97
132
118
132
119
38
99
38
38
56
77
68
34
83
83
89
73
88
74
73
p
Adj. AQ is the fitted air quality adjusted for background contri-
butions in
Based on application of current regulations.
152
-------
Table 29. FITTED PARTICULATE AIR QUALITY FOR 1972,1975,1980,1985a'b
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Location
Westminster
Aurora
Brighton
Adams City
Cherry Creek Dam
Englewood
Littleton
Boulder
Longmont
Idaho Springs
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Sewer Plant
Sch. Admin. Bldg. (State)
Gates Building
Sch. Admin. Bldg. (EPA)
2105 Broadway
Castle Rock
Black Hawk
Rocky Flats
Golden
Lakewood
Edgewater
Arvada
La Porte
Fort Collins
Loveland
Greely
Ft. Lufton
Greely
Johns town
Windsor
1972
70
47
51
68
41'
64
59
75
77
41
98
108
122
122
97
131
122
131
118
35
98
44
45
60
118
66
37
69
69
89
76
89
75
75
1975
63
43
45
57
37
58
48
75
75
39
92
101
110
101
85
114
102
114
103
34
97
37
38
50
69
59
34
70
70
83
73
82
73
72
1980
67
44
46
59
I
! 37
60
49
78
78
43
99
109
117
108
90
123
110
123
111
36
98
38
39
53
73
64
34
76
76
I
85
81
85
73
72
1985
! 68
44
46
86
37
63
51
83
80
46
107
117
125
115
97
132
118
132
119
38
99
38
38
56
77
68
34
83
83
89
73
88
74
73
Adjusted AQ is the fitted air quality adjusted for background con-
tributions in
1975-1985 based on application of current regulations.
153
-------
3
measured concentrations of 66 ng/m indicates that the estimate of
fugitive dust source strength was in error. The values for Weld
County are only slightly above the primary standard. This indicates
that the current regulations are not sufficient for the attainment of
secondary standards throughout the AQMSA or for the primary standards
in Denver County. Therefore, more strict controls are assumed to be
necessary to provide the attainment of standards.
To estimate the additional percentage of reduction in man-made emis-
sions necessary to attain the particulate air quality standards after
consideration of the current regulations, the proportional rollback
technique can be used on the 1975 data in Table 26 . Thus, the addi-
tional reduction necessary to achieve the primary standard in downtown
Denver would be
R = 1 x 100 = 46 percent
and for the secondary standard it is
R = ,,,_ - x 100 = 64 percent
In the more rural regions, the attainment of the secondary standards
requires a further reduction of
R = R, -Q x 100 = 43 percent
Such contingency planning, which is essential prior to the final devel-
opment of maintenance planning, is addressed in Section V of this report.
A review of Table 29 indicates that there is an upward trend in pro-
jected particulate concentrations over the 10-year period (1975-1985).
154
-------
Increases range from 0 to 54 percent with most increases less than 20 per-
cent. These increases are what the maintenance planning should be geared
to. The 10-year projection of air quality shows that, with the possible
exception of Arapahoe, Douglas, Gilpin, and Jefferson Counties, all or
parts of the remaining counties would also exceed the primary standard for
suspended particulates if no further attainment or maintenance controls are
implemented. Section VI of this report discusses what maintenance strat-
egies might be used.
It should be noted that this growth of particulate concentrations is not
in agreement with the projected air quality provided in the EPA Plan
Revision Management System (PRMS) for the Metropolitan Denver Intrastate
o
AQCR. The PRMS projects a decreasing concentration of particulates with
a leveling off between 1975 and 1978. It is felt that the projections
provided in this report are more representative of the expected situation
due to the inclusion and detailed analysis of fugitive dust contributions.
CARBON MONOXIDE
Summary of Observed Concentrations
Nearly continuous measurements of carbon monoxide by nondispersive infra-
red instrumentation are available from the CAMP station in the Denver
Central Business District (CBD) from January 1971 through July 1973 with
the exception of the period from June through September in 1971. Ob-
servations were made by five additional state-operated monitors located
within the Denver area during much of 1973. The highest and second
highest one-hour and eight-hour concentrations at these sites, and the
periods covered, are given in Table 30. The eight-hour concentrations
reported in this table are based on three discrete eight-hour periods per
day beginning at midnight as recommended in a draft report 13 from the
ft
EPA Guideline Series. When these results are compared with the national
*A recent revision to the referenced guideline recommends the use of the
8-hour running mean in place of the three discrete periods.
155
-------
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156
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ambient standards of 40 mg/m^ (35 ppm) for one-hour and of 10 mg/m^
(9 ppm) for eight-hours, it is clear that control measures adequate to
ensure meeting the eight-hour standard will be more than adequate to
ensure meeting the one-hour standard, as has been found to be generally
true in all urban areas.
•I O
According to current EPA procedures each site is allowed one excursion
above the standard per calendar year, and the percent reduction in emis-
sions required is consequently to be determined from the second-highest
concentration observed during the year. Examination of the second highest
eight-hour concentrations listed in Table 30 shows that the two highest
such concentrations, 31.6 mg/nr and 31.3 mg/m^, occurred at the CAMP sta-
tion in 1971 and 1972, respectively. The relatively low value reported
for 1973 is for a partial year only and should not be taken as an in-
o
dication of improving air quality. The use of 31.6 mg/m in the propor-
tional model gives a required reduction in emissions of
R = , ' " Q x 100 = 68 percent
Carbon monoxide emission density maps calculated from traffic data,
presented in Appendix L, for the Denver area show the highest concentra-
tion of emissions in the vicinity of the CAMP station (see Figure 31).
It is reasonable to assume that this location is representative of maxi-
mum concentrations not only within Denver but also within the entire AQMSA
with the possible exceptions of short-term concentrations near relatively
narrow strips of heavily traveled highways or intersections where traffic
congestion is created by indirect sources. This conclusion tends to be
supported by the limited measurements made at the other sites to date.
Of the five second-highest concentrations reported in Table 30 at these
sites, the highest, measured at Julian Street, was 27.6 mg/nr1 and indi-
cates a required reduction of 64 percent. The second highest such value,
o
measured at East Coifax and Colorado Boulevard, was 26.9 mg/m , indicating
a required reduction of 63 percent. The maximum reduction indicated at
any of the remaining sites is 50 percent.
157
-------
Because carbon monoxide from vehicular emissions is primarily a local
problem, emissions are calculated for a three-square-mile core area
of the City of Denver for use with the CAMP data in proportional modeling.
From the results, an allowable emission density is calculated for
general planning purposes. It must be understood, however, that an area
which meets the allowable emission density requirement may still experience
local problems in the vicinity of streets with exceptionally high traffic
volume or with long periods of traffic congestion. The detection and
elimination of such possible problem areas is a major requirement of any
air quality attainment plan. However, a street-by-street analysis of the
metropolitan areas within the AQMSA is beyond the scope of the present
effort.
No carbon monoxide data are available for cities within the AQMSA other
than for those listed in Table 30. In lieu of measurements, carbon
monoxide emission densities were calculated for three of the largest
cities--Boulder, Fort Collins, and Greeley—and compared with the emis-
sion density within a comparably sized central area of Denver.
The three- and twelve-square-mile core and central areas used for the
Denver carbon monoxide emission calculations referred to above were chosen
to correspond as closely as possible to the core and central areas referred
to in an earlier study by TRW.
Projected Carbon Monoxide Emissions and Ambient Concentrations
Using traffic projections, based on the JRPP transportation and land use
plan, and procedures summarized in Section III (see Appendix L for
details), average carbon monoxide emission densities per day were cal-
culated at the 240 points of the Denver metropolitan grid (Appendix L,
Figure L-2). Isopleths of the resulting emission densities for 1975,
1980, and 1985 have been superimposed on an outline map of Denver County
and the surrounding area in Figures 29, 30, and 31, respectively. These
projected emission density maps have three principal characteristics.
158
-------
Figure 29. Isopleths of projected carbon monoxide emission densities
from motor vehicles in Denver County and surrounding areas
in 1975. Units are kg/mi2/day.
159
-------
Figure 30. Isopleths of projected carbon monoxide emission densities
from motor vehicles in Denver County and surrounding area
in 1980. Units are kg/mi2/day.
160
-------
Figure 31. Isopleths of projected carbon monoxide emission densities
from motor vehicles in Denver County and surrounding area
in 1985. Units are kg/mi^/day.
161
-------
First, maximum emissions occur near the center of the CBD. Second, emis-
sions within Denver decrease markedly over each five-year period. Third,
emissions decrease generally throughout the entire area, indicating that
reductions in average tailpipe emissions more than compensate for pro-
jected growth in vehicular traffic in all major sections of the metropol-
itan area.
Table 31 lists the total vehicular emissions per day expected within the
three-square-mile core area of Denver at the end of each year from 1971
to 1990, calculated from traffic projections based on the JRPP plan and
emissions based on continued implementation of the Federal Motor Vehicle
Control Program (FMVCP). (Emission and deterioration factors for dif-
ferent model years under the FMVCP are given in Appendix L.) The total
vehicular emissions for the years 1977 through 1985 are distributed by
vehicle class in the next five columns.
According to EPA, Region VIII, it is currently felt that the following
transportation control strategies can be implemented on or before 1977:
1. Semi-annual inspection and maintenance using the idle
test mode (failure rate = 50 percent).
2. Air bleed retrofit on pre-1968 light duty vehicles.
3. Air bleed retrofit with exhaust gas recirculation
on 1968 to 1974 light duty vehicles.
4. A maximum reduction in light duty vehicle VMT of
15 percent for all VMT-reducing strategies. (See
Section V for a further discussion of these
measures.)
Strategies 1, 2, and 4 were promulgated by EPA on November 7, 1973
(38 FR 30818); Strategy 3 is a proposed replacement for the high altitude
modification promulgated at that time.
162
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An evaluation of the effectiveness of the first three strategies is in
progress and the results of the very limited test data collected to date
have been applied to obtain the emissions listed under the heading "With
strategies" in Table 31. The percent reductions, representing best cur-
rent estimates, are given at the bottom of the table. Allowable emissions
for the core area are calculated by assuming that a 68 percent reduction
in end-of-year 1971 emissions is required. Thus,
Allowable Emissions = 0.32 X 41,139 = 13,164 kg/day
and,
-i o I f i f\
Allowable Emission Density = —f = 4,388 kg/mi /day
The additional required reductions shown at the right of the table should
be compared to the 15 percent reduction considered feasible under Strategy
No. 4. These calculations indicate that the eight-hour standard will not
be achieved before the end of 1979 even with the use of the JRPP plan and
the four strategies listed above; thus some modification of the current
Transportation Control Plan appears to be necessary if the standard is to
be achieved in 1977. On the other hand, the calculations indicate that
maintenance of the standard, once it is achieved, can be accomplished
principally by the JRPP plan. It is also evident from Table 31 that emis-
sions from heavy duty vehicles play an increasingly important part in
total vehicular emissions during this period, and that control of emis-
sions from this class of vehicles could be an effective strategy. The
trend in carbon monoxide emissions expected to result from the FMVCP and
other control strategies shown in Table 31—and consequently the expected
trend in air quality—is presented in Figure 32.
It should be pointed out that emissions in Table 31 have been entered to
the nearest kg/day to illustrate trends and relative contributions, and
to avoid confusion due to roundoff. This apparent precision should not be
taken as an indication of the accuracy of the prediction methodology.
164
-------
40,000
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20,000
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TOTAL VEHICULAR EMISSIONS
(FMVCP + JRPP)
SCHEDULED
TAIL PIPE
CONTROLS
15 % VMT
REDUCTION (LDV)
70 72 74 76
78 80 82
YEAR
84
86 88 90
Figure 32. CO emissions within Denver core area
165
-------
Figure 33 is a plot of city-wide carbon monoxide emission density within
Fort Collins (7.362 mi2), Boulder (13.092 mi2), and Greeley (9.185 mi2)
with that of the twelve-square-mile central area of Denver used for com-
parison. These projections are based on the JRPP plan and the FMVCP and
do not contain the effect of the promulgated strategies. Examination of
these curves shows that emission densities within these cities should be
within the allowable value of 4,388 kg/mi/day estimated for Denver
throughout 1975 to 1985 without the implementation of additional strat-
egies. But it should be noted that the effects of differences in to-
pography, city structure, street and highway configuration, and meteo-
logy are not accounted for by a simple emission density comparison.
PHOTOCHEMICAL OXIDANTS
Summary of Observed Concentrations
Measurements of total oxidants were made at the Denver CAMP station by the
alkaline KI method from 16 July 1970 through 19 May 1971 and from 1 Octo-
ber 1971 through the remainder of 1971. The analysis method was changed
to calorimetric neutral KI at the beginning of 1972 and continued as such
through July 1973. The highest and second highest one-hour average con-
centrations measured by these methods during these three years were,
respectively: 1971 - 392 and 353 ^g/m3 (0.20 and 0.18 ppm); 1972 - 353
and 333 (ag/m3 (0.18 and 0.17 ppm); and 1973 - 235 and 235 |_ig/m3 (0.12 and
0.12 ppm). Using the relationship between hydrocarbon emissions and
ambient photochemical oxidant concentration as defined in Appendix J,
40 CFR Part 51 (36 FR 15502) and an oxidant concentration of 353 [ig/m3
(0.18 ppm) yields a required reduction in hydrocarbon emissions of 60 per-
cent, which is the value used for transportation control promulgation by
EPA in November 1973 (38 FR 30818).
In 1973 measurements were begun at the CAMP station using the approved
chemiluminescence method, and five additional sites using this method
were also activated within the Denver area by the state. The results are
shown in Table 32. The second highest one-hour concentration observed at
o
any of these locations was 490 |ig/m (0.25 ppm). Careful examination of
166
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YEAR
Figure 33. Carbon monoxide emission densities for four cities
in the Denver AQMSA.
168
-------
all 1973 data plus more recent data may show that the high levels reached
within the area on 13 August were episodic in nature and that a lower
value than 490 ng/m^ could properly be used for long range planning.
Also, as comprehensive data from the expanded network becomes available,
the use of a more broadly based index than the currently recommended-^
second highest one-hour concentration may become appropriate for rollback
calculations. However, unless subsequent developments indicate otherwise,
o
reduction estimates should be based on the observed value of 490 (j.g/m in
line with the current EPA guidelines. The use of 490 jj.g/nr in conjunction
with Appendix J yields a required reduction in hydrocarbons of approxi-
mately 82 percent. The use of a straight percentage rollback would re-
quire a reduction of approximately 67 percent. Because of serious uncer-
tainties in using Appendix J with high pohtochemical oxidant values, EPA
has allowed states to use Appendix J type relationships derived from
local data or to employ linear rollback--hence, since no Denver Appendix
J has been developed, the rollback estimate will be used to estimate al-
lowable emissions in the discussion which follows.
Hydrocarbon Emissions and Ambient Oxidant Concentrations
Figures 34, 35, and 36 are hydrocarbon emission density maps for the
Denver area based on projected vehicular emissions for 1975, 1980, and
1985, respectively. As was the case with carbon monoxide, the maximum
emissions occur near the CBD and the trend is for reduced emissions
throughout the area.
Table 33 lists the total daily vehicular emissions by year for the 960-
square-mile Denver metropolitan area calculated from traffic projections
based on the JRPP transportation and land use plan and emissions based on
the FMVCP. These total emissions are then broken down by vehicle type for
the years 1977 to 1985 in the next five columns. The emissions expected
after the currently planned transportation control strategies (see dis-
cussion, page 162) are shown under the heading "With Strategies." In
contrast to carbon monoxide, non-vehicular sources contribute substantial
amounts of hydrocarbons to the Denver area. Consequently, emissions from
169
-------
Figure 34. Isopleths of projected hydrocarbon emission densities from
motor vehicles in Denver County and surrounding area in
1975. Units are kg/mi2/day.
170
-------
Figure 35. Isopleths of projected hydrocarbon emission densities from
motor vehicles in Denver County and surrounding area in
1980. Units are kg/mi2/day.
171
-------
Figure 36. Isopleths of projected hydrocarbon emission densities from
motor vehicles in Denver County and surrounding area in
1985. Units are kg/mi2/day.
172
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these stationary sources must be considered when projecting air quality.
In Table 33 it has been assumed that the ratio of stationary emissions
(plus aircraft) to vehicular emissions given by the 1972 NEDS inventory
for the Denver AQGR applies to the 960-square-mile area. It has also been
assumed that the regulations introduced for the control of stationary
sources will have the overall effectiveness indicated by the Colorado
Transportation and Land Use Plan and by the EPA-promulgated transpor-
tation control plan. The additional reduction in hydrocarbon emissions
required from VMT-reducing strategies, based on a reduction of 67 percent,
is shown at the right of the table. In making these estimates, the al-
lowable emissions were calculated from mid-1973 vehicular and stationary
source emissions as follows:
(203,617+197,720)
The results shown at the right of Table 33 indicate that the ambient
oxidant standards will not be met until 1982 simply by the use of the
planned inspection and maintenance and retrofit programs even if the JRPP
plan is followed. Table 33 further shows that the additional reduction
required beyond that provided by these programs, when expressed as a re-
duction in light-duty VMT, exceeds the 15 percent expected from currently
promulgated plans (38 FR 30820) until sometime in 1981. Once attainment
is achieved, however, maintenance can be seen to follow as a matter of
course due to the reducing emissions from vehicular sources. Figure 37
presents the emission trend data from Table 33.
NITROGEN OXIDES
Summary of Observed Concentrations
The only reported set of nitrogen dioxide measurements made with a cur-
rently acceptable analytical method that is also statistically adequate
for the determination of an annual mean was collected at the CAMP station
in Denver in 1972. The annual arithmetic mean obtained from 6759
174
-------
250,000
200,000
D
"D
O>
Z
o
TAIL PIPE k
CONTROLS J \l
15% VMT "1
REDUCTION ^
(LDV) J
ALLOWABLE
ct
Z
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70 72 74 76 78 80 82
YEAR
84 86 88 90
Figure 37. HC emissions within Denver metropolitan area
175
-------
one-hour observations made by an instrumental colorimetric method during
the year was 73 n.g/m-', substantially lower than the national ambient
standard of 100 p.g/m .* Other data collected in Denver as part of the
field program to reevaluate the reference method for the measurement of
nitrogen dioxide, and summarized in the June 8, 1973 Federal Register
(38 FR 15174), suggest that the annual average does not exceed the stan-
dard, but are too limited to provide meaningful estimates of the annual
mean.
Projected Emissions and Concentrations of Nitrogen Oxides
Figures 38, 39, and 40 are nitrogen oxide emission density maps calculated
from projected vehicular sources in the Denver area in 1975, 1980, and
1985, respectively. Reflecting the annual changes in emission factors,
little change occurs in the emission pattern between 1975 and 1980 but a
marked decrease in the emission level takes place between 1980 and 1985.
No area with significantly increasing emissions--indicating deteriorating
air quality—is predicted due to the projected changes in vehicular travel
during the 10-year period.
Table 34 lists the calculated daily vehicular emissions for the 960-
square-mile Denver metropolitan area, broken down by vehicle type, for the
period from 1971 through 1980. Inspection of the table shows that emis-
sions from light duty vehicles increase until 1977 and then decrease
through 1990, but remain essentially constant between 1975 and 1980. Emis-
sions from heavy duty vehicles and diesel powered vehicles increase slowly
from year to year reflecting a projected regular increase in traffic from
these relatively uncontrolled vehicle types. The two columns at the right
*It is the opinion of EPA, Region VIII, that annual means determined from
CAMP station data by the Saltzman Colorimetric Technique will also be
accepted as valid after further investigation. For the period 1965-1972,
annual means based on this method are available for 5 years and are:
1965 - 68 M.g/m3; 1966 - 64 ^g/m^; 1969 - 62 \ig/m$; 1970 - 72 ug/nv3; and
1972 - 73 |ig/m3.
176
-------
Table 34. VEHICULAR EMISSIONS OF NITROGEN OXIDES WITHIN
DENVER METROPOLITAN AREAa
Emissions (kg/day)
Year
(31 Dec)
1971
1972
1973
1974
1975
1976
1977
1978
1979
1980
1981
1982
1983
1984
1985
1986
1987
1988
1989
1990
FMVCP with JRPP
traffic projections
Total
37,987
41,580
43,653
44,518
44,996
45,711
46,176
46,027
46,153
46,174
44,785
41,918
39,762
37,571
34,198
32,845
31,680
30,016
29,284
28,667
LDV
33,222
36,584
38,428
39,063
39,310
39,815
40,046
39,660
39,549
39,332
37,704
34,610
32,216
29,784
26,172
24,582
23,181
21,278
20,309
19,456
HDV
3909
4098
4285
4474
4663
4835
5028
5222
5417
5613
5809
5994
6191
6389
6586
6782
6976
7172
7369
7563
Other
856
898
939
981
1023
1061
1103
1145
1187
1229
1271
1313
1355
1398
1440
1481
1523
1564
1606
1648
With strategies
LDV
33,413
33,843
34,039
33,711
33,617
33,432
32,048
29,418
27,384
25,316
22,246
Total
39,100
39,739
40,170
40,078
40,221
40,274
39,128
36,725
34,930
33,103
30,272
£5
Metropolitan area comprises 960 square miles.
15 percent reduction in light-duty vehicle VMT.
177
-------
Figure 38. Isopleths of projected vehicular emissions of nitrogen oxides
in Denver County and the surrounding area in 1975. Units
are kg/tni^/day.
178
-------
Figure 39.
Isopleths of projected vehicular emissions of nitrogen oxides
in Denver County and surrounding area in 1980. Units are
kg/mwday.
179
-------
Figure 40. Isopleths of projected vehicular emissions of nitrogen oxides
in Denver County and surrounding area in 1985. Units are
kg/mi2/day.
180
-------
in the table show the effect of the 15 percent decrease in light-duty-
vehicle VMT assumed to be achievable under the existing transportation
control plans (38 FR 30820). The maximum total vehicular emissions pre-
dicted under these assumptions is 40,170 kg/day and is approximately that
calculated for the year 1972 when the annual mean nitrogen dioxide con-
centration was 73 percent of the standard. These calculations therefore
indicate that a substantial increase in emissions from other sources
could be tolerated without exceeding the standards. For example, the 1972
NEDS inventory for the Metropolitan Denver AQCR shows that emissions from
non-vehicular sources are approximately equal to those from highway vehi-
cles. Consequently, emissions from these non-vehicular sources could in-
crease at an annual rate of about 6.5 percent between 1972 and 1980 when
vehicular emissions start decreasing , without exceeding the allowable
emissions for the area of 108,996 kg/day.* In contrast, emissions of
nitrogen oxides from non-vehicular sources, excluding power plants, are
estimated to increase at less than 2 percent per year, and no additional
major power plants are currently scheduled for the metropolitan area
according to EPA, Region VIII. Therefore, barring the introduction of
currently unscheduled major uncontrolled sources, no violation of the
nitrogen dioxide standard is indicated during the forecast period.
*Allowable emmissions = twice the vehicular emission rate for mid-1972
(37,987 + 41,580) divided by 0.73, or 108,996 kg/day. Acceptable growth
A
rate obtained from P = .. J^n where P = 41,580, A^ = (108,996 - 40,274)
and n = 8. U '
181
-------
REFERENCES
1. U.S. Environmental Protection Agency. Air Quality Data - 1972
Annual Statistics. Publication Number EPA-450/2-74-001, Research
Triangle Park, N.C., March 1974.
2. U.S. Environmental Protection Agency. Guideline for the Evaluation
of Air Quality Trends. Guideline Series OAQPS No. 1.2-014, Research
Triangle Park, N.C., February 1974.
3. U.S. Environmental Protection Agency. The Plan Revision Management
System, Region VIII. OAQPS, Research Triangle Park, N.C., March
1974.
4. U.S. Environmental Protection Agency. Guidance for Air Quality
Monitoring Network Design and Instrument Siting. Draft Report,
Guideline Series OAQPS No. 1.2-012, Research Triangle Park, N.C.,
January 1974.
5. GCA/Technology Division. Idaho Particulate Matter Study. Draft
Final Report, U.S. Environmental Protection Agency, Contract No.
68-02-0041, Task Order No. 9, Bedford, Mass., October 1973.
6. Colorado Department of Health, Air Pollution Control Division.
Air Quality Implementation Plan for State of Colorado. Denver,
Colorado, January 1972.
7. U.S. Environmental Protection Agency. Guide for Compiling a
Comprehensive Emission Inventory (Revised). Monitoring and Data
Analysis Division, Office of Air and Water Programs, Office of Air
Quality Planning and Standards, Research Triangle Park, N.C.,
Publication Number APTD-1135, March 1973.
8. Research Triangle Institute. Computer Assisted Area Source Emis-
sions Gridding Procedures, Users Manual. EPA No. 68-02-1014.
9. PEDCo - Environmental Specialists, Inc. Investigation of Fugitive
Dust Sources, Emissions, and Control for Attainment of Secondary
Ambient Air Quality Standards (Colorado). Suite 13, Atkinson Square,
Cincinnati, Ohio 45246, EPA Contract No. 68-02-0044, Task Order
No. 16.
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10. Busse, A.D. and J. R. Zimmerman. User's Guide for the Climatological
Dispersion Model. EPA-R4-73-024, December 1973.
11. Gifford, F.A. and S.R. Hanna. Urban Air Pollution Modeling. Pro-
ceedings of the Second International Clean Air Congress, Washington,
B.C., December 6-11, 1970.
12. Hanna, S.R. A Simple Method of Calculating Dispersion From Urban
Area Sources. J. Air Poll. Contr. Assoc., 21:774-777, 1971.
13. U.S. Environmental Protection Agency. Guidelines for Interpretation
of Air Quality Standards. Draft Report, Guideline Series OAQPS
No. 1.2-008, Research Triangle Park, N.C., October 1973.
14. Larsen, R.I. A Mathematical Model for Relating Air Quality Measure-
ments to Air Quality Standards. U.S. Environmental Protection
Agency, Research Triangle Park, N.C., Office of Air Programs Publica-
tion No. AP-89, November 1971.
15. U.S. Environmental Protection Agency. Transportation Control
Strategy Development for the Denver Metropolitan Area. Research
Triangle Park, N.C., APTD-1368. Prepared by TRW Transportation
and Environmental Operations, December 1972.
16. Colorado Department of Health. The State of Colorado Air Pollution
Control Transportation and Land Use Plan. Denver, Colo., May 1973.
183
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SECTION V
CONTINGENCY ATTAINMENT STRATEGIES
INTRODUCTION
The attainment strategy is considered separately from the maintenance
strategy due to the different thrust of their control measures. Attain-
ment measures are primarily directed at the reduction of emissions from
existing sources, either by a direct control on the emissions them-
selves (e.g., a process rate or fuel content regulation), or by reducing
the number of certain types of sourceg of emissions (e.g., banning open
burning, VMT reductions). Maintenance measures, on the other hand, are
aimed at controlling the growth of emissions which would bring about an
infraction of the air quality standards. Such measures are then
directed at controlling the amount of growth, either the growth directly
(e.g., zoning approvals) or the emissions from the growth (e.g., New
Source Performance Standards), or the location of the future sources
(e.g., emission density zoning, regional development planning).
For the State of Colorado, attainment measures operate to reduce con-
centrations to the National Ambient Air Quality Standards within the
timeframe of the 1977 deadline. Maintenance measures, however, are
directed at the following period of time though they are also contin-
uously applicable from the time of implementation.
The projections of concentrations in the previous section demonstrated
that, given previously quantified control regulations and air quality
trends, the primary and secondary standards of total suspended
184
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particulates, carbon monoxide, and photochemical oxidants would not be
achieved by the specified attainment dates. Since the attainment of
the desired air quality is an integral part of the Air Quality Main-
tenance Plan development, it is essential to discuss those measures
which must be implemented to ensure attainment of the standards.
This section discusses transportation control measures and fugitive
dust control measures as a contingency attainment strategy package.
The measures are presented as a means of ensuring the effectiveness and
integrity of the Colorado SIP as well as the AQMP supplement to the plan.
TRANSPORTATION CONTROLS
Promulgated Transportation Control Plan
The U.S. Environmental Protection Agency (EPA) promulgated a Transporta-
tion Control Plan (TCP) for the Denver area in the Federal Register on
7 November 1973. The promulgated TCP includes several elements:
1. Program for inspection and maintenance of motor
vehicles, using the idle test mode, to be fully
implemented by 1 December 1975.
2. Program for equipping of pre-1968 model year
vehicles with engine air bleed devices, to be
implemented by 1 July 1976.
3. Program for modification of 1968-1975 model
year vehicles for high altitude, to be im-
plemented by 1 July 1976.
4. Program for control of hydrocarbon emissions from
stationary transportation, manufacturing, and
processing facilities.
5. Creation of bus-carpool lanes on existing roadways.
6. Limitation on construction of parking facilities,
to be implemented on 1 January 1975.
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7. Removal of on-street parking in the Denver
Central Business District (CBD).
8. Mass transit improvements.
9. Limitation on gasoline sales.
The last measure, namely the limitation of gasoline sales, was imposed
by EPA because the other measures are not expected to achieve as much
reduction in carbon monoxide emissions as is considered necessary to
meet the ambient air quality standards by the extended deadline of
31 May 1977. Carbon monoxide emissions were then thought to require a
64 percent reduction (from 1971 emissions); the gasoline limitation
was estimated to provide for a 6 percent reduction.
Section IV of this report discusses the present expectations of the
need for reducing emissions. It is indicated in Section IV that EPA
Region VIII now expects the TCP to be amended to include slightly dif-
ferent measures for inspection and maintenance and for modification of
existing automobile engines. The air quality estimates in that section
reflect this fact.
As shown in Tables 31 and 33, transportation control measures must be
able to reduce light duty vehicular travel by 34 percent to meet CO
standards and by 45 percent to meet applicable oxidant levels. Since
the first four transportation control measures listed have already been
incorporated into the air quality projection, the necessary reduction
must be achieved by the latter five measures.
In response to the EPA-promulgated TCP, the Air Pollution Control Com-
mission recently promulgated Regulation number 9 which deals explicitly
with measures 5 through 8 mentioned above. (It should be noted that as
of this writing this regulation has neither been approved by the Attor-
ney General of Colorado nor accepted by the EPA). Elements of Regula-
t ion number 9 are:
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1. Exclusive Bus-Carpool Lanes, to be implemented by
1 January 1976.
2. Creation of Park-N-Ride Facilities with express
buses to the CBD; with plan submission by 1 October
1974.
3. Carpooling programs, to be implemented by large em-
ployers (> 250 employees) by 1 April 1975, and by
other employers (50 to 250 employees) by 1 October
1975. In addition, employers must submit a descrip-
tion of incentives which encourage employees to make
use of mass transit facilities. Large employers
must submit their plan by 1 February 1975, with sub-
mittal by other employers by 1 August 1975.
In addition, the regulation requires that DRCOG submit recommendations
to the APCC by 1 March 1975 on parking requirements that may stimulate
the use of public transportation and decrease single passenger VMT.
As these latter control measures have only recently been promulgated
and are currently in the development stages, it is not yet possible to
precisely quantify the emission reduction potential of the measures.
If, however, the maximum possible expected reduction in VMT, estimated
by EPA Region VIII, is attained under these regulations, only a 15 per-
cent reduction is possible. This indicates that a further reduction
of 30 percent in VMT is required to meet the photochemical oxidant
standard. This is equivalent to a reduction of 10 percent in the hydro-
carbon emissions from the 1971 level. For carbon monoxide the addi-
tional reduction needed in light-duty VMT and total emissions from the
1971 level is 19 and 7 percent, respectively. This implies that the
control of hydrocarbon emissions will also bring about the needed con-
trol of carbon monoxide emissions if parallel reduction measures are
pursued.
As mentioned above, the TCP promulgated by EPA imposed gasoline sales
restrictions to provide for an additional 6 percent reduction in CO
emissions from the 1971 levels. These limitations also provide a 5
percent reduction in hydrocarbon emissions. From the above analysis
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it is evident that, since maximum feasible controls have already been
placed on the sources themselves, the gasoline limitation will have to
be doubled to provide for the additional 10 percent reduction in hydro-
carbon emissions.
An estimate of the impact of such a measure can be better determined
from considering the actual reductions in emissions from the projected
1977 levels instead of the 1971 emission levels presented above for
control measure evaluation. It has already been stated that these re-
ductions would be comparable to a 30 percent reduction in VMT in 1977.
From Table 33, it can be demonstrated that this is equivalent to 21
percent of all hydrocarbon emissions and 24 percent of all vehicular
emissions projected for 1977.
Since the impact of such a measure is potentially onerous from a social
and economic standpoint, no specific regulations for the implementation
of this measure are proposed at this time. Instead, continued monitor-
ing of air quality and investigation of alternative measures will be
increased. It is possible that greater than the 15 percent VMT reduc-
tion may be achieved by the state through the currently promulgated
regulations or additional measures which may be implemented by the
state, or that such a large VMT reduction may prove to be unnecessary
based upon 1976 air quality data.
The extent of any gasoline sales limitation is contingent upon the de-
termination of the effect of the currently promulgated transportation
control plan, with its supporting regulations, on the air quality. As
EPA's gasoline sales limitation regulation requires the state to make
this determination on the basis of data collected during fiscal year
1976, no further regulations to ensure continued evaluation are needed
at this time.
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FUGITIVE DUST CONTROLS
Promulgated Fugitive Dust Control Plan
The Colorado Air Pollution Control Commission recently promulgated a
regulation dealing with fugitive dust. This regulation is discussed
in more detail in Section II and the regulation itself appears in
Appendix E. A brief summary of the regulation appears below.
1. A general statewide requirement is that no fugitive dust
be emitted which exceeds 20 percent visible opacity or
which is visible after it leaves the property of the
owner of the emission source. Certain activities, such
as agriculture, are exempted.
2. Within the Priority I portions of Air Quality Control
Regions only (see Figure 24), including a portion of
the AQMSA, specific requirements are established for
control of dust from:
a. All new unpaved roads and parking areas with traf-
fic volumes of 165 vehicles/day (vpd) or more.
b. Existing privately owned roads and parking areas
with 165 vpd or more.
c. Existing publicly owned roads and parking areas
with 165 vpd or more, but with controls only to
the extent allowed by financial resources.
d. Land development, construction demolition, and
related activities.
3. Specific control requirements, statewide, on open
mining activities.
4. Where specific requirements for controls are provided,
a requirement that permits be obtained and a requirement
that specified types of abatement and preventive measures
be identified in the permit and utilized.
Contingency Fugitive Dust Attainment Measures
The contingency attainment strategy for fugitive dust control consists
of the controls in the promulgated regulations along with the following
additions.
189
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First, the promulgated controls are to be applied to the entire AQMSA
and not just the Priority I area. Thus, Gilpin, Clear Creek, Douglas,
and Arapahoe will be subject to the controls along with the parts of
Larimer, Weld, and Adams Counties which are excluded from the Priority I
area.
Second, control measures for dust from sand on paved roads will be pro-
mulgated. As estimated in the PEDCo report, this will reduce dust from
sanding by 25 percent. A further reduction of dust could be accomplished
by promulgating controls for dust from cattle feedlots with the poten-
tial for reducing such emissions by 50 percent. However, the minor im-
pact such a strategy would have on the total level of emissions of
fugitive dust (less than 0.5 percent) and the resulting insignificant
improvement in air quality does not warrant the expense that would be
involved in its implementation. Similarly, it would not be politically
feasible to expect livestockmen to incur such costs as they are pres-
ently supporting the mass transit system through sales taxes.
The impact of this maximum control plan is calculated for the years
1975, 1980 and 1985 based on the calculations given in Appendix J of
this report. The growth rates under this level of control are presented
in Table 35 for the fugitive dust zones.
This strategy is seen to generally prevent future growth in fugitive
dust emissions in spite of increased source activity. Maximum fore-
casted emissions would be less than 1975 emissions except in a few
zones. The worst future emissions increases will be in Clear Creek
County where, as noted earlier, substantial construction activity will
occur. There, 1985 emissions are estimated to be 11 percent more than
1975 emissions with the promulgated regulations. Without the increased
degree of control, emissions would be almost twice as much in several
zones.
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Table 35. FUGITIVE DUST EMISSIONS GROWTH RATES BY ZONES
WITH MAXIMUM FEASIBLE CONTROLS
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Zone
1.
2.
1.
2.
3.
1.
2.
3.
Cropland
Rang el and
Cropland
Range land
Range land
Cropland
Rang el and
Woodland
Predominantly
woodland
Urban
Range land and
woodland
Predominantly
woodland
1.
2.
3.
1.
2.
3.
1.
2.
Urban
Rang el and
Woodland
Cropland
Woodland
Recreation land
Cropland
Range land
1975
0.95
0.91
0.90
0.88
0.88
0.99
0.98
0.98
0.64
0.80
0.59
0.83
0.82
1.00
1.00
0.98
0.90
0.90
0.99
0.94
1975-1980
0.98
0.97
0.89
0.87
0.87
0.99
0.97
0.97
0.93
0.88
0.80
0.84
0.96
1.08
1.08
0.99
0.94
0.94
0.99
0.96
1975-1985
0.95
0.92
0.88
0.85
0.85
0.99
0.97
0.97
1.11
0.96
1.02
0.84
1.04
0.95
0.95
0.99
0.93
0.93
1.00
0.97
Tabulated quantities are the ratios
feasible controls to 1975 emissions
of emissions with maximum
with present regulations.
191
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These strategies have the least effect in the counties (Larimer and
Weld and, to a lesser degree, Adams and Boulder) where agriculture is
the predominant source of fugitive dust. Emissions could be substan-
tially different from these estimates if the amount of agricultural
activity should change.
These controls are then used for projecting air quality to 1975, 1980
and 1985 along with the percentage contributions (see Tables 36, 37 and
38). As is seen in these tables, no appreciable improvements in air
quality results from this maximum control level. This control measure
for fugitive dust still does not provide for the attainment of the
primary NAAQS for particulates in Denver County and one site in Weld
County by 1975. A further reduction of
R = -rr-r - — x 100 = 40 percent
is necessary to meet the primary standard and a reduction of
R = ; ~_ 3Q x 100 = 60 percent
is necessary to meet the secondary standard in Denver County.
While sttainment has not resulted, the final goal of maintenance of air
quality has been aided as far as increased emissions from the fugitive
dust sources sector. This is apparent from Table 35 which shows that
most growth rates are less than 1.0 and from Tables 36 , 37 , and 38 ,
which indicate a decreasing percentage contribution from this sector.
OTHER AREA SOURCE ATTAINMENT MEASURES FOR PARTICULATES
As the maximum practical controls have already been applied to the
point and fugitive dust source sectors, the only remaining sector for
control is area sources. Data provided on the 1972 NEDS summary sheet
for Denver County indicated that 53 percent of the total area source
emissions in that county were a direct result of the burning of
192
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Table 36. PERCENTAGE CONTRIBUTION OF PARTICULATE SOURCE SECTORS
FOR MAXIMUM CONTROL CASE FOR FUGITIVE DUST
1975
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Location
Westminster
Aurora
Brighton
Adams City
Cherry Creek Dam
Englewood
Littleton
Boulder
Longmont
Idaho Springs
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Sewer Plant
Sch. Admin. Bldg. (State)
Gates Building
Sch. Admin. Bldg. (EPA)
2105 Broadway
Castle Rock
Black Hawk
Rocky Flats
Golden
Lakewood
Edgewater
Arvada
La Porte
Fort Collins
Loveland
Greely
Ft. Lufton
Greely
Johnstown
Windsor
7=, Contribution
Point
3
7
13
19
—
3
10
- -
2
--
2
3
2
4
9
4
4
4
5
--
--
12
11
5
5
3
-. m.
2
2
3
2
2
2
2
Area
61
--
--
36
__
74
54
87
44
--
37
45
52
44
20
52
45
52
44
--
--
--
--
--
--
37
57
57
19
--
18
--
--
Fug.
36
93
87
45
100
23
36
13
54
100
61
52
41
52
71
44
51
44
51
100
100
Adj. AQa
63
43
44
57
36
57
48
75
75
36
83
93
102
93
76
105
94
105
95
32
86
I
88
89
95
95
60
100
41
41
78
98
80
98
98
49
38
26
66
56
34
68
68
83
73
82
73
72
aAdj. AQ is the fitted air quality adjusted for background contributions
in (ig/m3.
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Table 37. PERCENTAGE CONTRIBUTION OF PARTICULATE SOURCE SECTORS
FOR MAXIMUM CONTROL CASE FOR FUGITIVE DUST
1980
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Location
Westminster
Aurora
Brighton
Adams City
Cherry Creek Dam
Englewood
Littleton
Boulder
Longmont
Idaho Springs
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Sewer Plant
Sch. Admin. Bldg. (State)
Gates Building
Sch. Admin. Bldg. (EPA)
2105 Broadway
Castle Rock
Black Hawk
Rocky Flats
Golden
Lakewood
Edgewater
Arvada
La Porte
Fort Collins
Love land
Greely
Ft. Lufton
Greely
Johns town
Windsor
% Contribution
Point
3
8
16
20
—
3
10
__
2
--
1
3
2
3
9
4
3
4
5
--
--
13
12
5
4
3
-. _
2
2
4
18
2
2
2
Area
64
--
--
38
Fug.
33
92
84
42
i
_-
76
57
88
48
--
38
46
52
39
20
52
46
52
45
--
--
--
--
--
51
37
__
60
60
22
--
21
--
--
100
21
33
12
50
100
61
51
46
58
71
44
51
44
50
100
100
87
88
95
45
61
100
38
38
74
82
77
98
98
Adj. AQ3
67
43
45
59
36
61
49
80
79
38
90
100
109
109
81
114
101
114
103
33
87
51
38
49
70
60
34
75
75
85
81
85
73
72
aAdj. AQ-is the fitted air quality adjusted for background contributions
in ug/m .
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Table 38. PERCENTAGE CONTRIBUTION OF PARTICULATE SOURCE SECTORS
FOR MAXIMUM CONTROL CASE FOR FUGITIVE DUST
1985
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Location
Westminster
Aurora
Brighton
Adams City
Cherry Creek Dam
Englewood
Littleton
Boulder
Longmont
Idaho Springs
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Sewer Plant
Sch. Admin. Bldg. (State)
Gates Building
Sch. Admin. Bldg. (EPA)
2105 Broadway
Castle Rock
Black Hawk
Rocky Flats
Golden
Lakewood
Edgewater
Arvada
La Porte
Fort Collins
Loveland
Greely
Ft. Lufton
Greely
Johnstown
Windsor
% Contribution
Point
3
9
18
21
__
4
12
__
2
--
2
3
2
3
9
4
4
4
5
--
--
17
16
6
4
3
_ —
3
3
5
3
2
3
4
Area
68
--
--
40
_ _
79
60
90
51
--
39
46
52
44
21
53
46
53
45
--
--
_-
--
--
51
38
_ •»
65
65
25
--
24
--
--
Fug.
29
91
82
39
100
17
28
10
47
• 100
59
51
46
53
70
43
50
43
50
100
100
83
84
94
45
59
100
32
32
70
97
74
97
96
Adj. AQa
70
43
45
61
36
64
51
86
82
38
96
107
115
105
86
122
108
122
109
34
87
49
38
51
73
64
34
82
82
89
73
88
74
73
Adj. AQ is the fitted air quality adjusted for background contributions
in [ig/m .
195
-------
bituminous coal; of this, 96 percent of the emissions were ascribed
to industrial area sources. Unfortunately, uncertainties inherent in
the determination of the emission levels of the area sources in this
Denver County NEDS summary as well as the delineation of area versus
point sources preclude the formulation of any control measures based
upon this information. As this data tends to indicate the potential
for significant reductions in total suspended particulate concentra-
tions, given the control of bituminous coal-dependent sources, this
situation should receive additional attention. Prior to this, however,
existing data uncertainties must be resolved.
The removal of lead from gasoline has been shown to reduce particulate
emissions from the exhaust by 40 to 60 percent. An average reduction
of 50 percent would bring about only a 31 percent reduction in the total
particulates due to motor vehicles after consideration of tire wear.
This could result in another 4 percent reduction due to area sources,
or about 2 percent total reduction. However, as more cars become
equipped with catalytic mufflers, the impact of such a measure would
decrease over time.
Increased effort is still needed in this area to determine whether par-
ticulate levels in Denver County can feasibly be expected to attain
Federal air quality standards. The solution may lie in a more detailed
inventory of fugitive dust and other particulate sources.
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SECTION VI
THE PLAN FOR THE MAINTENANCE OF AIR QUALITY
INTRODUCTION
This section presents a strategy for maintaining air quality once it has
been attained (in part, with the methods proposed in Section V). The
maintenance strategy is based upon a land use and transportation plan
already developed for the Denver metropolitan area and used for the air
quality projections in this report. The proposed strategy would incor-
porate the regional plan into a regulatory framework, whereas at present
only portions of the plan can be enforced.
The projections of air quality to 1985, presented in Section IV, demon-
strate that, under current control requirements, the concentration of
total suspended particulates is expected to increase around 20 percent
during the time period 1975 to 1985. Hydrocarbons, carbon monoxide and
nitrogen oxide concentrations are decreasing during these years as a
direct result of the Federal Motor Vehicle Control Program.
The air quality analysis for this report is based, to a large extent,
upon the Joint Regional Planning Program (JRPP) for the Denver-Boulder-
Longmont metropolitan complex. The JRPP plan was developed jointly by
the Denver Regional Council of Governments (DRCOG), the Regional Trans-
portation District (RTD), and the Colorado Division of Highways, and
provides for orderly, controlled growth of the region to the year 2000.
The JRPP plan assumes the population growth of the area will be at a
lower rate than has prevailed recently, and that economic activity can
be encouraged to develop in concentrated centers and corridors which will
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be complementary to public transportation service. The alternative to
such a plan is continued sprawl and perhaps more total activity in the
Denver area than could be tolerated from the standpoint of air quality.
Based on the information in Section IV, it appears that hydrocarbon and
carbon monoxide air quality will be acceptable throughout the maintenance
period once the standards are initially met. In the long run, air qua-
lity will deteriorate again, unless policies such as that of the JRPP
are instituted. Such regional planning is not now essential for the non-
metropolitan regions in the AQMSA (at least, not for air quality pur-
poses), but in the future these areas (Larimer, Weld, Gilpin, Clear
Creek, and rural portions of the JRPP countries) also will need develop-
ment planning to prevent degradation of their air quality as a result
of continued growth.
The underlying concept of the Air Quality Maintenance Plan (AQMP) is to
institutionalize the JRPP plan. In this way, both the growth rate and
the distribution of growth which were used in projecting air quality are
assured. That is, with the JRPP plan in the SIP the JRPP plan will
necessarily be enforced along with the rest of the SIP.
It should be noted that this section does not address the maintenance of
the particulate standards. The analysis in Section V indicated that
with reasonably available control technology for point and fugitive dust
sources, it was not possible to attain even the primary standard in
Denver County. As lack of sufficient supporting data does not allow for
the implementation of any additional attainment measures and the current
and suggested controls are considered the maximum feasible, it is not
reasonable to formulate the maintenance of a standard which cannot be
achieved. At the most, the AQMP may be expected to slow down the rate
of increase of fugitive particulate emissions.
The next part is an overview of the maintenance plan, including the mea-
sures and tools for implementation. This is followed by a basically
198
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qualitative analysis of the air quality impact of the proposed plan. The
actual maintenance measures are then presented in more detail by providing
a description of each measure, its legal foundation, and the roles of the
agencies assigned to its implementation. The implementation tools are
presented next; the legal foundation of each as well as its relation to
maintenance implementation is described. The final part of this section
deals with the social and economic impacts associated with the maintenance
plan implementation.
MAINTENANCE PLAN DESCRIPTION
The specific measures of the maintenance plan are the following.
1. Construction of a rapid transit system.
2. Creation of activity centers throughout the RTD area.
3. Construction of the JRPP highway system.
As a means of fostering the implementation of the above measures, two
specific tools are to be utilized. These implementation tools are:
1. Air contaminant emission permits.
2. Land use development permits.
The major pieces of legislation relied upon for this maintenance strategy
package are the 1970 Colorado Air Pollution Control Act and the Colorado
Land Use Act as amended. These two acts provide a good legal foundation
on which to build a viable maintenance mechanism. As specified in more
detail in the text, it is recommended that the following specific actions
be taken:
1. The State Air Pollution Control Commission will promulgate
a regulation incorporating the Regional Transportation
District (RTD) transit system into the official state im-
plementation plan. This regulation will include the fol-
lowing elements.
a. An endorsement of the RTD plan by the Commission.
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b. The right of review by the Commission of any changes
in the RTD plan which may significantly affect the
expected impact of the system.
c. The stipulation that no air quality permit be issued
for air pollution sources which might interfere with
the construction or operation of the RTD system, the
approved highway plan, or land use plans.
d. The requirement that RTD submit within a specified
period a plan for reducing the air pollution impact
of any system change.
2. The Commission will promulgate a regulation requiring
DRCOG to submit an annual report on the progress of the
entire JRPP plan.
3. The Commission will promulgate a regulation which requires
no new highway construction unless such construction is
consistent with the approved highway construction plan.
Exceptions will be permitted only if a review shows that
the air quality impact is not adverse but is beneficial
and consistent with the overall land use plan.
4. An amendment will be enacted to the Coloraio Air Pollu-
tion Control Act to provide the power needed for absolute
review authority for all new sources and indirect sources.
The indirect source review authority may be delegated to
regional authorities or local authorities with final
review by the Air Pollution Control Commission.
Regulations to be promulgated under this amendment include;
a. The stipulation that the review criteria for indirect
sources include compliance with the JRPP plan.
b. The coordination of indirect source review with the
development controls specified in House Bill 1041,
which amends the Land Use Act.
Intergovernmental cooperation is essential for the success of this plan.
The agency assigned overall responsibility for the implementation and
operation of the maintenance plan is the Air Pollution Control Commission.
Enforcement of the plan is to be the responsibility of the Division of
Air Pollution Control. In addition, it is necessary to provide for
formal information links between the APCC and the Land Use Commission in
order to coordinate indirect source review with the land development
permit system. This will be accomplished through periodic meetings
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attended by representatives of both bodies and joint public hearings
or permit requests. (An alternative not recommended here but perhaps
worthy of consideration would be to make the APCC a formal member of
the JRPP, thus facilitating the coordination which is needed.)
Costs of this maintenance strategy package include any additional man-
power and monitoring equipment costs. It is felt that the nature of the
maintenance plan is such that no significant additional burden is placed
upon any of the involved agencies. Thus, a minimal cost is assigned to
the air quality maintenance plan.
EXPECTED AIR QUALITY IMPACT OF STRATEGY
As noted earlier, the air quality analysis for this report was based upon
data from the approved JRPP plans. It is of particular importance that
the travel information used for projecting CO and HC emissions are based
upon the JRPP reports and analysis; greater travel activity would entail
increased emissions.
Table 40 lists a number of parameters for two cases, the JRPP approved
plan and an alternative based upon continuing present trends ("sprawl").
As the table shows, the JRPP plan would not necessarily entail less total
socioeconomic activity in the area as a whole (see below) but would
concentrate it more (CBD employment would be greater) and would provide
much more transit service. At the end of the forecasting period for this
report, 1985, the JRPP plan would involve an estimated 1.5 million vehi-
cle-miles of travel per day less than would the alternative, a difference
of nearly 6 percent. The difference would actually be greater than that
in 1985 because the proposed rapid transit system would be just going
into full operation. The system is included in the year 2000 total
travel figures, but transit ridership would not be expected to increase
to the values estimated by linear interpolation. The effective benefit
of the strategy will be greater in certain areas. Because of the high
reliance on transit, peak concentrations of traffic and of pollutants
201
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will be greatly reduced. No data is available for quantitative estimates
of this effect. The comparison in Table 40 is based upon two cases with
the same total population but different distributions of population and
different transportation systems. Without the controls proposed here,
the total socioeconomic activity and associated travel volumes could be
substantially greater than assumed in Table 40. Consider the following:
The Denver Metropolitan Area, since the 1970 Census,
has been growing at an unprecedented rate. The over-
all increase in the 1960's was at a rate of slightly
less than 3.0 percent on an average yearly basis, while
in the three subsequent years, the annual growth rate
has been estimated at 3.3 percent in 1970, 4.4 percent
in 1971 and 5.3 percent during 1972 . . .
. . .Long-term forecasts show the potential of a
tripling in size of the metropolitan area in less
than thirty years . . . Without stretching the imag-
ination, a 'reasonable1 forecast of population can
range anywhere between 2.2 and 3.9 million people
for the Denver Metropolitan Area by the year 2000.
The Joint Regional Planning Program has adopted a
conservative estimate of about 2,350,000 people as
a desirable level for the year 2000 . . . 1
If population were to grow to 3.9 million in 2000 instead of to 2.35
million, as assumed in the JRPP plan, and if travel should increase pro-
portionally, automotive emissions would be 66 percent greater than would
be forecasted using the JRPP projected population, resulting in poorer
air quality.
MAINTENANCE MEASURES
Construction of a Rapid Transit System
The Regional Transportation District (RTD) is a transportation authority
for the Denver metropolitan area created by Chapter 89, Article 20 of
the Colorado Revised Statutes. RTD began to plan a mass transportation
system in 1970. At the present time the RTD consists of Boulder,
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Jefferson, and Douglas Counties, the City and County of Denver, and the
western portions of Adams and Arapahoe Counties. The public transporta-
tion plan developed by RTD is shown in Figure 41. It consists of 100
miles of two-way guideways with 58 stations interconnected by automat-
ically controlled, demand-activated, 12-passenger vehicles.
In September, 1973 the voters in the Regional Transportation District ap-
proved a bond issue as part of the financing for the public transporta-
tion system. In March 1974 RTD selected a systems engineering team to
develop detailed plans for the system. Alternatives, exact routes,
environmental impacts, and detailed design are all still under study.
It is expected that construction of the Personal Rapid Transit (PRT)
system will take 10 years, so that the complete system will not be
available until 1983 or 1984, near the end of the period with which
this maintenance plan is concerned. In the meantime, however,extensive
bus service increases are also planned and sections of the rapid transit
system will be utilized as they are completed. The first phase of the
bus service increase, the Early Action Program, will involve acquisi-
tion of six existing bus companies and increasing the amount of bus
2
service by 61 percent by 1975.
No additional legislation is necessary in order to carry out the RTD
program for a rapid transit system and increased bus service. RTD has
adequate taxation powers and bonding authority to construct the system
and operate it. What is needed is for the RTD plan to become part of
the official State Implementation Plan (SIP). The Colorado Air Pollution
Control Commission appears to have adequate authority under the Colorado
enabling legislation for state air pollution control (Chapter 66, Article
31) to allow the Commission to adopt the RTD plan (and other elements of
the Joint Regional Planning Program) as an official part of the SIP. If
this proves not to be the case the necessary legislation should be
enacted. It is recommended that the Commission adopt regulations incor-
porating the RTD rapid transit system into the official SIP. The Early
204
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PROPOSED REGIONAL
TRANSIT SYSTEM 1983
Personal Rapid Transit Network
Regional Bus Service
Local Bus Service
Park-and-Ride Facility A
Figure 41. Joint Regional Planning Program transit system
205
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Action bus portion of the RTD system is in the Colorado Transportation
Control Plan. The regulations will include the following elements:
An endorsement by the Commission of the RTD rapid transit
plan as an element of a coordinated community development
plan consistent with air quality goals.
A requirement that RTD submit for the Commission's review
any change in the plan which would significantly affect
the expected impact of the system on the amount or location
of automobile travel, or significantly affect air quality
in the metropolitan area.
A requirement that no permit be issued for air pollution
sources which would be located in a manner which could
interfere with construction or operation of the RTD sys-
tem, or would interfere with the associated approved
highway or land use plans.
A requirement that RTD develop, within a specified period,
a recommendation for reducing the air pollution impact of
any system change (from 2 or 3 above) which had been deter-
mined by RTD or the Commission to affect air quality
maintenance.
A related regulation will require the Joint Regional
Planning Program (RTD, DRCOG, and the Colorado Division
of Highways) to report annually to the Commission on the
progress of the entire JRPP planning process. Each annual
report should identify the estimated impact on air quality
of each project completed during the past year and the
expected effect of all major plans or plan changes adopted
during the past year. (This could also be accomplished by
requiring APCC approval of certain key reports issued as
part of the regional transportation planning process,
such as the annual Work Program and Unified Regional Trans-
portation Work Program, the Annual Report, or the Operations
Plan. This also could be combined with the review required
by 23 U.S.C. 109 (j) and described below.)
The recommended regulations will provide a legally enforceable basis for
using the RTD plan in the SIP and will provide a framework for incorpo-
rating air quality considerations in the detailed planning process and
in subsequent changes. Furthermore it will provide an important tool
for new source review. One of the criteria in 40 CFR 51.18 for review
of new sources is whether the source would violate an adopted control
strategy in the SIP; a new source could not be approved under the
206
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proposed regulations if it would be inconsistent with the JRPP plans for
the transit system (or associated highways and land use). Also, the
regulations provide for monitoring the long process of implementing the
plans. These regulations will be enacted within one year, as part of
preparation of the maintenance plan required by June 1975.
Implicit in the use of the JRPP plan as a maintenance strategy is the
need for coordination between the agencies responsible for the JRPP
plan (the Colorado Division of Highways, the Denver Regional Council of
Governments and the Regional Transportation District, and the local
government members of RTD and DRCOG) and the Colorado Air Pollution
Control Commission and Division. DRCOG and RTD will develop explicit
methods for incorporation of air quality considerations into their plan-
ning process, in a quantitative way. This is to be done internally
or arrangements will be made for technical assistance from the Air
Pollution Control Division or from DRCOG.
To a large extent, existing Federal regulations applicable to planning
and construction of transportation systems already require extensive
community and agency cooperation and involvement, and require analysis
of air quality (as well as other environmental effects), so existing
intergovernmental frameworks and processes should suffice.
The procedures for that planning, and how they can be related to air
quality maintenance plans, have been discussed at length in recent
345
reports. ' ' The requirements for interagency cooperation in trans-
portation planning are briefly summarized as follows.
1. Federal law (23 U.S.C. 134) requires state governors to
designate areawide transportation planning agencies for
all urban areas with 50,000 people or more, which in
turn are required to conduct the "continuing, comprehen-
sive, cooperative" (3-C) planning process for multi-modal
transportation systems. Regulations specify that this
planning must include a formal procedure for responding
to the needs and desires of local governments, including
public hearings. Numerous specific reports (some referred
to above) are required to be issued.
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2. The Urban Mass Transportation Assistance Act of 1970 (and
other legislation) requires that all applications for
Federal funds for planning or construction of transporta-
tion facilities be submitted to the areawide planning
agency designated as responsible for metropolitan and
regional planning (the so-called A-95 review process).
3. The National Environmental Policy Act requires prepara-
tion of environmental impact statements for all major
federal actions significantly affecting the environment
(such as grants for transportation facilities). Guide-
lines for preparing such statements require extensive
opportunities for public and government involvement and
comment.
4. Federal law (23 U.S.C. 109 (j)) and related regulations
require that each 3-C planning agency annually review
the transportation plan to insure it is consistent with
the SIP.
In the Denver area, the designated areawide 3-C planning agency is the
Joint Regional Planning Program, jointly operated by the Division of
Highways, the Denver Regional Council of Governments and the Regional
Transportation District. DRCOG is also the designated agency for A-95
review and for coordinating the review of environmental impact state-
ments. Since RTD and DRCOG are statutorily composed of representatives
from the county governments in their respective planning areas, inter-
governmental cooperation mechanisms are inherent. These relationships
could be modified by formally establishing criteria for incorporating
air quality considerations in planning, such as through additional
APCC regulations.
Creation of Activity Centers
A major feature of the JRPP land use plan is development of 13 activity
centers. These centers are described as aggregations of urban activity
large enough to be primary generators of large internal activity. They
are expected to be terminal locations for the rapid transit system.
Their creation will serve a twofold purpose. First, it will tend to
lessen the air pollution now centered around Denver by redirecting some
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of the future growth. Secondly, to the extent that large numbers of
individuals are expected to live, work, and shop in the activity centers,
VMT will be reduced.
The activity centers recommended by the JRPP are listed below.
Boulder
Northglenn
Arvada
Federal Center
Villa
Alameda
Denver CBD
Medical Center
Cherry Creek
South Colorado
Englewood
Technological Center
Littleton
University of Colorado/Crossroads Shopping Area/
CBD
Northglenn Shopping Area/Western Electric Front
Range Denver Area
Old CBD/Tri-Center Area
Federal Center/Community College/Westland Areas
Villa Italia Shopping Center
Alameda/I-225 Area
CBD/Auraria/Skyline Area
University of Colorado Medical Center/Colorado-
Colfax Area
Cherry Creek Shopping and Residential Area
Colorado Boulevard/I-25 Area/University of Denver/
University Hills
Englewood CBD/Cinderella City Shopping Center
Area of Denver Technological Center/Greenwood
Plaza
Littleton CBD Area
No additional legislation is needed to create activity centers. Instead,
their evolution is dependent upon the construction of the rapid transit
system as well as the JRPP highway plan. Air contaminant emission per-
mit review will also serve as a prime tool in activity center creation.
Construction of the JRPP Highway System
The Joint Regional Planning Program (JRPP) for the Denver metropolitan
area includes an approved highway plan intended to coordinate with and
complement the RTD public transportation plan. This plan is shown in
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Figure 42. The limited access and principal arterial portions of this
plan have been approved, and work in underway to develop a construction
program. This plan was the basis for the travel estimates used in this
study for computing future air quality.
No new legislation is required for completion of the highway program,
except for construction appropriations. Regulations will be adopted by
the Air Pollution Control Commission to require that no highways be
built unless they are consistent with this approved plan, exceptions
being permitted after a specific review for the air quality impact of
the change. (Present practice is for highway construction to be re-
viewed by the Air Pollution Control Division for its effect.) The intent
of this regulation is not to encourage highway construction but rather
to insure that no major highway links beyond the JRPP plan are built
without review for air quality. This regulation will complement indirect
source review in that it will apply to any link on the JRPP plan even
if such a link does not require indirect source analysis (only major
highways are subject to indirect source review under EPA regulations).
(DRCOG is at present planning to conduct an analysis of the air quality
impact of the JRPP system.)
In this connection it should be noted that the air quality analysis per-
formed for this report is a macroscale analysis and not sufficiently
detailed to demonstrate whether particular highway links would or would
not satisfy the requirements for such indirect sources. It is recom-
mended that a detailed areawide highway system review be undertaken
separately, before the Commission endorses the JRPP plan. (The DRCOG
review may suffice for this purpose.) Both this review and the proposed
regulations will be completed by June, 1975.
As with the RTD system, this measure will involve cooperative arrange-
ments among the JRPP members and the Air Pollution Control agencies.
EPA will be more involved in this case, because of the explicit re-
quirement in both EPA and Federal Highway Administration regulations for
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JOINT REGIONAL PLANNING PROGRAM
HIGHWAY PLAN
LIMITED ACCESS FACILITY
PRINCIPAL ARTERIAL
Figure 42. Joint Regional Planning Program highway plan
211
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review of the air quality impact of highways. To a large extent the
cooperative efforts for highway planning are already institutionalized
and involve the very agencies proposed here to be involved.
As with other types of transportation facilities, procedures for planning
highways and their relationship to air quality maintenance planning
n I f-
have been described in recent reports. ' ' These processes can be sum-
marized as follows.
1. Federal-aid highways must be planned as part of the multi-
modal 3-C process, described earlier for other transporta-
tion systems, and are subject to the environmental impact
and A-95 review processes.
2. State highway agencies must prepare "Action Plans" to
"assure that adequate consideration is given to possible
social, economic, and environmental effects of proposed
highway projects ..." These Action Plans must provide
for "involvement of other Federal, state, and local
agencies . . . and interested groups ..." in both
Action Plan preparation and highway planning.6 Colorado
has completed such an Action Plan.
3. Federal regulations (23 CFR 770) require that highway
agencies coordinate with the 3-C agencies and air pollu-
tion control agencies to establish a process for con-
tinuing review of the consistency of the transporta-
tion plan and the state implementation plan for air
quality.
Thus, these requirements already involve DRCOG, the Division of Highways,
local governments, and the Federal agencies in an established framework
for intergovernmental cooperation in highway planning. Little new ef-
fort is expected to be necessary for this measure.
IMPLEMENTATION TOOLS
The two primary tools for ensuring the implementation of the maintenance
measures are the air contaminant emission permit and the land development
permit systems. These two items are discussed below.
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Air Contaminant Emission Permit
EPA regulations (40 CFR 51.18) require that each state shall have legally
enforceable procedures to determine whether the construction or modifica-
tion of a facility will interfere with the attainment or maintenance of a
national standard either directly because of emissions from it, or in-
directly, due to emissions resulting from mobile source activities
associated with it. Such procedures must include means by which an
application for approval to construct or modify will be denied if it
would result in the interference with the attainment or maintenance of
the standard.
The Colorado Air Pollution Control Act of 1970, as amended, prohibits the
construction or operation of new direct or indirect sources of air pol-
lution without first filing an "air contaminant emission notice" and then
obtaining a valid permit therefor from the Air Pollution Control Com-
mission. However, no permit is required for new indirect sources until
regulations regarding the permits for such sources are promulgated by
the Commission; to date, no such regulations have been promulgated. The
permits are to be denied if the applicable emission standards are not
met or if it is determined to interfere with the attainment or main-
tenance of the federal ambient air standards unless the proposed project
or activity utilizes the best practical (reasonably available control)
technology. The law (66-31-15) also provides a variance process which
allows variances to be granted if compliance with emission control
regulations would create an "unreasonable economic burden." Note, how-
ever, that under either EPA or Colorado regulations only sources over a
certain size require permits.
This appears not to provide the authority required by 40 CFR 51.11 be-
cause permits can be granted through the Colorado variance procedure
even if the requirements of Federal regulations are not met. At pre-
sent Colorado has not promulgated regulations specifically for indirect
source review. In the absence of Colorado regulations, EPA regulations
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published in the Federal Register on 25 February 1974 and amended on
9 July 1974 make review of new or modified indirect sources in Colorado
(and other states) subject to EPA control under 40 CFR 52.22 (see Sec-
tion II). The Colorado Air Pollution Control Commission did, on April
26, 1973, adopt a policy related to indirect sources. In that policy
statement the Commission requested "that the Colorado Legislature
recognize the importance of and pass legislation mandating the joint
use of Land Use and Transportation planning as necessary tools for the
attainment and maintenance of publicly acceptable levels of air quality
by granting sufficient powers to appropriate agencies for this purpose."
A policy will be formulated and adopted which incorporates the JRPP land
use and transportation plans in the air contaminant emission permit re-
view process. The approved JRPP plan will be a criterion for judging
whether new sources are appropriate. This will complement the other
recommended measures involving the JRPP plan in maintenance of air qual-
ity, and provide a regulatory tool for fostering orderly development in
accordance with the JRPP plan. In essence, new sources could not be
built if they were not consistent with the JRPP plan, as for example
in the case where the new shopping center would violate the growth center
concept.
Several legal actions are required to implement this recommendation.
First, the Colorado legislature needs to enact a change in the Air Pol-
lution Control Act to provide the absolute authority required by Federal
regulations. Also, the law should provide for delegation of the indirect
source review authority to regional or local authorities. Next, the
Commission should enact the detailed regulations necessary to control
new sources. These regulations will include the following elements:
1. Establish or reiterate (as necessary) that the criteria
for review of air contaminant emission permit requests
in the JRPP area include the question of compliance with
the JRPP plan.
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2. Provide for coordination of indirect source review with
the provisions under Colorado House Bill 1041 for control
of development around key facilities such as highways.
All these regulations and legislative actions should be completed by
June 1975.
The JRPP planning process is already founded on a well-established co-
operative basis. This proposal will add to the use of the established
coordination functions and strengthen DRCOG's role in ensuring the co-
ordinated, orderly development of the Denver metropolitan area. Added
cooperation will be required between DRCOG and the Colorado Air Pollu-
tion Control agencies, as is required for the other measures involving
the JRPP plan.
Land Development Permits
House Bill 1041 amended the state Land Use Act by providing for the
identification, designation, and administration of areas and activities
of state interest. While it is primarily a local government responsi-
bility to designate and administer areas of state interest, the Colorado
Land Use Commission is given the authority to review such designations
and administration guidelines. Furthermore, the Land Use Commission
may submit a formal request to a local government to take action with
regard to a specific matter which the Commission considers to be of
state interest.
Among the enumerated state area interests are interchanges involving
arterial highways as well as rapid or mass transit terminals, stations,
and fixed guideways. Thus, the JRPP plan and hence the maintenance
plan includes areas of state interest. As such, development permits
will be required in these areas before such development can take place.
To this extent, H.B. 1041 can serve to control growth in accordance
with the JRPP plan. These development permits are needed to supplement
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air contaminant emission permits in part because small sources (such as
minor indirect sources) require no emission permits.
SOCIAL AND ECONOMIC IMPACTS
As has been mentioned, the components of the JRPP plan which were selected
as maintenance measures include the transit plan, the highway plan,
and the concept of activity centers. Since the transit plan is by far
the most significant of these in terms of impact, the following dis-
cussion will focus on it, with analysis of the highway and activity
centers relegated to secondary consideration.
The discussion is organized as follows. First the impacts on the social
system are analyzed. These impacts include not only objective considera-
tions, but certain subjective considerations as well. Economic impacts
are discussed next. The effects of the system on employment, income,
and business establishments are included under this category as are the
effect on the system on the state budget and on energy consumption. This
discussion is by no means meant to be a detailed analysis of the pro-
posed transportation plan. Instead, it is only meant to display the
possible areas of resistance to the JRPP plan implementation.
There are two major social impact areas. On the positive side is the in-
creased mobility which such a transportation system would bring about.
The main negative area of impact is the removal of houses and relocation
of the residents caused by guideway and station construction.
Mobility is perhaps the most obvious social area affected by a transpor-
tation system. Preliminary studies conducted for the RTD have indicated
a widespread increase in mobility for the population as a whole. For
upper and middle income families, the increased mobility is in the form
of having an alternative to the automobile. Low income families, which
comprise the bulk of transit-dependent individuals along with the phys-
ically handicapped and school-age youth, stand to benefit the most from
216
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a mass transit system. While there do exist certain gaps in service to
some transit-dependent areas, the group as a whole should be well served.
For example, the elderly and physically handicapped will have much bet-
ter access to hospitals and clinics once the complete system has been
constructed. One drawback does exist, however. As planned, several
transit-dependent areas have to rely on feeder bus service to the rapid
transit station. This involves both a time and pecuniary penalty to
these individuals. This penalty is offset to some extent by increased
job mobility, which is discussed later.
Relocation of individuals occurs when rapid transit corridors go through
residential areas. In general, the approved rapid transit routes do not
bisect any identifiable neighborhood units. There are some areas, how-
ever, where displacement of existing housing occurs. This must be con-
sidered a negative impact.
A final social impact is subjective in nature and has to do with the
reaction of residents of affected neighborhoods to a rapid transit sys-
tem and the proposed highway system. In general there is some reaction
by certain neighborhoods to either additional highways or a rapid transit
network going through their area. Obviously not all neighborhoods can
be satisfied but the plan appears to be flexible enough to mitigate at
least a portion of these negative feelings through public participation
meetings.
The economic impacts of the JRPP plan are impacts on employment, income,
and business establishments. Employment in the area is affected in two
ways. First, the construction and later the operation of a rapid transit
system will create additional employment opportunities. One study esti-
mated that 8,000-10,000 jobs would be provided in the construction in-
dustry over the 25-year construction period. Secondly, to the extent
the transit plan increases accessibility, labor force mobility will be
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increased. This in particular may prove to be a major benefit to low-
income groups since their geographic range of employment opportunities
will be increased.
Table 40 gives the three annual budgets for "typical" four person fami-
lies. The impact on household income arises from two areas. The first
area has to do with the method of financing. The method adopted by the
Colorado legislature revolves around a 0.5 precent sales tax. As shown
by the table below3 at best this is a proportional tax, and to a small
extent is income regressive in nature. The point is that as a percentage
of total income, lower income groups will be contributing as much to
the transportation financing as the intermediate and upper income groups.
This is compounded by the fact that in several low income areas there
is to be no rapid transit service, but instead feeder bus service.
IMPACT OF TRANSPORTATION PLAN SALES TAX
Taxable
income3
$4,582
6,563
9,127
0.5%
sales tax
$22.91
32.82
45.64
Rebateb
$1.17
1.17
1.17
Net tax
$21.74
31.65
44.47
Net tax.
income
0.27%
0.26%
0.26%
Four-family Annual
budget level income
Lower $ 7,976
Intermediate 12,107
Higher 17,422
o
Taxable income is composed of 100 percent of food, clothing, personal
care, and other family consumption as well as 40 percent of transpor-
tation and housing expenditures.
Present rebate is $7 for the 30 percent tax, therefore, the RTD rebate
would be 0.5
3.0
£ x $7 = $1.17.
A second impact of the transportation system on household income has to
do with transportation costs themselves. Transportation cost reductions
are expected to be greatest for lower income families who work in the
industrial and commercial areas served by the rapid transit/bus system.
218
-------
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The actual impact will be dependent upon the finalized rate structure
(projected to be an average of $0.35 per trip) as well as the final
route alignment.
The third economic impact area has to do with the effect of the trans-
portation system on the commercial business establishment. Surveys
conducted by the RTD have shown that only one-half of the respondents
felt that the rapid transit system would affect them. However, the
overall effect of the mass transit/bus system will be to concentrate
shopping activities in areas reserved for the rapid transit system.
This may force some business establishments to relocate to these re-
served areas or suffer possible loss in revenues.
In conclusion, the overall socioeconomic impact of the RTD transporta-
tion plan appears to be generally favorable.
220
-------
REFERENCES
1. Joint Regional Planning Program, Regional Development Policy. A
Growth Policy Strategy for the Regional Study Area. Technical
Memorandum 1-1/001, December 1973.
2. Regional Transportation District. Early Action Program. (Undated.)
3. Alan M. Voorhees and Associates, Inc. Guidelines for the Review of
Urban Transportation Plans and Programs Pursuant to 23 CFR 770.204.
Environmental Protection Agency, Office of Air Quality Planning and
Standards, Research Triangle Park, North Carolina, Draft, April 26,
1974.
4. U.S. Environmental Protection Agency, Office of Air and Waste
Management, Office of Air Quality Planning and Standards. Guidelines
for Air Quality Maintenance Planning and Analysis. .Vol. 4: Land
Use and Transportation Considerations. Research Triangle Park, North
Carolina, June 1974.
5. U.S. Environmental Protection Agency, Office of Air and Waste
Management, Office of Air Quality Planning and Standards. Guidelines
for Air Quality Maintenance Planning and Analysis. Vol. 2: Plan
Preparation. Research Triangle Park, North Carolina, June 1974.
221
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APPENDIX A
ECONOMIC DATA FOR THE DENVER AQMSA BY COUNTY
This appendix contains general economic data for the Denver Air Quality
Maintenance Study Area, compiled by county. This data was originally
presented in "Policy Analysis for Rural Development and Growth Management
in Colorado", a report prepared for the Colorado Rural Development Com-
mission by the Denver Research Institute, University of Denver.
EXPLANATION OF COUNTY DATA SHEETS
1. The 1970 population per the U.S. Census of Population.
la. The percent change in population 1950-1960 and 1960-1970.
2. Relative income, or this county's median family income as a percent
of median family income for Colorado, per Census of Population.
3. The percent of families with income below the poverty level per the
1970 Census of Population.
4. Labor participation rate, or percent of population employed, per
Census of population.
5. Total employment of residents of the county per Census of Population.
6. Unemployment as a percent of total civilian labor force per Census of
Population.
7. Per capita tax income to the State of Colorado is represented by the
county sum of state income tax liability plus state sales tax collec-
tions divided by the population.
8. Per capita welfare costs to the state are the state's contribution of
state funds (only) divided by population.
A-l
-------
9. Per capita education costs are total payments to school districts of
state funds divided by population.
10. This figure shows the surplus (S) or deficit (D) of state taxes
collected compared with education and welfare expenditures.
11. The percentage of employed residents of the county in each of 10
sectors of the economy. (The parenthetical numbers are absolute
numbers, in addition to the percentages.)
12. This is a subjective statement of the first order determinants of
change in population and economic activity. Agricultural employment
almost invariably shows substantial decreases over the 1950-1970
period because of greater economic efficiency in agricultural pro-
duction. This increased productivity was such that, given a constant
production level between 1950 and 1970:
employment in raising meat animals would have halved;
employment in raising feed grains would decrease to one fifth;
employment in raising hay would have halved;
employment in raising food grains would decrease to one third;
according to Changes in Farm Production and Efficiency, USDA.
In the same period, coal mining employment would similarly have
dropped to about a third of its original level, with constant output.
These increases in productivity have greatly affected employment and
population in Colorado farming, ranching and coal mining counties.
ADAMS COUNTY
County Seat: Brighton; population: 8,309
1. 1970 population: 185,789
la. Percent change 1960-1970: 54.4
Percent change 1950-1960: 199.0
2. Median income as percent of state average: 1970: 108.9
1960: 110.0
1950: 102.2
3. Percent families below poverty level: 18.1
4. Percent of population employed: 1970: 37.3
1960: 33.8
1950: 31.2
A-2
-------
5. Actual employment:
1970:
1960:
1950:
69,284
40,626
12,571
6. Percent of labor force unemployed:
7. Tax income to state: $101.15
8. Welfare costs to state: $9.03
9. Education costs to state: $71.19
10. Per capita surplus or deficit: $20.93 S
11. Percent employed by industry: 1970
1970: 4.0
1960: 3.5
1950: 3.9
agriculture
mining
construction
manufacturing
transportation
trade
services, including
lodging and finance
health services and
other professions
education
public administration
1960
2.4 4.3
0.6 0.6
7.5 9,5
18.9 (13138) 21.2
11.0 12.0
25.2 21.7
13.5 13.0
8.0 4.9
6.3 4.4
2.9 6.2
1950
20.5
0.2
10.5
15.0 (1886)
10.4
18.3
10.0
5.6
2.8
4.8
12. Agricultural employment declined somewhat, but manufacturing em-
ployees increased sevenfold and bedroom communities thrived as the
Denver metropolitan area grew.
ARAPAHOE COUNTY
County Seat: Littleton; population: 26,318
1. 1970 population: 162,142
la. Percent change 1960-1970: 42.9
Percent change 1950-1960: 117.6
2. Median income as percent of state average: 1970: 126.2
1960: 123.5
1950: 107.9
3. Percent families below poverty level: 4.6
A-3
-------
4. Percent of population employed: 1970: 39.2
1960: 35.4
1950: 35.0
5. Actual employment: 1970: 63,500
1960: 40,168
1950: 18,238
6. Percent of labor force unemployed: 1970: 2.8
1960: 3.5
1950: 3.2
7. Tax income to state: $151.74
8. Welfare costs to state: $5.35
9. Education costs to state: $73.95
10. Per capita surplus or deficit: $72.54 S
11. Percent employed by industry: 1970 1960 1950
agriculture 1.1 2.3 7.2
mining 1.6 1.1 0.3
construction 6.4 8.2 12.0
transportation 7.3 7.7 9.9
manufacturing 17.7 25.5 17.7
trade 23.5 19.2 21.9
services, including
lodging and finance 15.8 14.9 13.4
health services and
other professions 11.7 7.8 5.8
education 8.5 5.0 3.7
public administration 5.8 5.8 6.0
12. Typical of Denver metropolitan area growth. Manufacturing grew
steeply in the 1950's (Martin - Denver) and eased. Trades and
services have continually grown with suburbanization. Relative
income is high.
BOULDER COUNTY
County Seat: Boulder; population: 66,870
1. 1970 population: 131,889
la. Percent change 1960-1970: 77.6
Percent change 1950-1960: 53.7
A-4
-------
2. Median income as percent of state average:
1970: 117.2
1960: 105.8
1950: 94.2
3. Percent families below poverty level: 5.6
4. Percent of population employed: 1970: 39.8
1960: 36.9
1950: 33.5
5. Actual employment:
1970: 53,482
1960: 27,382
1950: 16,160
6. Percent of labor force unemployed:
1970: 4.4
1960: 3.1
1950: 6.7
7. Tax income to state: $126.59
8. Welfare costs to state: $7.63
9. Education costs to state: $48.72
10. Per capita surplus or deficit: $70.24 S
11. Percent employed by industry: 1970
agriculture
mining
construction
manufacturing
transportation
trade
services, including
lodging and finance
health services and
other professions
education
public administration
12.9
10.5
18.3
5.8
1960
15.7
7.9
14.8
6.6
1950
1.8
0.6
5.5
21.0
5.0
18.0
5.3
1.1
8.3
13.2
5.2
19.2
11.4
3.8
9.3
7.7
6.2
20.4
16.5
5.6
14.8
3.3
12. Manufacturing employees living in Boulder County increased ninefold,
1950-1970. Educational employment boomed as the University grew.
Boulder also became more of a bedroom community for the Denver metro
area. Relative income went up substantially.
A-5
-------
CLEAR CREEK COUNTY
County Seat: Georgetown: population: 542
1. 1970 population: 4,819
la. Percent change 1960-1970: 72.5
Percent change 1950-1960: -15.1
2. Median income as percent of state average: 1970: 101.4
1960: 88.5
1950: 95.3
3. Percent families below poverty level: 5.7
4. Percent of population employed: 1970: 42.2
1960: 39.0
1950: 32.6
5. Actual employment: 1970: 1,987
1960: 1,088
1950: 1,236
6. Percent of labor force unemployed: 1970: 4.1
1960: 4.5
1950: 4.2
7. Tax income to state: $109.77
8. Welfare costs to state: $13.00
9. Education costs to state: $30.28
10. Per capita surplus or deficit: $66.49 S
11. Percent employed by industry: 1970
agriculture
mining
construction
manufac tur ing
transportat ion
trade
services, including
lodging and finance
health services and
other professions
education
public administration
1960
17.3
5.0
5.8
7.3
20.0
2.7
6.3
5.4
1950
1.0
13.4
18.1
6.7
4.5
20.4
1.6
5.5
15.3
7.3
9.5
25.1
3.6
9.3
20.7
4.7
7.2
24.3
16.9
3.4
4.5
3.9
A-6
-------
12. Mining, construction and tourism all grew between 1960 and 1970 to
double the county's population. Natural resources and proximity to
Denver accounted for this growth.
DENVER COUNTY
County Seat: Denver
1. 1970 population: 514,678
la. Percent change 1960-1970: +4.2
Percent change 1950-1960: +18.8
2. Median income as percent of state average: 1970: 101.0
1960: 110.1
1950: 115.8
3. Percent families below poverty level: 9.4
4. Percent of population employed: 1970: 41.3
1960: 39.8
1950: 40.2
5. Actual employment: 1970: 212,695
1960: 196,383
1950: 167,218
6. Percent of labor force unemployed: 1970: 4.1
1960: 3.7
1950: 4.1
7. Tax income to state: $165.65
8. Welfare costs to state: $17.51
9. Education costs to state: $26.37
10. Per capita surplus or deficit: $121.77 S
11. Percent employed by industry: 1970 1960
agriculture
mining
construction
manufacturing
transportat ion
trade
services, including
lodging and finance
1950
0.7
1.0
5.1
14.9
7.9
23.0
0.8
0.8
5.3
18.0
8.3
21.7
0.9
0.3
7.0
16.7
11.7
25.3
18.0
16.8
17.5
A-7
-------
11. (continued) 1970 1960 1950
health services and
other professions 12.4 9.4 8.0
education 8.0 5.1 3.9
public administration 6.7 7.7 7.1
12. Growth has been physically constrained by contiguous incorporated
suburbs. There has been substantial white out-migration to suburbs,
and in-migration by blacks and browns. Relative income dropped,
1950-1970. However, Denver is the core of the fast growing Denver
Metropolitan Area, a beneficiary of the national trend toward
urbanization and of the area's attracting power for in-migration.
DOUGLAS COUNTY
County Seat: Castle Rock; population: 1,531
1. 1970 population: 8,407
la. Percent change 1960-1970: +74.6
Percent change 1950-1960: +37.3
2. Median income as percent of state average: 1970: 115.3
1960: 89.2
1950: 88.1
3. Percent families below poverty level: 8.2
4. Percent of population employed: 1970: 37.9
1960: 34.1
1950: 38.6
5. Actual employment: 1970: 3,207
1960: 1,643
1950: 1,352
6. Percent of labor force unemployed: 1970: 3.1
1960: 1.2
1950: 1.6
7. Tax income to state: $106.32
8. Welfare costs to state: $6.88
9. Education costs to state: $77.31
10. Per capita surplus or deficit: $22.13 S
A-8
-------
11. Percent employed by industry: 1970 1960 1950
agriculture 11.1 (360) 17.3 40.2 (540)
mining 1.3 0.5 0.7
construction 12.2 (394) 9.9 7.7 (104)
manufacturing 16.1 (519) 24.0 15.2
transportation 7.7 8.9 6.1
trade 15.0 14.1 10.1
services, including
lodging and finance 12.2 (360) 8.3 7.8
health services and
other professions 8.6 4.4 2.1
education 10.6 (343) 4.8 3.8 ( 51)
public administration 4.5 4.3 4.0
12. Agricultural employment has declined and manufacturing has increased
but the main change has been the new identity of Douglas County as a
residential community with relatively massive increases in residents
employed in construction, education, and real estate-financial em-
ployment. Relative income is up to a level typical of Denver's
suburban counties.
GILPIN COUNTY
County Seat: Central City; population: 228
1. 1970 population: 1,272
la. Percent change 1960-1970: +85.7
Percent change 1950-1960: -19.4
2. Median income as percent of state average: 1970: 76.6
1960:
1950:
3. Percent families below poverty level: 12.7
4. Percent of population employed: 1970: 32.4
1960: 39.0
1950: 36.7
5. Actual employment: 1970: 389
1960: 267
1950: 312
6. Percent of labor force unemployed: 1970: 5.1
1960: 2.6
1950: 10.3
A-9
-------
7. Tax income to state: $85.38
8. Welfare costs to state: $16.35
9. Education costs to state: $4.48
10. Per capita surplus or deficit: $64.55 S
11. Percent employed by industry: 1970 1960 1950
agriculture 0.0 4.1 6.4
mining 0.0 4.1 9.9
construction 19.5 10.1 20.8
manufacturing 10.7 4.8 4.5
transportation 6.4 10.8 11.2
trade 16.4 25.8 22.8
services, including
lodging and finance 27.7 10.4 6.1
health services and
other professions 6.1 0.0 1.6
education 1.2 11.6 6.1
public administration 11.6 12.3 7.7
12. Recreation-related service employment picked up in the 1960's.
JEFFERSON COUNTY
County Seat: Golden; population: 9,817
1. 1970 population: 233,031
la. Percent change 1960-1970: +82.7
Percent change 1950-1960: +129.0
2. Median income as percent of state average: 1970: 126.1
1960: 124.6
1950: 110.3
3. Percent families below poverty level: 4.1
4. Percent of population employed: 1970: 40.8
I960: 38.1
1950: 35.9
5. Actual employment: 1970: 95,000
1960: 48,527
1950: 19,971
A-10
-------
6. Percent of labor force unemployed: 1970: 2.9
1960: 2.7
1950: 2.6
7. Tax income to state: $140.37
8. Welfare costs to state: $3.85
9. Education costs to state: $59.38
10. Per capita surplus or deficit: $77.14 S
11. Percent employed by industry: 1970 1960 1950
agriculture 1.2 2.1 8.1
mining 1.7 1.1 0.7
construction 7.6 9.5 13.0
manufacturing 17.4 19.9 15.6
transportation 7.8 8.6 10.8
trade 22.9 20.9 21.2
services, including
lodging and finance 14.9 14.4 12.8
health services and
other professions 9.3 6.8 5.4
education 8.9 6.3 3.9
public administration 7.6 8.0 7.5
12. Denver Metro Area growth is typified here.
LARIMER COUNTY
County Seat: Fort Collins; population: 43,337
1. 1970 population: 89,900
la. Percent change 1960-1970: +68.5
Percent change 1950-1960: +22.5
2. Median income as percent of state average: 1970: 93.9
1960: 86.5
1950: 89.9
3. Percent families below poverty level: 9.4
4. Percent of population employed: 1970: 37.9
1960: 36.3
1950: 34.8
A-ll
-------
5. Actual employment: 1970: 34,094
1960: 19,319
1950: 15,171
6. Percent of labor force unemployed:
1970: 5.4
1960: 4.5
1950: 4.9
7. Tax income to state: $104.10
8. Welfare costs to state: $10.72
9. Education costs to state: $45.51
10. Per capita surplus or deficit: $47.87 S
11. Percent employed by industry: 1970 1960
agriculture
mining
construction
manufacturing
transportat ion
trade
services, including
lodging and finance 13.0 9.1
health services and
other professions 9.6 5.7
education 20.5 (6995) 14.0
public administration 4.1 4.5
1950
6.3 (2167)
0.3
7.1 (2450)
15.1 (5175)
4.4
19.0
11.2
0.6
8.9
13.0
6.2
18.9
18.6 (2765)
0.3
14.5 (2193)
dam bldg.
8.0 (1221)
5.2
18.7
14.4
4.0
10.0 (1521)
4.3
12. A prosperous agricultural economy (augmented in 1950 by Reclamation
construction) has grown rapidly, with fourfold increases in residents
supported by manufacturing and education.
WELD COUNTY
County Seat: Greeley, population: 38,902
1. 1970 population: 89,297
la. Percent change 1960-1970: +23.4
Percent change 1950-1960: +7.2
2. Median income as percent of state average: 1970: 87.5
1960: 81.7
1950: 87.8
3. Percent families below poverty level: 11.9
A-12
-------
4. Percent of population employed:
1970: 37.3
1960: 34.5
1950: 32.6
5. Actual employment:
1970: 33,341
1960: 24,929
1950: 22,035
6. Percent of labor force unemployed:
1970: 4.2
1960: 3.9
1950: 5.0
7. Tax income to state: $94.72
8. Welfare cost to state: $18.34
9. Education cost to state: $50.55
10. Per capita surplus or deficit: $25.83 S
11. Percent employed by industry: 1970 1960
agriculture
mining
construction
manufacturing
transportation
trade
services, including
lodging and finance 12.1
health services and
other professions 8.3
education 13.7 (4569)
public administration 3.2
14.8 (4958)
0.3 ( 113)
7.4
14.5 (4837)
5.2
20.0
25.8
0.6
7.7
10.0
6.4
17.6
11.6
5.8
8.9
3.4
1950
39.1 (8613)
1.1 ( 252)
6.6
5.9 (1300)
5.3
17.8
10.5
3.3
6.1 (1349)
2.8
12. Although agricultural employment (very diversified) halved 1950-1970,
both manufacturing and education employment more than tripled to
sustain substantial growth.
A-13
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APPENDIX B
COLORADO AIR POLLUTION CONTROL ACT - 1970
B-l
-------
CHAPTER 66
ARTICLE 31
AIR POLLUTION CONTROL
Page B-2
66-31-1.
66-31-2.
*/**66-31-3.
66-31-4.
66-31-5.
**66-31-6.
66-31-7.
66-31-8.
66-31-9.
66-31-10.
**66-31-ll.
**66-31-12.
**66-31-13.
66-31-14.
Short title. 66-31-15.
Legislative declaration. **66-31-16.
Definitions. 66-31-17.
Air pollution control 66-31-18.
commission created. 66-31-19.
Duties of air pollution 66-31-20.
control commission.
Commission—additional 66-31-21.
authority.
Commission to promulgate
ambient air quality
standards. 66-31-22.
Commission to promulgate
emission control regu- 66-31-23.
lations. 66-31-24.
Commission—procedures to
be followed in setting
standards and regula-
tions. 66-31-25.
Administration of air
pollution control 66-31-26.
programs.
Air pollution emergencies *66-31-27.
endangering public health
anywhere in this state. *66-31-28.
Air contaminant emission
notices and emission
permits. **66-31-29.
Enforcement.
Variance board.
Variances.
Hearings.
Judicial review.
Injunctions.
Civil penalties.
Incinerators and open
burning—penalties.
Relations with the
federal government,
regional agencies, and
other states.
Organization within the
department of health.
Application of article.
Temporary emission con-
trol regulations and
continuance of existing
orders.
Local government—
authority—penalty.
Disposition of fines and
penalties.
Motor vehicle emissions
control program.
Training programs and
studies—emission
controls.
Emission data—public
availability.
(Senate Bill No. 69, 1970, EFFECTIVE DATE April 10, 1970)
*AMENDED S.B. 393, 49th GENERAL ASSEMBLY
**AMENDED H.B. 1503, 49th GENERAL ASSEMBLY
-------
Air Pollution Control - Page B-3
Chap. 66, Art. 31
66-31-1. SHORT TITLE.—This article shall be known and may be cited as
the "Air Pollution Control Act of 1970".
66-31-2. LEGISLATIVE DECLARATION.—In order to foster the health, wel-
fare, convenience, and comfort of the inhabitants of the state of Colorado, and
to facilitate the enjoyment of nature, scenery, and other resources of the state,
it is hereby declared to be the policy of the state to achieve the maximum prac-
tical degree of air purity in every portion of the state. To that end, it is
the purpose of this article to require the use of all available practical methods
to reduce, prevent, and control air pollution throughout the entire state of
Colorado, and to maintain a cooperative program between the state and local
units of government. It is further declared that the prevention, abatement,
and control of air pollution in each portion of the entire state are matters
of statewide concern and are affected with a public interest and that the
provisions of this article are enacted in the exercise of the police powers of
this state for the purpose of protecting the health, peace, safety, and general
welfare of the people of this state.
*/**66-31-3. DEFINITIONS.— (1) When used in this article and in regu-
lations and orders promulgated under authority of this article, the following
words and phrases shall have the meanings ascribed to them in this section:
(2) "Air contaminant" means fumes, smoke, particulate matter, vapor,
gas, or any combination thereof, but not including water vapor or steam con-
densate.
(3) "Air contamination source" means any source whatsoever at, from,
or by reason of which there is emitted or discharged into the atmosphere any
air contaminant.
(4) "Air pollution control authority" means the division, or any
person or agency given authority by the division, or a local governmental
unit duly authorized with respect to air pollution control.
(5) "Ambient air" is the surrounding or outside air.
(6) "Commission" means the air pollution control commission created
by section 66-31-4.
(7) "Division" means the division of administration of the depart-
ment of health.
(8) "Emission" means the discharge or release into the atmosphere
of one or more air contaminants.
(9) "Emission control regulation" means and includes any standard
promulgated by regulation which is applicable to all air contamination
sources within a specified area and which prohibits or establishes permis-
sible limits for specific types of emissions in such area, and also any regu-
lation which by its terms is applicable to a specified type of facility,
process, or activity for the purpose of controlling the extent, degree, or
nature of contamination emitted from such type of facility, process, or
activity, and also any regulation adopted for the purpose of preventing or
minimizing emission of any air contaminant in potentially dangerous quan-
tities.
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Chap. 66, Art, 31
(10) "Indirect air contamination source" means any facility, building,
structure, or installation, or any combination thereof, which can reasonably
be expected to cause or induce substantial mobile source activity which results
in emissions of air contaminants which might reasonably be expected to inter-
fere with the attainment and maintenance of federal ambient air standards.
(11) "Local air pollution law" means any law, ordinance, resolution,
code, rule or regulation adopted by the governing body of any city, town,
county, or city and county, pertaining to the prevention, control and abate-
ment of air pollution.
(12) "Motor vehicle" means any self-propelled vehicle which is
designed primarily for travel on the public highways and which is generally
and commonly used to transport persons and property over the public highways.
(13) "Person" means any individual, public or private corporation,
partnership, association, firm, trust, estate, the state or any department,
institution, or agency thereof, any municipal corporation, county, city and
county, or other political subdivision of the state, or any other legal en-
tity whatsoever which is recognized by law as the subject of rights and duties.
(14) "Variance board" means the variance board created by section
66-31-14.
66-31-4. AIR POLLUTION CONTROL COMMISSION CREATED.—(1) (a) There
is hereby created in the department of health the air pollution control com-
mission, which shall consist of nine members as follows:
(b) One member designated by the state board of health, appointed
by the governor.
(c) Eight citizens of the state of Colorado who shall be appointed
by the governor with the consent of the senate.
(d) Appointments to the commission shall be made so as to include
appropriate scientific, technical, agricultural, and legal training within
its own membership, although no specific number of its members shall be re-
quired to be so trained.
(2) (a) Initial appointments shall be for terms expiring January 30,
1971.
(b) Thereafter, terms shall be for three years, except that, of ap-
pointments made to begin on February 1, 1971, three shall be for terms expi-
ring January 30, 1972, and three for terms expiring January 30, 1973, and two
for terms expiring January 30, 1974. Thereafter, the three year terms of all
appointed members shall commence on February 1 of the year of appointment.
Any vacancy occurring during the term of office of any appointed member shall
be filled by appointment by the governor of a qualified person for the unex-
pired portion of the regular term.
(3) The governor may remove any appointed member of the commission
for malfeasance in office, failure to regularly attend meetings, or for any
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Chap. 66, Art. 31
cause that renders such a member incapable or unfit to discharge the duties
of his office, and any such removal, when made, shall not be subject to re-
view. If any member of the commission is absent from two consecutive meet-
ings, the chairman of the commission shall determine whether the cause of
such absences was reasonable. If he determines that the cause of the absen-
ces was unreasonable, he shall so notify the governor, who shall appoint a
qualified person for the unexpired portion of the regular term.
(4) Each member of the commission not otherwise in full-time employ-
ment of the state shall receive a per diem of forty dollars for each day
actually and necessarily spent in the discharge of official duties, but not
to exceed twelve hundred dollars in any one year; and all members, ex officio
and those appointed by the governor, shall receive traveling and other neces-
sary expenses actually incurred in the performance of official duties.
(5) The governor shall appoint the chairman, vice-chairman, and sec-
retary from among the membership of the commission for the first year of its
operation, and each year thereafter the commission shall select from its own
membership a chairman, vice-chairman, and secretary. The secretary of the
commission shall keep a record of its proceedings. The commission shall hold
regular public monthly meetings and may hold special meetings on the call of
the chairman or vice-chairman at such other times as deemed necessary. Writ-
ten notice of the time and place of all meetings shall be mailed by the sec-
retary at least five days in advance of any such meetings to each member.
(6) All members, both ex officio and those appointed by the governor,
shall have a vote. A majority of the commission shall constitute a quorum,
and the concurrence of a majority of the commission in any matter within its
powers and duties shall be required for any determination made by the commis-
sion.
66-31-5. DUTIES OF AIR POLLUTION CONTROL COMMISSION.—(1) The com-
mission shall develop and maintain a comprehensive program for prevention,
control, and abatement of air pollution throughout the entire state, inclu-
ding a program for control of emissions from all significant sources of air
pollution, and shall promulgate ambient air goals for every portion of the
state.
(2) The commission shall adopt and modify such plans for the imple-
mentation of such programs as may be necessary. Ambient air quality stan-
dards and emission control regulations shall be adopted and promulgated in
accordance with sections 66-31-7 and 66-31-8.
(3) The commission shall employ a technical secretary and shall
delegate to such secretary such duties and responsibilities as it may deem
necessary; except, that no authority shall be delegated to such secretary
to adopt, promulgate, amend, or to repeal standards or regulations, or to
make determinations, or to issue or countermand orders of the commission.
Such secretary shall have appropriate practical, educational, and admini-
strative experience related to air pollution control, and shall be employed
pursuant to the civil service laws of this state.
(4) The commission and the state board of health shall hold a joint
public hearing during the month of October of each year in order to hear
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Chap. 66, Art. 31
public comment on air pollution problems within the state, alleged sources of
air pollution within the state, and the availability of practical remedies
therefor; and at such hearing the technical secretary shall answer reasonable
questions from the public concerning administration and enforcement of the
various provisions of this article, as well as rules and regulations promul-
gated under the authority of this article.
(5) (a) Prior to the hearing required under subsection (4) of this
section, the commission shall prepare and make available to the public a re-
port which shall contain the following specific information:
(b) A description of the pollution problem in each of the polluted
areas of the state, described separately for each such area.
(c) To the extent possible, the identification of the sources of air
pollution in each separate area of the state, such as motor vehicles, indus-
trial sources, and power generating facilities.
(d) A list of all alleged violations of emission control regulations
which shows the status of control procedures in effect with respect to each
such alleged violation.
(6) On or before December 1 of each year, the commission shall report
to the governor on the effectiveness of the provisions of this article in
carrying out the legislative intent, as declared in section 66-31-2, and shall
include in such report such recommendations as it may have with respect to
any legislative changes that may be needed or desirable. The commission shall
include in its annual report to the governor such recommendations with respect
to emission standards and emission control devices for motor vehicles, air-
craft, and other mobile equipment as it deems advisable.
(7) The commission shall receive all applications for hearings con-
cerning violations and all applications for the granting of variances made
pursuant to section 66-31-13 (4) or 66-31-15, and may, in its discretion,
either set such applications for hearing and determination by the commission
in accordance with the provisions of sections 66-31-15 and 66-31-16, or trans-
mit such applications to the variance board for hearing and determination in
accordance with the provisions of sections 66-31-15 and 66-31-16.
(8) The commission may, in its discretion, review any variance order
or determination of the variance board within thirty days of the issuance
thereof as provided for by section 66-31-16 (9).
**66-31-6. COMMISSION—ADDITIONAL AUTHORITY.—(1) (a) The commission
shall have maximum flexibility in developing an effective air pollution con-
trol program and may promulgate such combination of regulations as may be
necessary or desirable to carry out the legislative purpose set forth in sec-
tion 66-31-2. Such regulations may include, but shall not be limited to:
(b) Division of the state into such control zones or areas as may be
necessary or desirable for effective administration of the air pollution con-
trol program.
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Chap. 66, Art. 31
(c) Classification and definition of different degrees or types of
air pollution.
(d) Emission control regulations that are applicable to the entire
state, that are applicable only within specified areas or zones of the state,
or that are applicable only when a specified class of pollution is present.
(2) The commission may hold public hearings, issue notice of hear-
ings, issue subpoenas requiring the attendance of witnesses and the produc-
tion of evidence, administer oaths, and take such testimony as it deems
necessary, all in conformity with article 16 of chapter 3, C.R.S. 1963, and
with sections 66-31-9 and 66-31-16.
(3) The commission may adopt such rules and regulations governing
procedures before the variance board as may be necessary to assure that
hearings before said board will be fair and impartial.
(4) In the event the commission, after hearing, finds and determines
that a particular style or model of automobile air pollution control device
is not sufficiently effective to justify the continued connection and opera-
tion of such device, the commission shall so notify the motor vehicle divi-
sion of the department of revenue; thereafter, all devices of such particular
style or model shall be exempt from the provisions of sections 13-5-113 and
13-5-160, C.R.S. 1963.
(5) The commission may exercise all incidental powers necessary to
carry out the purposes of this article.
(6) (a) The commission may require the owner or operator, or both,
of any air contamination source to:
(b) Establish and maintain reports as precribed by the commission;
(c) Install, use, and maintain monitoring equipment or methods as
prescribed by the commission;
(d) Record sample emissions in accordance with such methods, at
such locations, at such intervals, and in such manner as the commission
shall prescribe;
(e) Provide such other information as the commission may require.
66-31-7. COMMISSION TO PROMULGATE AMBIENT AIR QUALITY STANDARDS.—
(1) (a) In addition to the other powers and duties enumerated in this arti-
cle, the commission shall have the power to adopt, promulgate, amend, and
modify such standards for the quality of ambient air as may be appropriate
or necessary to carry out the purposes of this article, including, but not
limited to:
(b) Standards which describe the maximum concentrations of speci-
fically described contaminants that can be tolerated, consistent with the
protection of the good health of the public at large; such standards may
differ for different parts of the state as may be necessitated by varia-
tions in altitude, topography, climate, or meteorology;
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Chap. 66, Art. 31
(c) Standards which describe the air quality goals that are to be
achieved by control programs within specified periods of time; such stand-
ards may be either statewide or restricted to specified control areas, and
(d) Standards which describe varying degrees of contamination of
ambient air.
(2) Ambient air standards shall include such requirements for test
methods and procedures as will assure that the samples of ambient air tested
are representative of the ambient air.
66-31-8. COMMISSION TO PROMULGATE EMISSION CONTROL REGULATIONS.—
(1) (a) As promptly as possible, the commission shall adopt and promulgate
emission control regulations which require the use of effective practical
air pollution controls for each and every significant source, potential
source, and type of source of air contamination throughout the entire state
and thereafter may modify such regulations from time to time. In the formu-
lation of each emission control regulation, the commission shall take into
consideration the following:
(b) The state policy regarding air pollution, as set forth in sec-
tion 66-31-2;
(c) Federal recommendations;
(d) The degree to which the concentrations of certain types of con-
taminants in certain portions of the state require that emission control
regulations be more stringent than in other portions of the state;
(e) The degree to which any particular type of emission is subject
to treatment, the availability and feasibility of control techniques, and
the extent to which the emission to be controlled is significant;
(f) The continuous, intermittent, or seasonal nature of the emis-
sion to be controlled;
(g) Whether the emission control regulation should be applied
throughout the entire state or only in a specified portion of the state;
(h) The need for specification of safety precautions that should
be taken with respect to any source or potential source or type of source
of air contamination.
(2) (a) Such emission control regulations may include, but shall
not be limited to, regulations pertaining to:
(b) Visible pollutants;
(c) Particulates;
(d) Sulfur oxides, sulfuric acids, hydrogen sulfide, nitrogen oxides,
carbon oxides, hydrocarbons, fluorides, and any other chemical substance;
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Chap. 66, Art. 31
(e) Odors;
(f) Open burning of incidental refuse, open burning at dumps, open
burning for agricultural purposes, open burning of junk automobiles, and any
other open burning activity;
(g) Organic solvents;
(h) Photochemical substances;
(i) Toxic gases.
(3) (a) The commission shall have the duty to identify each type of
facility, process, and activity which produces or which potentially or acci-
dentally might produce significant emissions of air contaminants, and shall
promulgate an emission control regulation for each such facility, process,
and activity, except for motor vehicles and airplanes to the extent prohi-
bited by federal law. The requirements and prohibitions contained in such
regulations shall be set forth with as much particularity and clarity as is
practical. Upon adoption of an emission control regulation under this sub-
section (3) for the control of a specific facility, process, or activity,
such regulation shall apply to the exclusion of other emission control regu-
lations adopted pursuant to subsection (2) of this section; prior to such
adoption the general regulations adopted pursuant to subsection (2) shall be
applicable to such facility, process, or activity. Emission control regula-
tions adopted pursuant to this section may include, but shall not be limited
to, regulations pertaining to the following facilities, processes, and acti-
vities ;
(b) Incinerator and incinerator design;
(c) Storage and transfer of petroleum products and any other vola-
tile substance;
(d) Activities which frequently result in particulate matter becom-
ing airborne, such as construction and demolition operations, and operation
of parking lots;
(e) Specifications, prohibitions, and requirements pertaining to
fuels and fuel additives, such as tetraethyl lead;
(f) Wigwam waste burners, pulp mills, alfalfa dehydrators, asphalt
plants, and any other industrial or commercial activity which tends to emit
air contaminants as a by-product;
(g) Industrial process equipment;
(h) Industrial spraying operations;
(i) Reduction of animal matter;
(j) Motor vehicles and airplanes;
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Chap. 66, Art. 31
(k) Diesel-powered machines, vehicles, engines, and equipment;
(1) Storage and transfer of toxic gases.
(4) Among its emission control regulations the commission shall in-
clude appropriate regulations pertaining to accidents, shutdowns, and other
conditions which justify temporary relief from controls.
(5) Each emission control regulation shall be operative without
regard to any ambient air quality standard unless such regulation expressly
provides otherwise.
66-31-9. COMMISSION—PROCEDURES TO BE FOLLOWED IN SETTING STANDARDS
AND REGULATIONS.—(1) Prior to adopting, promulgating, amending, or modify-
ing any ambient air standard authorized in section 66-31-7, or any emission
control regulation authorized in section 66-31-8, the commission shall con-
duct a public hearing thereon as provided in section 3-164, C.R.S. 1963.
Notice of any such hearing shall conform to the requirements of section
3-16-2, C.R.S. 1963, but such notice shall be given at least sixty days
prior to the hearing and shall include each proposed regulation, and shall
be mailed to all persons who have filed with the commission a written re-
quest to receive such notices.
(2) Any person desiring to propose a regulation differing from the
regulation proposed by the commission shall file such other proposal with
the commission not less than twenty days prior to the hearing, and, when on
file, such proposal shall be open for public inspection.
(3) Witnesses at the hearing shall be subject to cross-examination
by or on behalf of the commission, and by or on behalf of persons who have
proposed regulations pursuant to subsection (2) of this section.
(4) Regulations promulgated pursuant to sections 66-31-7 and 66-31-8
shall not take effect until thirty days after they have been filed with the
secretary of state.
66-31-10. ADMINISTRATION OF AIR POLLUTION CONTROL PROGRAMS.—(1) The
division shall administer and enforce the air pollution control programs
adopted by the commission. In furtherance of such responsibility of the
division, the executive director of the department of health shall establish
within the division a separate air pollution control agency the head of which
shall be a registered professional engineer or shall have a graduate degree
in engineering or other specialty dealing with the problems of air pollution
control. He shall also have appropriate practical and administrative experi-
ence related to air pollution control. Such person shall not be the technical
secretary employed pursuant to section 66-31-5 (3). All policies and proce-
dures followed in the administration and enforcement of the air pollution
control programs which have been adopted by the commission shall be subject
to supervision by the state board of health.
(2) (a) In addition to authority specified elsewhere in this article,
the division shall have the power to:
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Chap. 66, Art. 31
(b) Conduct or cause to be conducted studies and research with re-
spect to air pollution and the control, abatement, or prevention thereof, as
requested by the commission;
(c) Determine, by means of field studies and air monitoring and sam-
pling, if the ambient air standards are being violated in any area of the
state;
(d) Enter and inspect any property, premise, or place for the pur-
pose of investigating any actual, suspected, or potential source of air
pollution or air contamination, or ascertaining compliance or noncompliance
with any emission standard or any order promulgated under this article;
except that if such entry or inspection is denied or not consented to, and
no emergency exists, the division is empowered to and shall obtain from the
district or county court for the district or county in which such property,!
premise, or place is located, a warrant to enter and inspect any such pro-
perty, premise, or place prior to entry and inspection. The district and
county courts of the state of Colorado are empowered to issue such warrants
upon a proper showing of the need for such entry and inspection. Any infor-
mation relating to secret process, or methods of manufacture, or production,
obtained in the course of the inspection or investigation, shall be kept
confidential. If samples of air or air contaminants are taken for analysis,
a duplicate of the analytical reports shall be furnished promptly to the
person who is suspected of causing such air pollution or air contamination;
(e) Furnish technical advice and services relating to air pollution
problems and control techniques;
(f) Inform the appropriate governmental agency of the results of
atmospheric tests conducted in its jurisdiction, and notify the affected
city, town, county, or city and county, whenever tests establish that the
ambient air or source or sources of emission of smoke or air contaminant
fail to meet the standards established under this article;
(g) Designate one or more persons or agencies in any area of the
state as an air pollution control authority as agent of the division to
exercise and perform such powers and duties of the division as may be speci-
fied in such designation;
(h) Furnish such personnel to the variance board and the commission
as the variance board and commission may reasonably require to carry out
their duties and responsibilities under this article;
(i) Certify, or otherwise designate, to any other agency or depart-
ment of the government of this state or of any other state or of the federal
government, that any facility, land, building, machinery or equipment, or
any part thereof, has been constructed, erected, installed, or acquired in
confcuii'i t.y with the requirements of this state or of this article for control
of air pollution or in conformity with the requirements for control of air
pollution of any other stale or the federal government.
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Chap. 66, Art. 31
**66-31-ll. AIR POLLUTION EMERGENCIES ENDANGERING PUBLIC HEALTH
ANYWHERE IN THIS STATE.—(1) (a) Whenever the division shall determine,
after investigation, that any person is either engaging in any activity
involving a significant risk of air contamination or is discharging or
causing to be discharged into the atmosphere, directly or indirectly, any
air contaminant, and such activity or discharge constitutes a clear, present,
and immediate danger to the health of the public, or that any such activity
or discharge of air contaminants, if permitted to continue unabated, will
result in a condition of clear, present, and immediate danger to the health
of the public, the division shall:
(b) Issue a written cease and desist order to said person requir-
ing immediate discontinuance of such activity or the discharge of such con-
taminant into the atmosphere, and upon receipt of such order, such person
shall immediately discontinue such activity or discharge; or
(c) Apply to any district court of this state for the district in
which the said activity or discharge is occurring for a temporary restraining
order, temporary injunction, or permanent injunction as provided for in the
Colorado rules of civil procedure. Any such action in a district court shall
be given precedence over all other matters pending in such district court.
The institution of such injunction proceedings by the division shall confer
upon said district court exclusive jurisdiction to determine finally the
subject matter of the proceeding; or
(d) Both issue such a cease and desist order and apply for any such
restraining order or injunction.
(2) (a) Whenever the division shall determine, after investigation,
that the contaminated condition of the ambient air in any portion of this
state constitutes a clear, present, and immediate danger to the health of
the public, or that any activity or discharge of air contaminants, if per-
mitted to continue unabated, will result in a condition of clear, present,
and immediate danger to the health of the public, and that the procedures
available to the division under subsection (1) of this section will not
adequately protect the public, it shall immediately notify the governor of
its determination of either of such conditions, and it shall request the
governor to declare a state of air pollution emergency in such portion of
this state.
(b) (i) Upon such notification and request by the division, the
governor is empowered to declare a state of air pollution emergency in such
portion of the state, and to take any and all actions necessary to protect
the health of the public in such portion of the state, including, but not
limited to:
(ii) Ordering a halt or curtailment of the movement of all motor
vehicles except emergency vehicles; and
(iii) Ordering a halt or curtailment of all operations, activities,
processes, or conditions which he reasonably believes to be contributing to
such emergency.
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Chap. 66, Art. 31
(c) From time to time, whenever appropriate, the governor, in coop-
eration with his department heads, shall develop or modify such plans as will
be necessary or appropriate to control and abate the air pollution conditions
most likely to require the exercise of the powers granted in paragraph (b) of
this subsection (2).
**66-31-12. AIR CONTAMINANT EMISSION NOTICES AND EMISSION PERMITS.—
(1) After ninety days from the date on which this act becomes law, no per-
son shall permit emission of air contaminants from, or construction or alter-
ation of, any facility, process, or activity except residential structures,
from which air contaminants are, or are to be, emitted through any perma-
nently located chimney, stack, pipe or other conduit unless and until an "air
contaminant emission notice" has been filed with the division with respect
to such emission. A revised emission notice shall be filed whenever a sig-
nificant change in emissions is anticipated or shall have occurred.
(2) Each such notice shall specify the location at which the pro-
posed emission will occur, the name and address of the person operating or
owning such facility, process, or activity, the nature of such facility,
process, or activity, and an estimate of the quantity and composition of
the expected emission. The division shall make available at all air pollu-
tion control authority offices appropriate forms on which the information
required by this section shall be furnished.
(3) If the information required by subsection (1) of this section
is on file with the division at the time this act becomes effective, such
information shall be deemed to constitute compliance with the requirements
of said subsection (1) as to the emission covered thereby.
(4) (a) No person shall construct or substantially alter any build-
ing, facility, structure, or installation, except single family residential
dwellings, or install any machine, equipment or other device, or commence
the conduct of any activity, or commence performance of any combinations
thereof, or commence operations of any of the same which will or does con-
stitute a new air contamination source or a new indirect air contamination
source without first obtaining or having a valid permit therefor from the
commission; except that no permit shall be required for new indirect air
contamination sources until regulations regarding permits for such sources
shall have been promulgated by the commission. The commission shall esta-
blish rules, regulations, and procedures in accordance with the provisions
of this article for the issuance or denial of permits which shall be in
conformity with the purposes of this article as set forth in section 66-31-2,
but in no event shall regulations governing indirect air contamination
sources be more stringent than those required for compliance with the fed-
eral "Clean Air Act of 1970", as the same may be amended from time to time,
and final rules and regulations adopted pursuant thereto. Such procedures
shall include, but not be limited to, the following:
(b) Filing an application with the division which may include such
relevant plans, specifications, air quality data, and other information as
the division may reasonably request.
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Chap. 66, Art. 31
(c) The division shall prepare its preliminary analysis of the
effect upon the ambient air quality and the extent of emission control
within twenty days after date on which an application is filed.
(d) For those types of projects or activities defined or desig-
nated by the commission as warranting public comment with respect thereto,
the division shall within fifteen days after it has prepared its prelimi-
nary analysis give public notice of the proposed project or activity by
at least one publication in a newspaper of general circulation in the
county in which the proposed project or activity, or a part thereof, is
to be located. If no qualified newspaper is published within such county,
then the publication shall be made in a newspaper published in an adjoin-
ing or nearby county. The division shall also within such period of time
maintain in the office of the county clerk and recorder of the county in
which the proposed project or activity, or a part thereof, is located a
copy of its preliminary analysis and a copy of the application with all
accompanying data for public inspection. The division shall receive and
consider public comment thereon for a period of thirty days thereafter.
(e) Within thirty days following the period for public comment,
or within fifteen days after the preparation of its preliminary analysis
where no delay for public comment is required, the division shall grant
the permit unless it determines that the proposed project or activity would
not meet applicable emission standards or regulations of the commission or
would interfere with the attainment or maintenance of the then existing
federal primary or secondary ambient air standards; the division shall
deny the permit if such standards would not be met except that when the
proposed project or activity utilizes the best practical alternatives
even through applicable emission control regulations and ambient air qual-
ity standards would not be met or the modification or replacement of a
stationary source, by using the best practical technology, would signi-
ficantly reduce emissions, the division shall consult with the commission
and thereafter the division, with the concurrence of the commission, or
the commission alone, may grant the permit. Any permit issued by the divi-
sion may contain such terms and conditions as it deems necessary for the
proposed project or activity to qualify for a permit. If any of such terms
or conditions of the permit are violated, the division may revoke the per-
mit. If the division fails to act upon the application within the pre-
scribed time, the permit shall be deemed to have been granted.
(f) If the division denies or revokes a permit, the applicant
may request a conference with the commission or a hearing before the com-
mission in accordance with the provisions of section 66-31-16. The commi-
sion may delegate the responsibility to hold a conference or hearing with
respect to any such request to the variance board.
(g) Within thirty days after such conference or Bearing, the com-
mission or variance board shall issue an order either affirming or revers-
ing the decision of the division. If the decision or revocation of the
division is reversed, the commission or variance board shall order the
issuance or reinstatement of the permit which order may contain such terms
and conditions as shall be necessary and reasonable. If a conference is
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Chap. 66, Art. 31
requested in lieu of a hearing, the applicant may request a hearing there-
after if the applicant is not satisfied with the results of such conference.
(h) Orders of the commission or variance board shall be final upon
the date of issuance.
(i) No person shall commence the operation of any project or the
conduct of any activity for which a permit has been issued without giving
at least thirty days prior notice to the division of the date on which such
commencement is to take place. During such thirty-day period and again
within thirty days after commencement, the division shall inspect the pro-
ject or activity to determine whether or not the terms and conditions of
the permit have been properly satisfied. If the division finds that the
terms or conditions of the permit have been violated it may revoke the
permit, or it may grant a period of not more than six months in which the
terms or conditions may be satisfied. If the division determines that the
terms and conditions of the permit have not been satisfied within such per-
iod of time, the division shall revoke the permit. If the division deter-
mines that the terms and conditions of the permit have been satisfied, the
division shall grant its final approval of the permit whereupon all require-
ments of this subsection (4) shall have been fulfilled by the applicant.
(j) Any permit issued under prior existing law with respect to a
project or the operation thereof shall continue in full force and effect
and shall not be affected by the terms hereof and the holder of such a per-
mit shall not be required to comply with the provisions hereof. Regulations
concerning permits for the construction and operation of new direct air
contamination sources in effect as of July 1, 1973, and not inconsistent
with the provisions of this article shall continue in effect until repealed
or amended from time to time by the commission.
**66-31-13. ENFORCEMENT.—(1) The division shall enforce compliance
with the emission control regulations promulgated pursuant to the provisions
of section 66-31-8.
(2) In case any written and verified complaint shall be filed with
the division alleging that, or in case the division itself shall have cause
to believe that, any person is violating any emission control regulation,
the division shall cause a prompt investigation to be made, and if the per-
son who makes such investigation on behalf of the division shall find after
such investigation that a violation of any such regulation exists, he shall
promptly so notify both the alleged violator and the commission in writing.
Thereupon the division shall diligently endeavor to obtain voluntary abate-
ment of such violation.
(3) After notice has been given pursuant to subsection (2) of this
section, but in no event later than six months after the giving of such
notice, if the alleged violation has not been abated, the division shall
cause to be issued and served upon the person allegedly violating any such
regulation, a written order which shall specify the provision of the emis-
sion control regulation of which such person is said to be in violation,
and a statement of the manner in which such person is said to violate it,
and such order shall require the person so complained against to cease and
desist from such violation within such reasonable time as the division may
determine, but not to exceed six months.
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Chap. 66, Art. 31
(4) (a) (i) Within twenty days after receipt of such order, if
subsection (4) (a) (ii) or (iii) of this section is applicable; and, at
the election of the recipient of the order, either within twenty days after
receipt of such order or on or before thirty days prior to the effective
date of said order, if subsection (4) (a) (iv) is applicable, the recipient
thereof may file with the commission or the variance board a written peti-
tion requesting a hearing to determine any one of the following matters:
(ii) Whether or not the alleged violation exists or did exist;
(iii) Whether or not the alleged violation exists or did exist
and whether or not a variance should be granted with respect to any viola-
tion determined to exist or have existed;
(iv) Whether or not a variance should be granted with respect to
such violation.
(b) In no event shall the recipient have the right to separate
hearings to determine the matters described in paragraph (a) of this sub-
section (4), provided always in the case of a hearing provided for in sub-
paragraph (iii) of paragraph (a), the commission or variance board shall
render its final determination of whether or not the alleged violation
exists or did exist before proceeding to take or hear evidence or make any
final determination based thereon as to whether or not a variance should
be granted with respect to an alleged violation; and further provided the
commission or variance board may authorize separate hearings to determine
the matters described in said paragraph (a) (iii) if it is determined that
such separate hearings are necessary and proper for a fair and impartial
hearing under the circumstances.
(c) Except with respect to actions taken pursuant to section
66-31-11, upon the filing of such a request with the commission or variance
board, the order shall be stayed pending the final determination of the
petition by the commission or variance board.
66-31-14. VARIANCE BOARD.—(1) (a) There is hereby created a
variance board which shall consist of nine members as follows:
(b) One member designated by the state board of health to repre-
sent said board in matters of air pollution in the interests of the public
health of the people of the state;
(c) One member shall be a registered professional engineer with at
least five years' experience in the actual practice of his profession, and
who is not from industry;
(d) One member, who is not from industry, shall be either a physi-
cian licensed to practice in this state, or a toxicologist;
(e) Three members from industry in this state;
(f) Three members, as representatives of the public at large, not
from industry.
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Chap. 66, Art. 31
(2) All members appointed under the provisions of paragraphs (c)
to (f) of this subsection (1) shall be appointed by the governor.
(3) All members appointed by the governor shall hold office for
terms of four years and until their successors are selected and qualified.
The member designated by the state board of health shall serve at the dis-
cretion of the state board of health. There shall be no limitation on the
number of terms any appointed member may serve. If any member of the vari-
ance board appointed by the governor shall resign or be removed from the
variance board, the governor shall promptly appoint a new member, as pro-
vided in this section, to fill the vacancy for the remainder of the term
of the member of the variance board who has ceased to be a member thereof.
(4) The governor shall appoint alternates for all members of the
variance board appointed by him. Each such alternate shall have the same
qualifications as the member for which appointed. Each alternate shall be
appointed for a term which shall terminate on the same date as that of the
member for which appointed. An alternate shall act as a member of the vari-
ance board, only when the member for whom appointed fails or refuses to so
act, and when so acting, the alternate shall have all the rights, powers,
duties, and functions of a member of the variance board. Alternates shall
be compensated as provided in subsection (9) of this section.
(5) The governor may remove any appointed member of the variance
board for malfeasance in office, failure to regularly attend meetings, or
for any cause that renders such a member incapable or unfit to discharge
the duties of his office, and any such removal, when made, shall not be
subject to review. If any member of the variance board is absent from two
consecutive meetings, the chairman of the variance board shall determine
whether the cause of such absences was reasonable. If he determines that
the cause of the absences was unreasonable, he shall so notify the governor,
who shall appoint a qualified person for the unexpired portion of the regu-
lar term.
(6) (a) The variance board shall:
(b) Elect its chairman annually from its members for a term of one
year;
(c) Meet at least quarterly, but special meetings of the variance
board may be called by its chairman upon his own initiative, or by the com-
mission, and such a meeting shall be called by him upon the receipt by him
of a written request therefor, signed by two or more members of said vari-
ance board;
(d) Keep a record of its proceedings.
(7) Five members shall constitute a quorum, and the concurrence of
at least a majority of all members of the variance board in any matter within
its powers and duties shall be required for any determination made by the
said variance board.
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Chap. 66, Art. 31
(8) At least three days prior to each meeting, written notice shall
be given to each member of the variance board of the time, place, and pur-
pose of such meeting.
(9) Each member of the variance board shall receive a per diem of
forty dollars for each day actually spent in the discharge of official
duties, not to exceed twelve hundred dollars in any one year; and shall be
reimbursed for necessary and actual expenses incurred in the performance
of his duties under this article.
(10) The individuals serving as members of the air pollution vari-
ance board as existing pursuant to article 29 of chapter 66, C.R.S. 1963,
as that article existed on January 1, 1970, shall serve as the variance
board created by this article until the expiration dates of the respective
terms to which they have been appointed.
66-31-15. VARIANCES.—(1) (a) The variance board or commission
may grant a variance, suspending or modifying the enforcement of any emis-
sion control regulation, or any rule, regulation, or enforcement order
issued pursuant to this article against any person, whenever the said vari-
ance board or commission shall determine that:
(b) Control techniques are not available or that compliance with
applicable emission control regulations from which a variance is sought
would create an unreasonable economic burden; and
(c) That the granting of such variance would be consistent with,
and aid in, implementing the legislative policy as set forth in section
66-31-2.
(2) The variance board or the commission shall grant a variance
suspending or modifying the enforcement of any emission control regulation,
or any rule, regulation, or enforcement order issued pursuant to this arti-
cle against any person, whenever the said variance board or the commission
shall determine that strict compliance with any provision of, or order
issued pursuant to, this article would result in an arbitrary and unreason-
able taking of property or in the practical closing of any lawful business
or activity and such would be without sufficient corresponding public bene-
fit.
(3) The variance shall be granted, terminated, or modified by the
variance board or the commission only after a hearing before it, held pur-
suant to the provisions of this article. A variance may be granted with
respect to any existing or proposed facility, process, or activity. Hear-
ings may be requested either by the variance board, the commission, the
division, or by any person applying for or having received such a variance.
(4) Any variance granted pursuant to the provisions of this article
shall be granted for such period of time and under such conditions as shall
be specified by the variance board or the commission. The failure to meet
any condition of the variance without prior written permission of the said
variance board or the commission shall render such variance null and void.
The variance board shall review, at least annually, any variance that has
been granted to determine whether the terms and conditions of said variance
have been complied with, and whether the continuance of the variance is jus-
tified.
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Chap. 66, Art. 31
(5) Nothing in this section, and no variance or renewal granted
pursuant hereto, shall be construed to prevent or limit the application of
the emergency provisions of section 66-31-11.
(6) The variance board shall have the power to hold public hearings,
conduct investigations, compel the attendance of witnesses, receive such
pertinent and relevant proof and do such other things as it may deem to be
necessary, proper, or desirable in order that it may effectively discharge
its duties and responsibilities under this article; all in conformity with
article 16 of chapter 3, C.R.S. 1963, and with regulations of the commis-
sion adopted pursuant to section 66-31-6.
**66-31-16. HEARINGS.—(1) Not less than fifteen days after a hear-
ing has been requested, the variance board or the commission, as the case
may be, shall grant such request and set a time and place therefor. Every
such hearing shall be conducted pursuant to the provisions of this article
and the provisions of article 16 of chapter 3, C.R.S. 1963.
(2) The division shall appear as a party in any hearing before the
variance board or the commission and shall have the same rights to judicial
review as any other party.
(3) All testimony taken at any such hearing before the variance
board or the commission shall be under oath or affirmation. A full and
complete record of all proceedings and testimony presented shall be taken
and filed. The stenographer shall furnish, upon payment and receipt of
any fees allowed therefor, a certified transcript of the whole or any part
of his record to any party in such hearing requesting the same.
(4) Any information relating to secret processes, methods of manu-
facture or production, which may be required, ascertained, or discovered,
shall not be publicly disclosed in public hearings or otherwise, and shall
be kept confidential by any member, officer, or employee of the variance
board, the commission or the division, but any person seeking to invoke
the protection of this section in any hearing for a variance shall bear
the burden of proving its applicability.
(5) At any hearing, any person who is affected by the proceeding
and whose interests are not already adequately represented, shall have the
opportunity to be a party thereto'upon prior application to and approval
by the variance board or commission, in its sole discretion, as deemed
reasonable and proper by said variance board and commission, and such per-
son shall have the right to be heard and to cross-examine any witness.
(6) After due consideration of the written and oral statements,
the testimony, and the arguments presented at any such hearing, the variance
board or commission shall enter its findings and final order, based upon
evidence in the record, or make such final determination of the matter as
it shall deem appropriate.
(7) In all proceedings before the variance board or the commission
with respect to any alleged violation of any emission control regulation or
order, the burden of proof shall be upon the division.
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Chap. 66, Art. 31
(8) The applicant for a variance shall bear the burden of proof.
(9) Variances, orders, and determinations of the variance board
shall become final within thirty days from the date on which they are issued,
unless within such period the variance board grants a rehearing, or unless
within such period the commission concludes that said variance, order, or
determination interferes with the attainment of the objectives of this arti-
cle, as set forth in section 66-31-2. If the commission so concludes, it
shall, within said thirty-day period, notify the applicant of such conclu-
sion, including the nature of the interference involved, and allow the appli-
cant ten days in which to request a hearing before the commission on said
variance, order, or determination, which hearing shall be set and held in
accordance with the provisions of section 66-31-15 and of this section. Fol-
lowing the hearing before the commission, or if no hearing is requested, the
commission shall enter its final order affirming or modifying said variance,
order, or determination.
(10) Every hearing granted by the variance board or the commission
shall be conducted by either body or by a hearing officer designated by
either body, and every hearing shall comply with the provisions of this
article and the provisions of article 16 of chapter 3, C.R.S. 1963.
66-31-17. JUDICIAL REVIEW.—(1) Any final order or determination
by the variance board, the division, or the commission, shall be subject to
a judicial review in accordance with the provisions of this article and the
provisions of article 16 of chapter 3, C.R.S. 1963. Such final order or
determination shall be stayed pending the decision of the court.
(2) Any party may move the court to remand the case to the variance
board, the division, or the commission in the interests of justice, for the
purpose of adducing additional specified and material evidence, and findings
thereon; but such party shall show reasonable grounds for the failure to ad-
duce such evidence previously before the variance board, the division, or
the commi s s ion.
(3) Any proceeding for judicial review of any final order or deter-
mination of the variance board, the division, or the commission shall be
filed in the district court for the district in which is located the air
contamination source affected, and shall be filed within twenty days after
the date of said final order or determination.
66-31-18. INJUNCTIONS.—In the event any person fails to comply with
a cease and desist order that is not subject to a stay pending administrative
or judicial review, the commission may request the district attorney for the
district in which the alleged violation exists, or the attorney general, to
bring, and if so requested it shall be his duty to bring, a suit for an in-
junction to prevent any further or continued violation of such order. In
any such suit the final findings of the division or commission, based upon
evidence in the record, shall be prima facie evidence of the fact or facts
found therein.
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Chap. 66, Art. 31
66-31-19. CIVIL PENALTIES.—(1) (a) Penalties shall be determined
and collected by a court of competent jurisdiction upon action instituted by
the division for the determination and collection of said penalty under this
section, and in accordance with the following provisions:
(b) Any person who shall violate any final cease and desist order
which is not subject to a stay pending judicial review and which has been
issued either pursuant to article 29 of chapter 66 prior to adoption of this
article or pursuant to this article shall be subject to a civil penalty of
not more than two thousand five hundred dollars per day for each day during
which such violation occurs.
(c) On and after July 1, 1970, any person failing to comply with
the provisions of section 66-31-12 (1) shall be subject to a civil penalty
of not more than one hundred dollars.
66-31-20. INCINERATORS AND OPEN BURNING—PENALTIES.— (1) (a) The
commission shall adopt a program to control incinerator burning and open
burning in each portion of the state in which such control is necessary in
order to carry out the policies of this article as set forth in section
66-31-2. Such program shall include emission control regulations and the
designation, after public hearing and from time to time, of such portions
by legal description.
(b) Open burning in the course of agricultural operations may be
regulated only where the absence of regulations would substantially impede
the commission in carrying out the objectives of this act. In adopting any
program applicable to agricultural operations, the commission shall take
into consideration the necessity of conducting open burning.
(2) (a) Within such designated portions of the state, no person
shall burn or permit to be burned in any incinerator or on any open premises
owned or controlled by him, or on any public street, alley, or other land
adjacent to such premises, any rubbish, waste paper, wood, or other flam-
able material, unless a permit therefor shall first have been obtained from
the appropriate air pollution control authority. In granting or denying the
issuance of any such permit, said authority shall base its action on the
location and proximity of such burning to any building or other structure,
the potential contribution of such burning to air pollution in the area,
climatic conditions on the day or days of such burning, and compliance by
the applicant for the permit with applicable fire protection and safety
requirements of the local authority or area.
(b) In all or any part of any portion of the state designated pur-
suant to subsection (1) of this section the prohibition contained in this
subsection (2) may be suspended by the commission with respect to any parti-
cular type or category of incinerator or open burning upon a finding that
enforcement of the prohibition would neither significantly assist in the
prevention, abatement, and control of air pollution, nor significantly en-
hance the quality of the ambient air in such designated area.
(3) Any person who violates subsection (2) (a) of this section by
burning or permitting any burning without first having obtained a permit as
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Air Pollution Control - Page B-22
Chap. 66, Art. 31
required shall be subject to a civil penalty of not more than one hundred
dollars per day for each day during which such a violation occurs.
66-31-21. RELATIONS WITH THE FEDERAL GOVERNMENT, REGIONAL AGENCIES,
AND OTHER STATES.—(1) The department of health shall serve as the state
agency for all purposes of the federal "Clean Air Act", as amended, and regu-
lations promulgated under said act, and shall accept and supervise the ad-
ministration of loans and grants from the federal government and from other
sources, public or private, which are received by the state for air pollution
control purposes.
(2) As promptly as possible the commission shall hold a public hear-
ing and adopt ambient air quality standards for the Denver air quality con-
trol region which has heretofore been designated by the federal government.
(3) The department of health may enter into agreements with any
air pollution control agencies of the federal government, or other states,
and with regional air pollution control agencies, but any such agreement
involving, authorizing, or requiring compliance in this state with any am-
bient air standard or emission control regulation shall not be effective
unless or until the commission has held a hearing with respect to such stand-
ard or regulation and has adopted the same in compliance with section 66-31-9.
66-31-22. ORGANIZATION WITHIN THE DEPARTMENT OF HEALTH.—The air
pollution control commission, together with the variance board and the
technical secretary under said commission, shall exercise their powers and
perform their duties and functions specified in this article in the depart-
ment of health as if the same were transferred to the department by a
"Type 1" transfer, as such transfer is defined in the "Administrative
Organization Act of 1968", being chapter 53, Session Laws of Colorado 1968.
66-31-23. APPLICATION OF ARTICLE.—(1) The factual or legal basis
for proceedings or other actions that shall result from a violation of any
emission control regulation inure solely to, and shall be for the benefit
of the people of the state generally, and it is not intended to create by
this article, in any way, new or enlarged private rights or to enlarge exist-
ing private rights, or to diminish private rights. A determination that air
pollution or air contamination exists or that any standard has been disre-
garded or violated, whether or not a proceeding or action may be brought by
the state, shall not create by reason thereof any presumption of law or
finding of fact which shall inure to or be for the benefit of any person
other than the state.
(2) Other than section 66-31-11, the provisions of this article and
regulations adopted hereunder shall not apply to air contamination insofar
as such contamination exists within the confines of a particular commercial
or industrial plant, works, or shop which is the source of air contamination,
and shall not apply or affect the relations between employers and employees,
with respect to, or arising out of, any condition of air contamination.
(3) It is the purpose of this article to provide additional and
cumulative remedies to prevent and abate air pollution and air contamination.
Nothing in this article shall abridge or alter rights of action or remedies
now or hereafter existing, nor shall any provision of this article or any-
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Air Pollution Control - Page B-23
Chap. 66, Art. 31
thing done by virtue of this article be construed as estopping individuals,
cities, towns, counties, cities and counties, or duly constituted political
subdivisions of the state, from the exercise of their respective rights to
suppress nuisances.
66-31-24. TEMPORARY EMISSION CONTROL REGULATIONS AND CONTINUANCE OF
EXISTING ORDERS.—(1) Upon the effective date hereof, the commission shall
be deemed to have adopted temporary emission control regulations whose pro-
visions are identical to the provisions of section 66-29-5 (2) through (6),
as those subsections existed on January 1, 1970, and such regulations shall
be in full force and effect in each area of the state which was designated
by the division pursuant to section 66-29-8 (1) (c) , as that paragraph
existed on January 1, 1970, and such temporary emission control regulations
shall remain in full force and effect until modified, altered, or revoked
by the commission.
(2) All actions, orders, and determinations by the division of
administration and the state board of health pursuant to article 29 of
chapter 66, as that article existed on January 1, 1970, shall remain in
full force and effect until countermanded or modified by the division.
(3) All actions, orders, and determinations of the air pollution
variance board created by article 29 of chapter 66, as that article existed
on January 1, 1970, shall remain in full force and effect until counter-
manded or modified by the variance board created by this article.
66-31-25. LOCAL GOVERNMENT—AUTHORITY—PENALTY.—(1) Home rule
cities, cities, towns, counties, and cities and counties are hereby author-
ized to enact local air pollution laws. Every such law shall provide for
variances, hearings, judicial review, and injunctions consistent with sec-
tions 66-31-15 to 66-31-18, and shall include emission control regulations
which are at least the same as or may be more restrictive than the emission
control regulations adopted pursuant to this article; except that, nothing
contained in this article shall prohibit any such local law from controlling
any air contamination or air contamination source which is not subject to
control under the provisions of this article; and except that, no variance
or permit issued under any local air pollution law with respect to any facil-
ity, activity, or process, shall ever be construed to relieve any holder
thereof from the duty to maintain such facility, activity, or process in
compliance with the emission control regulations adopted pursuant to this
article, nor to relieve the division from its duty to enforce such emission
control regulations with respect to such facility, activity, or process.
(2) All local air pollution laws and orders issued pursuant thereto
in existence at the time this article takes effect are hereby validated as
though adopted pursuant to the authority of subsection (1) of this section;
but if any such local law or order fails to meet the requirements of this
article, the governing body under whose authority such law or order was pro-
mulgated shall have until July 1, 1971, to amend, modify, or repeal the same
so that it will meet the requirements of this article, but if not so amended,
modified, or repealed, the same shall be superseded by this article.
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Chap. 66, Art. 31
(3) To the extent a local air pollution law adopted by a county is
more restrictive than such a law adopted by any city or town within such
county, the county law shall apply in lieu of the city or town law to the
extent of the inconsistency.
(4) Application, operation, and enforcement of valid local air pol-
lution laws shall be completely independent of but may be concurrent with
the application, operation, and enforcement of this article. The appoint-
ment of an air pollution control authority by the division shall in no way
affect the duties and responsibilities given the same person or agency under
a local air pollution law, and the appointment of an air pollution control
authority by a local governmental unit shall in no way affect the duties and
responsibilities given the same person or agency by the division.
(5) Any local governmental authority enforcing air pollution control
regulations which shall issue any enforcement order or grant any variance
shall, at the time of such issuance or granting, transmit to the commission
a copy of such order or variance.
(6) In order to assure coordination of efforts to control and abate
air pollution, at least semiannually the commission and each air pollution
control authority created by a local air pollution law shall confer and re-
view each other's records concerning the area subject to such local law and
coordinate their respective plans and programs for such area.
(7) No local air pollution control authority shall institute any
system or program that conflicts with, or is in any way inconsistent with,
air pollution emergency plans promulgated by the governor pursuant to section
66-31-11 (2).
(8) Subject to such variances as may be issued pursuant to a local
air pollution law, any person who shall violate any emission control regula-
tion specified in any local air pollution law, within the jurisdiction of
the local government unit enacting the same, shall be subject to a civil
penalty of not more than three hundred dollars. Each day during which such
a violation occurs shall be deemed a separate offense.
66-31-26. DISPOSITION OF FINES AND PENALTIES.—All receipts from
penalties or fines collected under the provisions of sections 66-31-19 and
66-31-20 shall be credited to the general fund of the state.
*66-31-27. MOTOR VEHICLE EMISSIONS CONTROL PROGRAM.—(1) The com-
mission shall have the authority to adopt regulations concerning high alti-
tude tuning specifications to control motor vehicle emissions in this state.
(2) The departments of revenue and health shall develop joint pro-
grams where appropriate for the control of motor vehicle emissions. Though
the departments of health and revenue shall confer and cooperate in all
aspects of the motor vehicle emission control program, the primary respon-
sibility of the commission is the adoption of rules and regulations, and
the primary responsibility of the department of revenue is the enforcement
of those rules and regulations as delegated pursuant to 66-31-10 (2) (g).
(3) Not later than December 1, 1973, the departments of health and
revenue are directed to complete certain pilot and testing programs and
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Chap. 66, Art. 31
studies and make joint recommendations to the governor and to the general
assembly.
(4) (a) The department of health shall develop a pilot program for
the purpose of testing a representative sample of motor vehicles with vari-
ous vehicle emission control alternatives which may include emission testing
and maintenance, air pollution control tuneup, and vehicle modification al-
ternatives as determined by the commission.
(b) Based upon the results of the pilot program, the commission
shall develop recommendations for implementing programs of emission testing
or mandatory maintenance, or both; air pollution control tuneups; and vehi-
cle modifications, including altitude modifications and retrofit control
systems, for the control of motor vehicle emissions. Such recommendations
shall include information on the costs and air pollution control effective-
ness of alternate control measures and legislative and regulatory measures
necessary to implement an effective program. Any program recommended shall
be based upon establishing statewide minimum standards and shall include
more stringent standards for motor vehicles registered in air quality con-
trol basins defined by the commission.
*66-31-28. TRAINING PROGRAMS AND STUDIES—EMISSION CONTROLS.—(1)
No later than July 1, 1974, state-employed investigators shall complete a
training course and pass qualification tests as developed and approved by
the commission, after conferring with the department of revenue, as re-
lated to the orientation and basic maintenance procedures on air pollution
control systems installed by manufacturers. The commission may waive the
requirement for completion of such a training course under such circum-
stances as the commission deems appropriate. Only inspectors passing said
qualification tests shall perform emission inspections. The commission
may require, pursuant to section 13-5-113, C.R.S. 1963, that inspection
stations have on hand by July 1, 1974 any equipment necessary to complete
emission inspections as provided for in this section.
(2) The departments of health and revenue shall jointly recommend,
by December 1, 1973, additional training programs which may be necessary to
help implement motor vehicle emission control measures.
(3) No later than February 1, 1974, pilot training programs con-
sistent with the provisions of this section shall have been completed to
determine program costs and effectiveness in meeting the training require-
ments of this section.
(4) (a) The departments of health and revenue jointly shall recom-
mend a program to insure consumer protection in the implementation of the
motor vehicle emission control program. The departments shall make recom-
mendations relating to penalties and enforcement procedures that will not
only be effective in the control of emissions, but also allow persons in
violation reasonable time to comply with any requirements established.
(b) The commission shall consider, in promulgating rules and regu-
lations, the adverse effect of said rules and regulations upon gasoline
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Chap. 66, Art. 31
mileage, performance, or other factors as to any make, model, or class of
motor vehicles as well as the public benefit in reducing air pollution.
The commission may make recommendations to exempt from regulations any make
or model of motor vehicle for which either gas mileage, performance, or
other factor would be adversely affected in a significant manner by said
control measures.
(c) Any make or model of motor vehicle, fueled by natural gas, or
powered by electrical energy, or powered by a Rankin cycle engine, shall be
exempt from the provisions of section 66-31-27.
**66-31-29. EMISSION DATA—PUBLIC AVAILABILITY.—Notwithstanding any
other provisions of this article, or any other law to the contrary, all
emission data received or obtained by the commission or the variance board
shall be available to the public to the extent required by the federal
"Clean Air Act of 1970" as the same may be amended from time to time.
For reference purposes, the following sections are included:
Chapter 13, Section 5, Operation of Vehicles
** 13-5-113 Periodical Inspections Required
** 13-5-160 Air Pollution Control Devices - Tampering - Operation
of Vehicle
Chapter 40, Colorado Criminal Code
** 40-13-110 Air Pollution Violations
40-1-107 Petty Offenses Classified
40-8-503 Perjury in the Second Degree
13-5-113 (2), Colorado Revised Statutes 1963 (1969 Supp.), is
repealed and reenacted, with amendments, to read:
13-5-113. PERIODICAL INSPECTIONS REQUIRED.—(2) (a) The inspection
required by this section shall include an inspection of the lights, brakes,
steering assemblies, window and windshield glass, exhaust system, mufflers,
fenders, and any other equipment or accessory, the proper functioning of
which is found by the department of revenue to be necessary to the safe
operation of the vehicle.
(b) Except as to devices found by the air pollution control com-
mission to be ineffective pursuant to section 66-31-6 (4), C.R.S. 1963, the
inspection required by this section shall include the crank case ventilat-
ing system on gasoline propelled automobiles and trucks manufactured in the
United States after July 1, 1965, and on all other motor vehicles equipped
with the same, connection of air pollution control devices installed by the
manufacturer of any automobile of a model year of 1968 or later, and any
other inspection prescribed pursuant to paragraph (c) of this subsection (2),
(c) Effective July 1, 1973, as part of the inspection required by
this section, the air pollution control commission is authorized to adopt
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Air Pollution Control - Page B-27
Chap. 66, Art. 31
regulations pursuant to sections 66-31-8 and 66-31-9, C.R.S. 1963, for the
proper connection and operation of air pollution control devices installed
by the manufacturer in any motor vehicle for the purpose of controlling
vehicle emissions; the air pollution control commission may further adopt
rules and regulations governing other air pollution control devices; which
rules and regulations shall be enforced by the department of revenue. Such
rules and regulations pertaining to inspections for the proper operation of
all pollution control devices shall not become effective before July 1, 1974,
and prior to that time, the air pollution control commission shall recommend
to the general assembly an appropriate fee therefor.
(d) Effective with the sale of inspection certificates to be issued
after July 1, 1973, there shall be a fee of fifteen cents in addition to
that prescribed by section 13-5-114 (5), which fee shall be paid to the
department of revenue along with the fee paid under section 13-5-114 (4),
and shall be credited to the special account prescribed by section 13-5-114
(4) and may be used, subject to appropriation by the general assembly, to
cover the cost of the motor vehicle emissions control activities of the
departments of health and revenue.
13-5-160. AUTOMOBILE AIR POLLUTION CONTROL DEVICES—TAMPERING—
OPERATION OF VEHICLE.—(1) No person shall knowingly disconnect, deactivate,
or otherwise render inoperable any air pollution control device which has
been installed by the manufacturer of any automobile of a model year of 1968
or later.
(2) No person shall operate on any highway in this state any auto-
mobile described in subsection (1) of this section knowing that any air
pollution control device installed on such automobile has been disconnected,
deactivated, or otherwise rendered inoperable.
(3) Any person who violates any provision of this section shall be
guilty of a misdemeanor, and upon conviction thereof shall be punished by a
fine of not less than ten dollars nor more than one hundred dollars, or by
imprisonment in the county jail for not more than ten days, or by both such
fine and imprisonment.
(4) The air pollution control commission may adopt rules and regu-
lations pursuant to sections 66-31-8 and 66-31-9, C.R.S. 1963, which permit
or allow for the alteration, modification, or disconnection of manufacturer-
installed air pollution control systems or manufacturer tuning specifica-
tions on motor vehicles for the purpose of controlling vehicle emissions.
Nothing in this section shall prohibit the alteration or the conversion of
a motor vehicle to operate on a gaseous fuel, providing that the resultant
emissions are at levels complying with state and federal standards for that
model year of motor vehicle.
40-1-107. PETTY OFFENSES CLASSIFIED, PENALTIES.—A violation of a
statute of this state is a "petty offense" if specifically classified as a
class 1 or class 2 petty offense. The penalty for commission of a class 1
petty offense is a fine of not more than five hundred dollars or imprison-
ment for not more than six months other than in the state penitentiary, or
both. The penalty for commission of a class 2 petty offense is a fine
specified in the section defining the offense. The penalty assessment
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Air Pollution Control - Page B-28
Chap. 66, Art. 31
procedure of section 40-1-305 is available for the payment of fines in
class 2 petty offense cases.
Editor's note: Section 40-1-305 has been repealed.
40-13-110. AIR POLLUTION VIOLATIONS.—(1) (a) (i) It is a class 2
petty offense as specified in section 40-1-107 for any person to cause air
pollution by any of the means:
(ii) To cause or permit, in any air pollution control region desig-
nated by the commission in which more than thirty times per year the carbon
monoxide level exceeds nine parts per million averaged over an eight hour
period, the emission into the atmosphere from any motor vehicle powered by
gasoline, or other fuel except diesel, of any visible air contaminant
(except water vapor) for a period greater than five consecutive seconds;
except that no two-cycle gasoline-powered motor vehicle shall emit into
the atmosphere any air contaminant (except water vapor) of a shade or den-
sity equal to or greater than twenty percent opacity for a period greater
than ten consecutive seconds;
(iii) To cause or permit the emission into the atmosphere from any
diesel-powered motor vehicle operating not more than at an altitude of eight
thousand feet above mean sea level any air contaminant (except water vapor)
of a shade or density equal to or greater than thirty percent opacity for
a period greater than ten consecutive seconds, other than as a result of a
cold engine start-up;
(iv) To cause or permit the emission into the atmosphere from any
diesel-powered motor vehicle operating at more than eight thousand feet
above mean sea level any air contaminant (except water vapor) of a shade
or density equal to or greater than forty percent opacity for a period
greater than ten consecutive seconds, other than as a result of a cold
engine start-up;
(b) Opacity is defined as the degree to which an air contaminant
emission obscures the view of an observer, expressed in percentage of the
obscuration or in the degree (percent) to which transmittance of light is
reduced by an air contaminant emission.
(2) (a) The air pollution control commission shall establish train-
ing requirements for peace officers charged with the enforcement of the pro-
visions of subsection (1) of this section.
(b) In addition to the enforcement of the provisions of subsection
(1) of this section by peace officers, the air pollution enforcement offi-
cers of the department of health, including designated air pollution agents
of the department, shall enforce the provisions of this section and, for
such purposes only, shall have the powers of peace officers.
(3) (a) Effective January 1, 1974, the offense of causing air pol-
lution as defined in this section is punishable by a fine of twenty-five
dollars. Penalty assessment procedures provided in section 39-2-201, C.R.S.
1963, shall be utilized in the enforcement of this section and shall be
subject to the additional provisions of this subsection (3). Prior to such
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Air Pollution Control - Page B-29
Chap. 66, Art. 31
date, peace officers may issue notices warning of conditions which appear
to violate the provisions of this section.
(b) Copies of every notice issued on or after January 1, 1974,
shall be forwarded by the issuing officer to the Colorado department of
revenue, motor vehicle division, and to the clerk of the county court of
the appropriate county. The notice, in the form of a summons and complaint,
shall provide that the person charged may pay the specified fine in person
or by mail at the office of the Colorado department of revenue, motor ve-
hicle division, Denver, Colorado, within seven days after the date of
issuance of the notice, shall specify a date not less than thirty nor more
than sixty days after its date of issuance for appearance to answer the
charge if the fine is not paid, and shall further give notice that, in the
alternative, the person may have the charge dismissed by complying with
the provisions of paragraph (c) of this subsection (3).
(c) Upon presentation to the court, by mail or in person, of an
affidavit by the owner of the vehicle described in the penalty assessment
notice that the vehicle has been disposed of in such manner that it will
no longer be operated on the highways, together with the registration
card and number plates of such vehicle, the complaint shall be dismissed.
Likewise, upon presentation, by mail or in person, of an affidavit of the
owner that such automobile has been repaired prior to the date set for
appearance upon the charge and that it is not in violation of the provi-
sions of this section when in normal operation, the complaint shall be
dismissed. Any such affidavit is subject to the penalties of perjury in
the second degree if made in violation of the provisions of section
40-8-503.
40-8-503. PERJURY IN THE SECOND DEGREE. A person commits perjury
in the second degree if, other than in an official proceeding, with an
intent to mislead a public servant in the performance of his duty, he
makes a materially false statement, which he does not believe to be true,
under an oath required or authorized by law. Perjury in the second degree
is a class 1 misdemeanor.
APPROPRIATION.—(1) In addition to any other appropri-
ation, there is hereby appropriated out of any moneys in the state treasury
not otherwise appropriated, to the department of health, for the fiscal
year beginning July 1, 1973, the sum of three hundred eighty thousand nine
hundred fifty-one dollars ($380,951), or so much thereof as may be neces-
sary, for the motor vehicle emissions control program authorized by this
act. These funds shall be used to develop within the department of health
a motor vehicle emissions control section, to develop a pilot program for
the testing of vehicle emission control alternates, to develop training
programs, and to develop other measures and recommendations in line with
the intent of this act.
(2) In addition to any other appropriation, there is hereby ap-
propriated out of any moneys in the special account within the highway users
tax fund prescribed by section 13-5-114 (4), C.R.S. 1963, not otherwise
appropriated, to the department of revenue, for the fiscal year beginning
July 1, 1973, the sum of twenty-five thousand fifty-nine dollars ($25,059),
or so much thereof as may be necessary, for the performance of its duties
in the implementation of this act.
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APPENDIX C
40 CFR 52, SUBPART G - COLORADO
C-l
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Subpart G—Colorado
§ 52.320 Identification of plan.
(a) Title of plan: "Air Quality Implementation Plan for State of Colorado".
(b) The plan was officially submitted on January 26, 1972.
(c) Supplemental information was Pollution Control Commission;
submitted on: (3) May 1, 1972, by the Colorado Air
(1) February 14, and March 20, 1972; Pollution Control revision, and
(2) May 1, 1972, by the Colorado Air (4) June 4, 1973, and July 16, 1973.
§ 52.321 Classification of regions.
The Colorado plan was evaluated on the basis of the following classifications:
Air quality
control region i
Pawnee Intrastate
Metropolitan
Denver
Intrastate
Comanche
Intrastate
San Isabel
Intrastate
San Luis
Intrastate
Four Corners
Interstate
Grand Kssa
Intrastate
Yairpa Intrastate
Partkulate
n-atter
I
I
III
I
III
IA
III
III
Sulfur
oxides
III
III
III
III
III
IA
III
III
''ollutant ]
HUrogcn
dioxide
III
III
III
III
III
III
III
III
Carbon
ironoxide
III
I
III
III
III
III
III
III
fhotochem'cdl
oxidants
(hydrocarbons)
III
I
III
III
III
III
III
III
[39 FR 16344, May 8, 1974]
§ 52.322 Extensions.
(a) The Administrator hereby extends for 18 months the statutory timetable for
submission of Colorado's plan for attainment and maintenance of the secondary
standards for paniculate matter in the Metropolitan Denver, San Isabel, and
Pawnee Intrastate Regions.
(b) The Administrator hereby extends monoxide and photochemical oxidants in
until May 31, 1977, the attainment date the Metropolitan Denver Intrastate Air
for the national standards for oarbon Quality Control Region.
§ 52.323 Approval status.
With the exceptions set forth in this subpart, the Administrator approves Colo-
rado's plan for the attainment and maintenance of the national standards.
§ 52.324 Legal authority.
(a) The requirements of § 51.11(a) (6) of this chapter are not met since the State
lacks the authority to require owners or operators of stationary sources to install,
maintain, and use emission monitoring devices and to make periodic reports to the
State on the nature and amounts of emissions from such stationary sources.
(b) Delegation of authority: Pursuant to section 114 of the Act, Colorado re-
quested a delegation of authority to enable it to require sources to install and main-
tain monitoring equipment and to report periodically on the nature and amount of
their emissions. The Administrator has determined that Colorado is qualified to
receive a delegation of the authority it requested. Accordingly, the Administrator
delegates to Colorado his authority under section 114(a)(l) (B) and (C) of the
Act, i.e., authority to require sources within the State of Colorado to install and
maintain monitoring equipment and to report periodically on the nature and
amount of their emissions.
C-2
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§ 52.32."> Attainment The requirements of § 51.14 of this
chapter are not met because the plan
does not provide for attainment and
maintenance of the national standards
for photochemical oxidants (hydrocar-
bons) and carbon monoxide in the Met-
ropolitan Denver Intrastate Air Quality
Control Region by May 31, 1977.
§ 52.329 Rules and regulations.
(a) The requirements of § 51.22 are
not met since regulations for the control
cf stationary hydrocarbon regulations
necessary for the attainment of the na-
tional standards for photochemical oxi-
dants have not been submitted or
adopted.
§ 52.330 Gasoline limitations.
(a) Definitions:
(1) "Distributor" means any person or
entity that transports or stores or causes
the transportation or storage of gasoline
between any refinery and any retail out-
let.
(2) "Retail outlet" means any estab-
lishment at which gasoline is sold or
offered for sale to the public, or intro-
duced into any vehicle.
(b) This section is applicable .within
the Metropohtan Denver Intrastate Air
Quality Control Region (hereafter re-
ferred to as the Region) to all distribu-
tors of gasoline to any retail outlet in the
Region, and to the owners and operators
of all retail outlets in the Region.
(c) If the Administrator determines,
on the basis of air quality monitoring
in the Region, that the national ambient
air quality standards for carbon monox-
ide and photochemical oxidants will not
be attained in the Region by May 31,
1977, the Administrator shall implement
a program, to be effective no later than
May 31, 1977, limiting the total gallonage
of gasoline delivered to retail outlets to
that amount which, when combusted, will
not result in such ambient air quality
standards being exceeded.
(d) All distributors to which this sec-
tion applies shall provide the Adminis-
trator with a detailed annual accounting
of the amount of gasoline delivered to
each retail outlet in the region for cal-
endar year 1976, and for each calendar
year during which the gasoline limita-
tion program Is in effect. The owner or
operator of each retail outlet to which
this section applies shall provide the Ad-
ministrator with a detailed accounting
of gasoline received from each distribu-
tor, the total amount of gasoline sold
during the year, and the amount of gaso-
line on hand at the beginning and end
of the year, for each year during which
the gasoline limitation program Is in
effect. All accountings required by this
section shall be provided no later than
90 days after the end of the applicable
year. The Administrator may require
any other reports that he may deem
necessary for the implementation of
this section.
C-3
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§ 52.331 Control of dry clrnniiiR solvent
evaporation.
(a) "Drycleanlng operation" means
that process by which an organic solvent,
as denned In 5 52.333(k), Is used In the
commercial cleaning of garments and
other fabric materials.
(b) This section is applicable In the
Metropolitan Denver Intrastate Air
Quality Control Region.
(c) No person shall operate a dry
cleaning operation using other than
perchloroethylene, 1,1,1-trlchloroethane,
or saturated halogenated hydrocarbons
unless toe uncontrolled organic emissions
from such operation are reduced at least
85 percent, except that dry cleaning op-
erations emitting less than 3 pounds per
hour and less than 15 pounds per day
of uncontrolled organic materials are
exempt from the requirements of this
section.
(d) If incineration is used as a control
technique, 90 percent or more of the
carbon In the organic compounds being
Incinerated must be oxidized to carbon
dioxide. Compliance with this require-
ment shall be in accordance with the
provisions of § 52.338.
(e) Any owner or operator of a source
subject to this section shall achieve com-
pliance with the requirements of para-
graph ic) of this section by discontinu-
ing the use of photochemically reactive
solvents as defined by 152333(1) no
later than January 31, 1974, or by con-
trolling emission as required by para-
graphs (c) and (d) of this section in
accordance with the requirements of
§52.338.
§ 52.332 Dcgreasing operations.
(a> "Degreasing" means the operation
of using an organic solvent as a surface
cleaning agent.
(b) This section is applicable hi the
Metropolitan Denver Intrastate Air
Quality Control Region.
(c) No person shall use for degreasing
any organic solvent other than 1,1,1-
trlchloroethane, perchloroethylene, or
saturated halogenated hydrocarbons
after January 31, 1974, unless the uncon-
trolled organic emissions from such op-
eration have been reduced at least 85 per-
cent overall.
(d) Degreasing operations emitting
less than 3 pounds per hour and less
than 15 pounds per day of uncontrolled
organic materials are exempt from the
requirement of this section.
(e) If incineration is used as a con-
trol technique, 90 percent or more of the
carbon in the organic compounds being
Incinerated must be oxidized to carbon
dioxide. Compliance with this paragraph
shall be in accordance with the provi-
sions of § 52.338.
(f) Any owner or operator of a sta-
tionary source subject to this section
shall achieve compliance with the re-
quirements of paragraph (c) of this sec-
tion by discontinuing the use of any
organic solvent other than 1,1,1-trlchlo-
roethane, percloroethylene, or saturated
halogenated hydrocarbons no later than
January 31, 1974, or by controlling emis-
sions as required by paragraphs (c) and
(e) of this section in accordance with
the requirements 01' } 52.338.
§ 52.333 Organic golvrnl \intgr.
(a) This section is applicable in the
Metropolitan Denver Intrastate Air
Quality Control Region. Compliance with
the requirements of paragraphs (b)
through (i) of this section shall be In
accordance with the provisions of
§ 52.338.
(b) No person shall discharge more
than 15 pounds of organic materials into
the atmosphere In any one day nor more
than 3 pounds in any one hour from any
article, machine, equipment or other con-
trivance In which any organic solvent or
any material containing organic solvent
comes into contact with flame or is
baked, heat-cured, or heat polymerized,
in the presence of oxygen, unless all
organic materials discharged from such
article, machine, equipment, or other
contrivance have been reduced by at
least 85 percent overall.
(c) No person shall discharge more
than 40 pounds of organic material into
the atmosphere in any one day or more
than 8 pounds in any one hour from any
article, machine, equipment, or other
contrivance used under conditions other
than described in paragraph (b) of this
section for employing, applying, evap-
orating, or drying any photochemically
reactive solvent, as denned in paragraph
(1) of this section,"or material contain-
ing such solvent, unless all organic mate-
rials discharged from such article, ma-
chine, equipment, or other contrivance
have been reduced by at least 85 percent
overall.
(d) Any series of articles, machines,
equipment, or other contrivances de-
signed for processing a continuously
moving sheet, web, strip, or wire which
is subjected to any combination of oper-
ations described in paragraphs (b) and
(c) of this section involving any photo-
chemically reactive solvent, as defined
in paragraph (1) of this section, or mate-
rial containing such solvent, shall be
subject to compliance with paragraph (c)
of this section. Where only non-photo-
chemically reactive solvents or mate-
rials containing only non-photochemi-
cally reactive solvents are employed or
applied, and where any portion or por-
tions of said series of articles, machines,
equipment, or other contrivances involves
operations described in paragraph (b)
of this section, said portions shall be
collectively subject to compliance with
paragraph >t>> of this section.
(e) Emissions of organic materials to
the atmosphere from the cleanup with
photochemically reactive solvent, as de-
nned in paragraph (11 of this section, of
any article, machine, equipment, or other
contrivance described in paragraphs (b),
(c), or (d) of this section shall be in-
cluded with the other emissions of or-
ganic materials from that article, ma-
chine, equipment, or other contrivance
for determining compliance with this
section.
(f) Emissions of organic materials
into the atmosphere as a result of con-
tinuous drying of products during the
first 12 hours after their removal from
any article, machine, equipment, or other
contrivance described in paragraphs (b),
(c), or (d) of this section shall be in-
cluded with other emissions of organic
materials from that article, machine,
equipment or other contrivance for de-
termining compliance with this section.
(g) Emissions of organic materials
Into the atmosphere required to be con-
trolled by paragraphs (b), (c), or ,
(c), (d), or (e) of this section, if:
(i) The organic solvent content of such
material does not exceed 20 percent by
volume of said material,
(ii) The volatile content is not photo-
chemically reactive as defined in para-
graph (1) of this section,
(iii) More than 50 percent by volume
of such volatile material is evaporated
before entering a chamber heated above
ambient application temperature, and
(iv) The organic solvent or any ma-
terial containing organic solvent does not
come into contact with flame.
C-4
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(6) The use of any material, In any
article, machine, equipment, or other
contrivance described In paragraphs (b),
(c), (d), or (e) of this section, If:
(!) The organic solvent content of such
material does not exceed 5 percent by
volume of said material,
(11) The volatile content is not photo-
chemically reactive as defined In para-
graph (1) of this section, and
(111) The organic solvent or any ma-
terial containing organic solvent does not
come Into contact with flame.
(k) For the purposes of this section,
organic solvents include diluents and
thinners and are defined as organic ma-
terials which are liquids at standard con-
ditions and which are used as dissolvers,
viscosity reducers, or cleaning agents.
(1) For the purposes of this section, a
photochemically reactive solvent is any
solvent with an aggregate of more than
20 percent of its total volume composed
of the chemical compounds classified
below or which exceeds any of the fol-
lowing individual percentage composition
limitations, referred to the total volume
of solvent:
(1) A combination of hydrocarbons,
alcohols, aldehydes, esters, ethers, or ke-
tones having an olefinic or cyclo-olefinic
type of unsaturation: 5 percent;
(2) A combination of aromatic com-
pounds with eight or more carbon atoms
to the molecule except ethylbenzene: 8
percent;
(3) A combination of ethylbenzene or
ketones having branched hydrocarbon
structures, trichloroethylene or toluene:
20 percent.
(m> Whenever any organic solvent or
any constituent of an organic solvent
may be classified from its chemical struc-
ture into more than one of the above
groups of organic compounds, it shall be
considered as a member of the most re-
active chemical group, that is, that group
having the least allowable percent of the
total volume of solvents.
(n) For the purpose of this section,
organic materials are defined as chemical
compounds of carbon excluding carbon
monoxide, carbon dioxide, carbonic acid,
metallic carbides, metallic carbonates,
and ammonium carbonate.
(o) This section shall be effective on
the date of its adoption for any article,
machine, equipment, or other contriv-
ance not then completed and put into
service. As for all other articles, ma-
chines, equipment, or other contrivances,
compliance shall be required in accord-
ance with § 52.338.
(p) A person shall not, after May 31,
1975, discharge into the atmosphere more
than 3,000 pounds of organic materials
in any one day nor more than 450 pounds
in any one hour from any article, ma-
chine, equipment, or other contrivance in
which any non-photochemically reactive
solvent or any material containing such
solvent is employed or applied, unless
said discharge has been reduced by at
least 85 percent. Emissions of organic
materials into the atmosphere resulting
from air or heated drying of products for
the first 12 hours after their removal from
any article, machine, equipment, or other
contrivance described In this section
shall be included in determining com-
pliance with this section. Emissions re-
sulting from baking, heat-curing, or
heat-polymerizing shall be excluded from
determination of compliance with this
section. Those portions of any series of
articles, machines, equipment, or other
contrivances designed for processing a
continuous web, .strip, or wire which emit
organic materials and using operations
described in this section shall be col-
lectively subject to compliance with this
section.
§ 52,334 Storage of petroleum products.
(a) This section is applicable In the
Metropolitan Denver Intrastate Air Qual-
ity Control Region. Compliance with the
requirements of paragraph (b) of this
section shall be in accordance with the
provisions of § 52 338.
(b) No person shall place, store or hold
in any stationary tank, reservoir, or
other container of more than 40.000 gal-
lons capacity any gasoline or any petro-
leum distillate having a vapor pressure
of 1.5 pounds per square inch absolute
fpsia) or greater under actual storage
conditions, unless such tank, reservoir or
other container is a pressure tank niain^
taming working pressures sufficient at all
times to prevent hydrocarbon vapor or
gas loss to the atmosphere, or is designed
and equipped with one of the following
vapor loss control devices, properly in-
stalled, in good working order, and in
operation:
(DA floating roof, consisting of a pon-
toon type or double deck type roof, rest-
ing on the surface of the liquid contents
and equipped with a closure seal, or seals,
to close the space between the roof edge
and tank wall. The control equipment
provided for in this paragraph shall not
be used if the gasoline or petroleum dis-
tillate has a vapor pressure of 110
pounds per square inch absolute or
greater under actual storage conditions.
AH tank gauging and sampling devices
shall be gas-tight except when gaug-
ing or sampling is taking place.
(2) A vapor recovery system, consist-
ing of a vapor gathering system capable
of collecting the hydrocarbon vapors and
gases discharged and a vapor disposal
syscem capable of processing such hydro-
carbon vapors and gases so as to prevent
their emission to the atmosphere, with
all tank gauging and sampling devices
gas-tight, except when gauging or sam-
pling is taking place.
(3) Other equipment of equal effi-
ciency, provided such equipment is ap-
proved by the Administrator.
§ 52.335 Organic liquid loading.
(a) "Loading- facility" means any ag-
gregation or combination of organic
liquid loading equipment which is both
possessed by one person and located so
that all the organic liquid loading out-
lets for such aggregation or combination
of loading equipment can be encom-
passed within any circle of 300 feet in
diameter.
(b) This section is applicable In the
Metropolitan Denver -Intrastate Air
Quality Control Region. Compliance with
the requirements of paragraphs (b)
through (d) of this section shall be in
accordance with 'he provisions of
5 52 338.
(c) No person shall load organic liquids
having a vapor pressure of 1 5 psi.a or
greater under actual loading conditions
into any tank truck, trailer, or railroad
tank car from any loading facility un-
less the loading facility is equipped with
a vapor collection and disposal system,
or its equivalent, approved by the Ad-
ministrator.
(d) Loading shall be accomplished in
such a manner that all displaced vapor
and air will be vented only to the vapor
collection system. Measures shall be
taken to prevent liquid drainage from the
loading device when it is not in use or to
accomplish complete drainage before the
loading device is disconnected.
(e) The vapor disposal portion of the
vapor collection and disposal system
shall consist of one of the following:
(1) An absorber system or condensa-
tion system which processes all vapors
and recovers at least 90 percent by
weight of the organic vapors and gases
from the equipment being controlled.
(2) A vapor handling system which
directs all vapors to a fuel gas system.
(3) Other equipment of equal efficiency
provided such equipment is approved by
the Administrator.
(f) This section shall apply only to the
loading of organic liquids having a vapor
pressure of 1.5 psia or greater under
actual loading conditions at a facility
from which at least 20,000 gallons of such
organic liquids are loaded in any one day.
§ ,)2.336 Gasoline transfer vapor con-
trol.
(a) "Gasoline" means any petroleum
distillate having a Reid vapor pressure
of 4 pounds or greater.
>b) Tl-is section is applicable in the
Metropoatan Denver Intrastate Air
Quality Control Region.
(c) No person shall transfer gasoline
from any delivery vessel into any station-
ary storage container with a capacity
greater than 250 gallons unless such con-
tainer is equipped with a submerged fill
pipe and unless the displaced vapois from
the storage container are processed by a
system that prevents release to the
atmosphere of no less than 90 peicent by
weight of organic compounds in said
vapors displaced from the stationarj con-
tainer location.
(1) The vapor recovery portion of the
system shall include one or moie of the
following:
(i) A vapor-tight return line from the
storage container to the delivery vessel
and a system that will ensure that the
vapor return line is connected befoie
gasoline can be transferred into the
container.
(ii> Refrigeration-condensation system
or equivalent designed to recover no less
than 90 percent by weight of the oiganlc
compounds in the displaced vapor.
(2) If a "vapor-tight vapor return"
system is used to meet the requirements
of this section, the system shall be so
constructed as to be readily added on
to retrofit with an adsorption system,
refrigeration-condensation syscem, or
equivalent vapor removal system, and so
constructed as to anticipate compliance
with § 52 337.
05
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(3) The vnpor-lnden delivery vessel
shall be subject to the following condi-
tions:
(1) The delivery vessel must be so de-
signed and maintained as to be vapor-
tight at all times.
(ii) The vupor-laden delivery vessel
may be refilled only at facilities
equipped with a vapor recovery system
or the equivalent, which can recover at
least 90 percent by weight of the organic
compounds m the vapors displaced from
the delivery vessel during refilling.
(iii) Gasoline storage compartments of
•1,000 gallons or less in gasoline delivery
vehicles presently in use on the promul-
gation date of this regulation will not be
required to be retrofitted \\ith a vapor
return system until January 1, 1977.
(d) The provisions of this paragraph
(c) shall not apply to the f piloting:
(1) Stationary containers having a ca-
pacity less than 550 gallons used exclu-
sively for the fueling of implements of
husbandry.
(2) Any container having a capacity
less than 2,000 gallons installed prior to
promulgation of this para-graph.
(3) Transfer made to storage tanks
equipped with floating roofs or their
equivalent.
(e) Compliance schedule:
(1) June 1, 1974. Submit to the
Administrator a final control plan, which
describes at a minimum the steps which
will be taken by the source to achieve
compliance with the provisions of para-
graph (c) of this section.
[39 FR 4880, February 8, 1974]
(2) November I, 1974. Negotiate and sign
all necessary contracts for emission control
systems, or issue orders for the purchase of
component parts to accomplish emission con-
trol.
[39 FR 4880, February 8, 19741
(3) Jcnuary I, 1975. Initiate on-site
construction or installation of emission con-
trol equipment.
[39 FR4880, February 8, 1974)
(4) February 1, 1976 Complete on-site
construction or installation of emission
control equipment.
(5) March -1, 1976 Assure final com-
pliance with the provisions of paragraph
(c) of this section.
(6) Any owner or operator of sources
subject to the compliance schedule in
this paragraph shall certify Co the Ad-
ministrator, within 5 days after the dead-
line for each increment of progress,
whether or not the required increment
of progress has been met
(f) Paragraph (e) of this section shall
not apply:
(1) To a source which is presently in
compliance with the provisions of para-
graph (cJ of this section and which has
certified such compliance to the Admin-
istrator by June 1,1974. Phe Administrator
may request whatever supporting information
he considers necessary for proper certification.
(39 PR 4880, February 8, 1974]
(2) To a source for which a compli-
ance schedule is adopted by the State
and approved by the Administrator.
(3) To a source whose owner or opera-
tor submits to the Administrator, by June i,
1974, a proposed alternative schedule. No
such schedule may provide for compliance
after March 1, 1976. If promulgated by the
Administrator, such schedule shall satisfy the
requirements of this paragraph for the af-
fected source.
[39 FR 4880, February 8, 1974)
(g) Nothing in this paragraph shall
preclude the Administrator from promul-
gating a separate schedule for any source
to which the application of the com-
pliance schedule in paragraph (e) of this
section fails to satisfy the requirements
of § 51.15 (b) and (c) of this chapter.
(h) Any gasoline dispensing facility
subject to this regulation which installs
a storage tank after the effective date of
this regulation shall comply with the re-
quirements of paragraph (c) of this sec-
tion by March 1, 1976. Any facility sub-
ject to this regulation which installs a
storage tank after March 1, 1976, shall
comply with the requirements of para-
graph (c) at the time of installation.
§ 52.337 Control of evaporative losses
from the filling of vehicular tanks.
(a) "Gasoline" means any petroleum
distillate having a Reid vapor pressure of
4 pounds or greater.
(b) This section is applicable In the
Metropolitan Denver Intrastate Air
Quality Control Region.
(c) A person shall not transfer gaso-
line to an automotive fuel tank from,
gasoline dispensing system unless the
transfer is made through a fill nozzle
designed to:
(1) Prevent discharge of hydrocarbon
vapors to the atmosphere from either the
vehicle filler neck or dispensing nozzle;
(2) Direct vapor displaced from the
automotive fuel tar.k to a system
wherein at least 90 percent by weight of
the organic compounds in displaced
vapors are recovered; and
(3) Prevent automotive fuel tank over-
fills or spillage on fill nozzle disconnect.
(d) The system referred to in para-
graph (c) of this section can consist of
a vapor-tight vapor return line from the
fill nozzle-filler neck interface to the dis-
pensing tank, to an adsorption, absorp-
tion, incineration, refrigeration-con-
densation system or equivalent.
(e) Components of the systems re-
quired by §52336(c) can be used for
compliance with paragraph (c) of this
section.
(f) If it is demonstrated to the satis-
faction of the Administrator that it is
impractical to comply with the provi-
sions of paragraph (c) of tills section as
a result of vehicle fill neck configuration,
location, or other design features, the
provisions • of this paragraph shall not
apply to such vehicles. However, in no
case shall such configuration exempt any
gasoline dispensing facility from install-
ing a system required by paragraph (c).
(g) Compliance schedule:
(1) January I, 1975. Submit to the
Administrator a final control plan.
which describes at a minimum the stepa
which will be taken by the source to
•chieve compliance with the provisions
of paragraph (c) of this section.
139 FR 4880, February 8, 1974; 39 FR
21049, June 18, 19741
(2) March I, 1975. Negotiate and sign
»U necessary contracts for emission con-
trol systems, or issue orders for the pur-
chase of component parts to accomplish
emission control.
139 PR 4880, February 8, 1974, 39 FR
21049, June 18, 1974]
(3) May I, 1975. Initiate on-site construc-
tion or installation of emission control equip-
ment.
[39 FR 21049, June 18, 1974]
(4) May 1,1077. Complete on-site con-
struction or installation of emission con-
trol equipment or process modification.
(5) May 31, 1977. Assure final compli-
•tnce with the provisions of paragraph
(c) of this section.
(6) Any owner or operator of sources
subject to the compliance schedule in
this paragraph shall certify to the Ad-
ministrator, within 5 days after the
deadline for each increment of progress,
whether or not the required increment of
progress has been met.
(h) Paragraph (g) of this section shall
not apply:
(1) To a source which is presently In
compliance with the provisions of para-
graph (c) of this section and which has
certified such compliance to the Admin-
istrator by January 1, 1975. The Ad
ministrator may request whatever sup-
porting information he considers neces-
sary for proper certification.
|39 FR 4880, February 8, 1974; 39 FR
21049, June 18, 1974]
(2) To a source for which a compli-
ance schedule is adopted by the State
and approved by the Administrator.
(3) 'To a source whose owner or op-
erator submits to the Administrator, by
June 1, 1974, a proposed alternative sched-
ule. No such schedule may provide for com-
pliance after Mcy 31, 1977. If promulgated
by the Administrator, such schedule shall
satisfy the requirements of this paragraph for
Ihe affected source.
[39 FR 4880, February 8, 1974]
(i) Nothing in this paragraph shall
preclude the Administrator from pro-
mulgating a separate schedule for any
source to which the application of the
compliance schedule in paragraph (g)
of this section fails to satisfy the re-
quirements of § 51.15 (b) and (c) of this
chapter.
(j) Any gasoline dispensing facility
subject to this regulation which installs
s gasoline dispensing system after the
effective date of this regulation shall
comply with the requirements of para-
graph (c) of this section by May 31,
1977. Any facility subject to this regula-
tion which installs a gasoline dispensing
system after May 31, 1977, shall comply
with the requirements of paragraph (c)
of this section at the time of installation.
§ 52.338 FfJcml compliance icficflulcs.
(ft) Except as provided In paragrapn
(c) of Uiis section, the owner or operator
06
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of any stationary source subject to the
requirements of 53 52 331, 52 332, 52.333,
52.334, and 52 335 shall comply with the
compliance schedule la paragraph (b)
of this section,
(b) Compliance schedule:
(1) December 17, 1073. Submit to the
Administrator a final control plan, which
describes, at a minimum, the steps which
will be taken by the source to achieve
compliance with the sections cited in
paragraph (a) of this section.
(2) February 16, 1974. Negotiate and
sign all necessary contracts for emission
control systems or process modifications,
or issue orders for the purchase of com-
ponent parts to accomplish emission con-
trol or process modification.
(3) July 1, 1974. Initiate on-site con-
struction or installation of emission con-
trol equipment or process modification.
(4) May 1, 1975. Complete on-site
construction or installation of emission
control equipment or process modifica-
tion.
(5) May 31, 1975. Asiure final compli-
ance with the sections cited in paragraph
(a) of this section.
(6) Any owner or operator of station-
ary sources subject to the compliance
schedule in this paragraph shall certify
to the Administrator, within 5 days after
the deadline for each increment of prog-
ress, whether or not the required incre-
ment of progress has been met.
(c) Paragraph (b) of this section shall
not apply:
(1) To a source which is presently in
compliance with the regulations cited in
paragraph fa) of this section and which
has certified such compliance to the Ad-
ministrator by December 15, 1973. The
Administrator may request whatever
supporting information he considers
necessary for proper certification.
'2) To a source for which a compli-
ance schedule is adopted by the State and
appoved by the Administrator.
(3) To a source whose owner or oper-
ator submits to the Administrator, by
December 15, 1973, a proposed alterna-
tive schedule. No such schedule may pro-
vide for compliance after May 31, 1975. If
promulgated by the Administrator such
schedule shall satisfy the requirements
of this paragraph for the affected source.
(d) Nothing in this paragraph shall
preclude the Administrator from pro-
mulgating a separate schedule for any
source to which the application of the
compliance schedule in paragraph (b) of
this section fails to satisfy the require-
ments of § 51.15 (b) and (c) of this chap-
ter.
Istrator, shall monitor the transportation
control measures approved for the State's
implementation plan as follows:
(1) The actual per vehicle emission
reductions occurring as a result of:
(i) Inspection/maintenance;
(ii) Airbloed (pre-19G8 light-duty ve-
hicles) ; and
(lit) High altitude modification (1968-
1974 light-duty vehicles).
(2) 7Tie observed changes in vehicle
miles traveled (VMT) and average ve-
hicle speeds as a result of:
(1) Bus/carpool lanes;
(ii) Parking lot construction limita-
tion;
(ui) Limitation of on-street parking;
and
(iv) Mass transit improvements.
(c) No later than January 15, 1974, the
State shall submit to the Administrator a
detailed program demonstrating compli-
ance with paragraph (b) of this section
and in accordance with § 51.19rd) of this
chapter. The program description shall
include the following:
il) The agency or agencies responsible
for conducting, overseeing, and main-
taining the monitoring program.
(2) The administrative pzocess to be
used.
(3) A description of the methods to be
used to collect the vehicle emission re-
ductions, and changes in VMT and aver-
age vehicle speed, including a description
of any modeling techniques to be em-
ployed.
(4) The funding requirements, includ-
ing a signed statement from the Gover-
nor or the State Treasurer or their re-
spective designees Identifying the source
and amount of funds for the program.
(d) No later than February 15, 1974,
the Administrator will approve or disap-
prove the proposed monitoring program.
(e) All data collected as a result of the
monitoring program shall be submitted
to the Administrator on a semiannual
basis beginning August 15, 1974. The
data shall be submitted in a format sim-
ilar to that presented in Appendix M to
Part 51 of this chapter.
§ 52.340 Review of new sources and
modifications.
(a) The requirements of § 51.18 of
this chapter are not met because the
State failed to submit a plan for the
review of new or modified indirect
sources.
(b) Regulation for review of new or
modified indirect sources. The provisions
of § 5222(b) of this chapter are hereby
incorporated by reference and made a
part of the applicable implementation
plan for the State of Colorado.
§ 52.339 Monitoring transportation con-
trols.
(a) Tliis section is applicable to the
Metropolitan Denver Intrastate Region.
(b) The State of Colorado, or a desig-
nated agency approved by the Admin-
C-7
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APPENDIX D
HOUSE BILL 1041
D-l
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1974
HOUSE BILL NO. 1041. BY REPRESENTATIVES Dittemore, Buechner,
Herzberger, Miller, Pettie, Eaker, Eckelberry, Friedman,
Gustafson, Hamlin, Koster, O'Brian, Ross, Sack, Sonnenberg, and
Tenpest; also SENATORS Allshouse, Darby, Johnson; Plock, H.
Brown, DeBerard, L. Fowler, Gamsey, Jackson, Klein, McCormick,
Schieffelin, Stockton, and Strickland.
CONCERNING LAND USE, AND PROVIDING FOR IDENTIFICATION,
DESIGNATION, AND ADMINISTRATION OF AREAS AND ACTIVITIES OF
STATE INTEREST, AND ASSIGNING ADDITIONAL DUTIES TO THE
COLORADO LAND USE COMMISSION AND THE DEPARTMENT OF LOCAL
AFFAIRS, AND MAKING APPROPRIATIONS TIEREFOR.
Be rt enacted by_ the General Assembly p_f the State of Colorado:
SECTION 1. Chapter 106, Colorado Revised Statutes 1963, as
amended, is amended BY THE ADDITION OF A NEW ARTICLE to read:
ARTICLE 7
Areas and Activities of State Interest
PART 1
GENERAL PROVISIONS
106-7-101. Legislative declaration. (1) In addition to the
legislative declaration contained insection 106-4-1 (1), the
general assembly further finds and declares that:
(a) The protection of the utility, value, and future of all
lands within the state, including the public domain as well as
privately owned land, is a matter of the public interest;
Capital letters indicate new material added to existing statutes;
dashes through words indicate deletions from existing statutes and
such material not part of act.
D-2
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(b) Adequate information OH land use and systematic methods
of definition, classification, aj>d utilization thereof are either
lacking or not readily available 10 land use decision makers;
(c) It is the intent of the general assembly that land use,
land use planning, and quality oc development are matters in
which the state has responsibility for the health, welfare, and
safety of the people of the state and for the protection of the
environment of the state.
(2) It is the purpose of this article that:
(a) The general assent)ly shall describe areas which may be
of state interest and activities which may be of state interest
and establish criteria for the administration of such areas and
activities;
(b) Local governments shall be encouraged to designate areas
and activities of state interest and, after such designation,
shall administer such areas and activities of state interest and
promulgate guidelines for the administration thereof; and
(c) Appropriate state agencies shall assist local
governments to identify, designate, and adopt guidelines for
administration of matters of state interest.
106-7-102. General definitions. As used in this article,
unless the context otherwise requires:
(1) "Development" means any construction or activity which
changes the basic character or the use of the land on which the
construction or activity occurs.
(2) "Local government" means a municipality or county.
(3) "Local permit authority" means the governing body of a
local government with which an application for development in an
area of state interest or for conduct of an activity of state
interest must be filed or the designee thereof.
(4) "Matter of state interest" means an area of state
interest or an activity of state interest or both.
(5) "Municipality" means a home rule or statutory city,
town, or city and county or a territorial charter city.
(6) "Person" means any individual, partnership, corporation,
association, company, or other public or corporate body,
including the federal government, and includes any political
subdivision, agency, instrumentality, or corporation of the
state.
106-7-103. Definitions pertaining to natural hazards. As
D-3
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used in this article, unless the context otherwise requires:
(1) "Aspect" ir-eans the cardinal direction the land surface
faces, characterized by north-facing slopes generally having
heavier vegetation cover.
(2) "Avalanche" means a mass of snow or ice and other
material which may become incorporated therein as such mass moves
rapidly down a mountain slope.
(3) "Corrosive soil" means soil which contains soluble salts
which may produce serious detrimental effects in concrete, metal,
or other substances that are in contact with such soil.
(4) "Debris-fan .floodplain" means a floodplain which is
located at the mouth of a mountain valley tributary stream as
such stream enters the valley floor.
(5) "Dry wash channel and dry wash floodplain" means a small
watershed with a very high percentage of runoff after torrential
rainfall.
(6) "Expansive soil and rock" means soil and rock which
contains clay and which expands to a significant degree upon
wetting and shrinks upon drying.
(7) "Floodplair:" means an area adjacent to a stream, which
area is subject to flooding as the result of the occurrence of an
intermediate regional flood and which area thus is so adverse to
past, current, or foreseeable construction or land use as to
constitute a significant hazard to public health and safety or to
property. The tern includes but is not limited to:
(a) Mainstream floodplains;
(b) Debris-fan floodplains; and
(c) Dry wash channels and dry wash floodplains.
(8) "Geologic hazard" means a geologic phenomenon which is
so adverse to past, current, or foreseeable construction or land
use as to constitute a significant hazard to public health and
safety or to property. The term includes but is not limited to:
(a) Avalanches, landslides, rock falls, mudflows, and
unstable or potentially unstable slopes;
(b) Seismic effects;
(c) Radioactivity; and
(d) Ground subsidence.
D-4
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(9) "Geologic hazard area" me:uis an area which contains or
is directly affected by a geologic hazard.
(10) "Ground subsidence" means a process characterized by
the downward displacement of surface material caused by natural
phenomena such as removal of underground fluids, natural
consolidation, or dissolution of underground minerals or by
man-made phenomena such as underground mining.
(11) "Mainstream floodplain" means an area adjacent to a
perennial stream that is subject to periodic flooding.
(12) "F'fudflow" neans the downward movement of mud in a
mountain watershed because of peculiar characteristics of
extremely high sediment yield and occasional high runoff.
(13) "Natural hazard" means a geologic hazard, a wildfire
hazard, or a flood.
(14) "Natural, hazard area" means an area containing or
directly affected by a natural hazard.
(15) "Radioactivity" means a condition related to various
types of radiation emitted by natural radioactive minerals that
occur in natural deposits of rock, soil, and water.
(16) "Seismic effects" means direct and indirect effects
caused by an earthquake or an underground nuclear detonation.
(17) "Siltation" means a process which results in an
excessive rate of removal of soil and rock materials from one
location and rapid deposit thereof in adjacent areas.
(18) "Slope" means the gradient of the ground surface which
is definable by degree or percent.
(19) "Unstable or potentially unstable slope" neans an area
susceptible to a landslide, a mudflow, a rock fall, or
accelerated creep of slope-forming materials.
(20) "Wildfire behavior" means the predictable action of a
wildfire under given conditions of slope, aspect, and weather.
(21) "Wildfire hazard" means a wildfire phenomenon which is
so adverse to past, current, or foreseeable construction or land
use as to constitute a significant hazard to public health and
safety or to property. The term includes but is not limited to:
(a) Slope and aspect;
(b) Wildfire behavior characteristics; and
(c) Existing vegetation types.
D-5
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(22) "Wildfire hazard area" means an area containing or
directly affected by a wildfire hazard,
106-7-104. Pqfin itions pertaining to other areas and
activities of state" ytercst. As "used in this article, unless
the context otherwise "requires":"
(1) "Airport" means any municipal or county airport or
airport under the jurisdiction of an airport authority.
(2) "Area around a key facility" means an area immediately
and directly affected by a key facility.
(3) "Arterial highway" means any limited-access highway
which is part of the federal-aid interstate system or any
limited-access highway constructed under the supervision of the
state department of highways.
(4) "Collector highway" means a major thoroughfare serving
as a corridor or link between municipalities, unincorporated
population centers or recreation areas, or industrial centers and
constructed under guidelines and standards established by, or
under the supervision of, the state department of highways.
Collector highway does not include a city street or local service
road or a county ro?-d designed for local service and constructed
under the supervision o£ local government.
(5) "Domestic water and sewage treatment system" means a
wastewater treatTnent plant, water treatment plant, or water
supply system, as defined in section 66-38-2 (6), (7), and (8),
C.R.S. 1963, srol ar>y system of pipes, structures, and facilities
through which wastewatnr is collected for treatment.
(6) "Historical or archaeological resources of statewide
importance" mear»s resources which have been officially included
in the national register of historic places, designated by
statute, or included in ?»n established list of places compiled by
the state historical society.
(7) "Key facilities" ineans:
(a) Airports;
(b) Major facilities of a public utility;
(c) Interchanges involving arterial highways;
(d) Rapid or mass transit terminals, stations, and fixed
guideways.
(8) '"Major facilities of a public utility" means:
(a) Central office buildings of telephone utilities;
D-6
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CD) Transmission lines, powr plants, and siibstations o£
electrical utilities; and
(c) Pipelines and storage areas of utilities providing
natural gas or other petroleum derivatives.
(9) "Mass transit" means a coordinated system of transit
modes providing transportation for use by the general public.
(10) "Mineral" means an inanimate constituent of the earth,
in either solid, liquid, or gaseous state which, when extracted
from the earth, is usable in its natural form or is capable of
conversion into usable form as a metal, a metallic compound, a
chemical, an energy source, a raw material for manufacturing, or
construction material. This definition does not include surface
or ground water subject to appropriation for domestic,
agricultural, or industrial purposes, nor does it include
geothermal resources.
(11) "Mineral resource area" means an area in which
minerals are located in sufficient concentration in veins,
deposits, bodies, bads, seams, fields, pools, or otherwise, as to
be capable of economic recovery. The term includes but is not
limited to any area in which there has been significant mining
activity in the past, there is significant mining activity in the
present, mining development is planned or in progress, or mineral
rights are held by mineral patent or valid mining claim with the
intention of mining.
(12) "Natural resources of statewide importance" is limited
to shorelands of major publicly-owned reservoirs and significant
wildlife habitats in which the wildlife species, as identified by
the division of wildlife of the department of natural resources,
in a proposed area could be endangered.
(13) "New communities" means the major revitalization of
existing municipalities or the establishment of urbanized growth
centers in unincorporated areas.
(14) "Rapid transit" means the element of a mass transit
system involving a mechanical conveyance on an exclusive lane or
guideway constructed solely for that purpose.
106-7-105. Effect of article - public utilities. (1) With
regard to publicutilities,nothingin this article shall be
construed as enhancing or diminishing the power and authority of
municipalities, counties, or the public utilities commission.
Any order, rule, or directive issued by any governmental agency
pursuant to this article shall not be inconsistent with or in
contravention of any decision, oixler, or finding of the public
utilities commission with respect to public convenience and
necessity. The public utilities commission and public utilities
shall take into consideration and, when feasible, foster
D-7
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compliance with adopted land use master plans of local
governments, regions, and the state.
(2) Nothing in this article shall be construed as enhancing
or diminishing the rights and procedures with respect to the
power of a public utility to acquire property and rights-of-way
by eminent domain to serve public need in the most economical and
expedient manner.
106-7-106. Effect of article - rights of property owners -
water rights. (1)Nothing in this articleshall be construed
as:
(a) Enhancing or diminishing the rights of owners of
property as provided by the state constitution or the
constitution of the United States;
(b) Modifying or amending existing laws or court decrees
with respect to the determination and administration of water
rights.
106-7-107. Effect, of article - developments in areas of
state interest andactivities ofstateinterest meeting certain
conditions^ [IJ 'This article shall not apply to any development
in an area of state interest or any activity of state interest
which meets any one of the following conditions as of the
effective date of this article:
(a) The development or activity is covered by a current
building permit issued"by the appropriate local government; or
(b) The development or activity has been approved by the
electorate; or
(c) The development or activity is to be on land:
(I) Which has been conditionally or finally approved by the
appropriate local government for planned unit development or for
a use substantially the same as planned unit development; or
(II) Which has been zoned by the appropriate local
government for the use contemplated by such development or
activity; or
(III) With respect to which a development plan has been
conditionally or finally approved by the appropriate governmental
authority.
106-7-108. Effect of article - state agency or commission
responses. (1) %ienevcr any person desiring to carry out
development as defined in section 106-7-102 (1) is required to
obtain a permit, to be issued by any state agency or commission
for the purpose of authorizing or allowing such development,
D-8
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pursuant to this or any other statute or regulation promulgated
thereunder, such agency shall establish a reasonable time period,
which shall not exceed sixty days following receipt of such
permit application, within which such agency must respond in
writing to the applicant, granting or denying said permit or
specifying oil reasonable additional information necessary for
the agency or commission to respond. If additional information
is required, said agency or commission shall set a reasonable
time period for response following the receipt of such
information.
(2) Whenever a state agency or commission denies a permit,
the denial must specify:
(a) The regulations, guidelines, and criteria or standards
used in evaluating the application;
(b) The reasons for denial and the regulations, guidelines,
and criteria or standards the application fails to satisfy; and
(c) The action that the applicant would have to take to
satisfy the state agency's or commission's permit requirements.
(3) Whenever an application for a permit as provided under
this section contains a statement describing the proposed nature,
uses, and activities in conceptual terms for the development
intended to be accomplished and is not accompanied with all
additional information, including, without limitation,
engineering studies, detailed plans and specifications, zoning
approval, or where a hearing is required by the statutes,
regulations, rules, ordinances, or resolutions thereof prior to
the issuance of the requested permit, the agency or commission
shall, within the time provided in this section for response,
indicate its acceptance or denial of the permit on the basis of
the concept expressed in the statement of the proposed uses and
activities contained in the application. Such conceptual
approval shall be made subject to the applicant filing and
completing all prerequisite detailed additional information in
accordance with the usual filing requirements of the agency or
commission within a reasonable period of time.
(4) All agencies or commissions authorized or required to
issue permits for development shall adopt rules and regulations,
or amend existing rules and regulations, so as to require that
such agency or commission respond in the time and manner required
in this section.
(5) Nothing in this section shall shorten the time allowed
for responses provided by federal statute dealing with, or having
a bearing on, the subject of any such application for permit.
((>) The provisions of this section shall not apply to
applications approved, denied, or processed by a unit of local
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government.
PART 2
AREAS AND ACTIVITIES DESCRIBED -
CRITERIA FOR ADMINISTRATION
106-7-201. Areas of state interest - as determined by local
governments. (1)Subject to the procedures set forth in part3"
o?thisarticle, a local government may designate certain areas
of state interest from among the following:
(a) Mineral resource areas;
(b) Natural hazard areas;
(c) Areas containing, or having a significant impact upon,
historical, natural, or archaeological resources of statewide
importance; and
(d) Areas around key facilities in which development may
have a material effect upon the facility or the surrounding
community.
106-7-202. Criteria for administration of areas of state
interest. (1) (a) Mineral resource areas designated as areas of
state interest shall be protected and administered in such a
manner as to permit the extraction and exploration of minerals
therefrom, unless extraction and exploration would cause
significant danger to public health and safety. If the local
government having jurisdiction, after weighing sufficient
technical or other evidence, finds that the economic value of the
minerals present therein is less than the value of another
existing or requested use, such other use should be given
preference; however, other uses which would not interfere with
the extraction and exploration of minerals may be permitted in
sudi areas of state interest.
(b) Areas containing only sand, gravel, quarry aggregate,
or limestone used for construction purposes shall be administered
as provided by article 36 of chapter 92, C.R.S. 1963.
(c) The extraction and exploration of minerals from any
area shall be accomplished in a manner which causes the least
practicable environmental disturbance, and surface areas
disturbed thereby shall be reclaimed in accordance with the
provisions of article 13 or article 32 of chapter 92, C.R.S.
1963, whichever is applicable.
(d) Unless an activity of state interest has been
designated or identified or unless it includes part or all of
another area of state interest, an area of oil and gas or
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geothenoal resource development .c,iall not be designated as an
area of stare interest unless th<; state oil and gas conservation
commission identifies such area for designation.
(2) (a) Natural hazard aieas shall be administered as
follows:
(I) Floodplains shall be administered so as to minimize
significant hazards to public health and safety or to property.
The Colorado water conservation board shall promulgate a model
floodplain regulation no later than September 30, 1974. Open
space activities such as agriculture, recreation, and mineral
extraction shall be encouraged in the floodplains. Any
combination of these activities shall be conducted in a mutually
compatible manner. Building of structures in the floodplain
shall be designed in terms of the availability of flood
protection devices, proposed intensity of use, effects on the
acceleration of floodwateis, potential significant hazards to
public health and safety or to property, and other impact of such
development on downstream communities such as the creation of
obstructions during floods. Activities shall be discouraged
which, in time of flooding, would create significant hazards to
public health and safety or to property. Shallow wells, solid
waste disposal sites, and septic tanks and sewage disposal
systems shall be protected from inundation by floodwaters.
Unless an activity of state interest is to be conducted therein,
an area of corrosive soil, expansive soil and rock, or siltation
shall not be designated as an area of state interest unless the
Colorado soil conservation board, through the local soil
conservation district, identifies such area for designation.
(II) Wildfire hazard areas in which residential activity is
to take place shall be administered so as to minimize significant
hazards to public health and safety or to property. The Colorado
state forest service shall promulgate a model wildfire hazard
area control regulation no later than September 30, 1974. If
development is to take place„ roads shall be adequate for service
by fire trucks and other safety equipment. Firebreaks and other
means of reducing conditions conducive to fire shall be required
for wildfire hazard areas in which development is authorized.
(Ill) In geologic hazard areas all developments shall be
engineered and administered in a manner that will minimize
significant hazards to public health and safety or to property
due to a geologic hazaid. The Colorado geological survey shall
promulgate a model geologic hazard area control regulation no
later than September 30, 1974.
(b) After promulgation of guidelines for land use in
natural hazard areas by the Coloiado water conservation board,
the Colorado soil conservation board through the soil
conservation districts, the Colorado state forest service, and
the Colorado geological survey, natural hazard areas shall be
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administered by local government in a manner which is consistent
with the guidelines for land use in each of the natural hazard
areas.
(3) Areas containing, or having a significant impact upon,
historical, natural, or archaeological resources of statewide
importance, as determined by the state historical society, the
department of natural resources, and the appropriate local
government, shall be administered by the appropriate state agency
in conjunction with the appropriate local government in a manner
that will allow man to function in harmony with, rather than be
destructive to, these resources. Consideration is to be given to
the protection of those areas essential for wildlife habitat.
Development in areas containing historical, archaeological, or
natural resources shall be conducted in a manner which will
minimize damage to those resources for future use.
(4) The following criteria shall be applicable to areas
around key facilities:
(a) If the operation of a key facility may cause a danger
to public health and safety or to property, as determined by
local government, the area around the key facility shall be
designated and administered so as to minimize such danger; and
(b) Areas around key facilities shall be developed in a
manner that will discourage traffic congestion, incompatible
uses, and expansion of the demand for government services beyond
the reasonable capacity of the community or region to provide
such services as determined by local government. Compatibility
with nonmotorized traffic shall be encouraged. A development
that imposes burdens or deprivation on the communities of a
region cannot be justified on the basis of local benefit alone.
(5) In addition to the criteria described in subsection (4)
of this section, the following criteria shall be applicable to
areas around particular key facilities:
(a) Areas around airports shall be administered so as to:
(I) Encourage land use patterns for housing and other local
government needs that will separate uncontrollable noise sources
from residential and other noise-sensitive areas; and
(II) Avoid danger to public safety and health or to
property due to aircraft crashes.
(b) Areas around major facilities of a public utility shall
be administered so as to:
(I) Minimize disruption of the service provided by the
public utility; and
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(II) Preserve desirable existing comnunity patterns.
(c) Areas around interchanges involving arterial highways
shall be administered so as to:
(I) lincourage the smooth flow of motorized and nonmotorized
traffic;
(II) Foster the development of such areas in a manner
calculated to preserve the smooth flow of such traffic; and
(III) Preserve desirable existing conanunity patterns.
(d) Areas around rapid or mass transit terminals, stations,
or guideways shall be developed in conformance with the
applicable municipal master plan adopted pursuant to section
139-59-6, C.R.S. 1%3, or any applicable master plan adopted
pursuant to section 106-2-7. If no such master plan has been
adopted, such areas shall be developed in a manner designed to
minimize congestion in the streets; to secure safety from fire,
flood waters, and other dangers; to promote health and general
welfare; to provide adequate .light and air; to prevent the
overcrowding of land; to avoid undue concentration of population;
to facilitate the adequate provision of transportation, water,
sewerage, schools, parks, and other public requirements. Such
development in such areas shall be made with reasonable
consideration, among other things, as to the character of the
area and its peculiar suitability for particular uses, and with a
view to conserving the value of buildings and encouraging the
most appropriate use of land throughout the jurisdiction of the
applicable local government.
106-7-203. Activities of state interest as determined by
local governmentsT(T5Subject to the procedures set forth in
part 4 of this article, a local government may designate certain
activities of state interest from among the following:
(a) Site selection and construction of major new domestic
water and sewage treatment systems and major extension of
existing domestic water and sewage treatment systems;
(b) Site selection and development of solid waste disposal
sites;
(c) Site selection of airports;
(d) Site selection of rapid or mass transit terminals,
stations, and fixed guideways;
(e) Site selection of arterial highways and interchanges
and collector highways;
(f) Site selection and construction of major facilities of
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a public utility;
(g) Site selection and development of new communities;
(h) Efficient utilization of municipal and industrial water
projects; and
(i) Conduct of nuclear detonations.
106-7-204. Criteria for administration of activities of
state interest. (T)[a]New domestic water and sewage treatment
systems shall he constructed in areas which will result in the
proper utilization of existing treatment plants and the orderly
development of domestic water and sewage treatment systems of
adjacent communities.
fb) Major extensions of domestic water and sewage treatment
systems shall bu permitted in those areas in which the
anticipated growth and development that may occur as a result of
such extension can be accommodated within the financial and
environmental capacity of the area to sustain sucli growth and
development.
(2) Major solid waste disposal sites shall be developed in
accordance with sound conservation practices and shall emphasize,
where feasible, the recycling of waste materials. Consideration
shall be given to longevity and subsequent use of waste disposal
sites, soil and wind conditions, the potential problems of
pollution inherent in the proposed site, and the impact on
adjacent property owners, compared with alternate locations.
(3) Airports shall be located or expanded in a manner which
will minimize disruption to the environment of existing
communities, will minimize the impact on existing community
services, and will complement the economic and transportation
needs of the state and the area.
(4) (a) Rapid or mass transit terminals, stations, or
guideways shall be located in conformance with the applicable
municipal master plan adopted pursuant to section 139-59-6,
C.R.S. 1963, or any applicable master plan adopted pursuant to
section 106-2-7. If no such master plan has been adopted, such
areas shall be developed in a manner designed to minimize
congestion in the streets; to secure safety from fire, flood
waters, and other dangers; to promote health and general welfare;
to provide adequate light and air; to prevent the overcrowding of
land; to avoid undue concentration of population; to facilitate
the adequate provision of transportation, water, sewerage,
schools, parks, snd other public requirements. Activities shall
be conducted with reasonable consideration, among other things,
as to the character of the area and its peculiar suitability for
particular uses, and with a view to conserving the value of
buildings and encouraging the most appropriate use of land
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throughout the jurisdiction of the applicable local government.
(b) Proposed locations of rapid or mass transit terminals,
stations, and fixed guideways uhich will not require the
demolition of residences or businesses shall be given preferred
consideration over competing alternatives.
(c) A proposed location of a rapid or mass transit
terminal, station, or fixed guideway that imposes a burden or
deprivation on a local government cannot be justified on the
basis of local benefit alone, i/or shall a permit for such a
location be denied solely because the location places a burden or
deprivation on one local government.
(5) Arterial highways and interchanges and collector
highways shiill be located, so that:
(a) Cornnunity traffic needs are met;
(b) Desirable community patterns are not disrupted; and
(c) Direct conflicts with adopted local government,
regional, and state master plans are avoided.
(6) Where feasible, major facilities of public utilities
shall be located so as to avoid direct conflict with adopted
local government, regional, and state master plans.
(7) When applicable, or as may otherwise be provided by
law, a new community design shall, at a minimum, provide for
transportation, waste disposal, schools, and other governmental
services in a manner that will not overload facilities of
existing communities of the region. Priority shall be given to
the development of total communities which provide for commercial
and industrial activity, as well as residences, and for internal
transportation and circulation patterns.
(8) Municipal arid industrial water piojects shall emphasize
the most efficient use of water, including, to the extent
permissible under existing law, the recycling and reuse of water.
Urban development, population densities, and site layout and
design of storm water and sanitation systems shall be
accomplished in a manner that will prevent the pollution of
aquifer recharge areas.
(9) Nuclear detonations shall be conducted so as to present
no material danger to public health and safety. Any danger to
property shall not be disproportionate to the benefits to be
derived from a detonation.
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PART 3
LEVELS OF GOVERNMENT INVOLVED AND THEIR FUNCTIONS
106-7-301. Functions of local government. (1) Pursuant to
this article, it is the function of local government to:
(a) Designate matters of state interest after public
hearing, taking into consideration:
(I) The intensity of current and foreseeable development
pressures; and
(II) Applicable guidelines for designation issued by the
applicable state agencies;
(b) Hold hearings on applications for permits for
development in areas of state interest and for activities of
state interest;
(c) Grant or deny applications for permits for development
in areas of state interest and for activities of state interest;
(d) Receive recommendations from state agencies and other
local governments relating to matters of state interest;
(e) Send recommendations to other local governments and the
Colorado land use commission relating to matters of state
interest; and
(f) Act, ur)on request of the Colorado land use commission,
with regard to specific matters of state interest.
106-7-302. Functions of other state agencies. (1)
Pursuant to thisarticle,itisthe function of other state
agencies to:
(a) Send recommendations to local governments and the
Colorado land use commission relating to designation of matters
of state interest on the basis of current and developing
information; and
0) Provide technical assistance to local governments
concerning designation of and guidelines for matters of state
interest.
(2) Primary responsibility for the recommendation and
provision of technical assistance functions described in
subsection (1) of this section is upon:
(a) The Colorado water conservation board, acting in
cooperation with the Colorado soil conservation board, with
regard to floodplains;
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(b) The Colorado state rorest service, with regard to
wildfire hazard ureas;
(c) The Colorado geological survey, with regard to geologic
hazard areas, geologic reports, and the identification of mineral
resource areas;
(d) The Colorado division of mines, with regard to mineral
extraction and the reclamation of land disturbed thereby;
(e) The Colorado soil conservation board and soil
conservation districts, with regard to resource data inventories,
soils, soil suitability, erosion and sedimentation, floodwater
problems, and watershed protection; and
(f) The division of wildlife of the department of natural
resources, with legard to significant wildlife habitats.
(3) Pursuant to section 106-7-202 (1) (d), the oil and gas
conservation commission of the state of Colorado may identify an
area of oil and gas development for designation by local
government as an area of state interest.
PART 4
DESIGNATION OF MATTERS
OF STATE INTEREST - GUIDELINES FOR ADMINISTRATION
106-7-401. Designation of matters of srate interest.. (1)
After public hearing, a local government may designate matters of
state interest within its jurisdiction, taking into
consideration:
(a) The intensity of current and foreseeable development
pressures; and
(b) Applicable guidelines for designation issued by the
Colorado land use commission after recommendation from other
state agencies, if appropriate. In adopting such guidelines, the
Colorado land use commission shall be guided by the standards set
forth in this article applicable to local governments.
(2) A designation shall:
(a) Specify the boundaries of the proposed area; and
(b) State reasons why the particular area or activity is of
state interest, the dangers that would result from uncontrolled
development of any such area or uncontrolled conduct of such
activity, and the advantages of development of such area or
conduct of such activity in a coordinated manner.
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106-7-402. Guidelines - regulations. (1) Hie local
government shall develop guidelines for administration of the
designated matters o£ state interest. The content of such
guidelines shall be such as to facilitate administration of
matters of state interest consistent with sections 106-7-202 and
106-7-204.
(2) A local government may adopt regulations interpreting
and applying its adopted guidelines in relation to specific
developments in areas of state interest and to specific
activities of state interest.
(3) No provision in this article shall be construed as
prohibiting a local government from adopting guidelines or
regulations containing requirements which are more stringent than
the requirements of the criteria listed in sections 106-7-202 and
106-7-204.
106-7-403. Technical and financial assistance. (1)
Appropriate state agencies shail provide technical assistance to
local governments in order to assist local governments in
designating matters of state interest and adopting guidelines for
the administration thereof.
(2) (a) The department of local affairs shall oversee and
coordinate the provision of technical assistance and provide
financial assistance as may be authorized by law.
(b) The department of local affairs shall determine whether
technical or financial assistance or both are to be given to a
local government on the basis of the local government's:
(I) Showing that current or reasonably foreseeable
development pressures exist within the local government's
jurisdiction; and
(II) Plan describing the proposed use of tedmical
assistance and expenditure of financial assistance.
106-7-404. Public hearing - designation of an area or
activity of state interest and adoption of guidelines by order of
local government^ (Tj The" local government shall hold a public
hearing before designating an area or activity of state interest
and adopting guidelines for administration thereof.
(2) (a) Notice, stating the time and place of the hearing
and the place at which materials relating to. the matter to be
designated and guidelines may be examined, shall be published
once at least thirty and not more than sixty days before the
public hearing in a newspaper of general circulation in the
county. The local government shall send written notice to the
Colorado land use commission of a public hearing to be held for
the purpose of designation and adoption of guidelines at least
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thirty days and not more than si> y days before such hearing.
(b) My person may request, in writing, that his name and
address be placed on a mailing list to receive notice of all
hearings held pursuant to this section. If the local government
decides to maintain such a mailing list, it shall mail notices to
cadi person paying an annual fee reasonably related to the cost
of production, handling, and mailing such nocice. In order to
have his name and address retained on said mailing list, the
person shall resubmit his name and address and pay such fee
before January 31 of each year.
(3) Within thirty days after completion of the public
hearing, the local government, by order, may adopt, adopt with
modification, or reject the particular designation and
guidelines; but the local government, in any case, shall have the
duty to designate any matter whidi has been finally determined to
be a matter of state interest and adopt guidelines for the
administration thereof.
(4) After a matter of state interest is designated pursuant
to this section, no person shall .engage in development in such
area and no such activity shall be conducted until the
designation and guidelines for such area or activity are finally
determined pursuant to this article.
(5) Upon adoption by order, all relevant materials relating
to the designation and guidelines shall be forwarded to the
Colorado land use commission for review,
106-7-405. Report of local government's progress. (1) Not
later than one hundred eighty days after theeffective date of
this article, each local government shall report to the Colorado
land use commission, on a form to be furnished by the Colorado
land use commission, the progress made toward designation and
adoption of guidelines for administration of matters of state
interest.
(2) Upon the basis of the information contained in such
reports and any information received pursuant to any other
relevant provision of this article, the Colorado land use
commission may take appropriate action pursuant to section
106-4-3(2)(a).
106-7-406. Colorado land use commission review of local
government order containing designatron and guidelines. ~(l)Not
later than thirty days after receipt of a local government order
designating a matter of state interest and adopting guidelines
for the administration thereof, the Colorado land use commission
shall review the contents of such order on the basis of the
relevant provision:; of part 2 of this article and shall accept
the designation and guidelines or recommend modification thereof.
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(2) If the Colorado land use commission decides that
modification of the designation or guidelines is required, the
Colorado land use commission shall, within said thirty-day
period, submit to the local government written notification of
its recommendations and shall specify in writing the
modifications which the Colorado land use commission deems
necessary for compliance with the relevant provisions of part 2
of this article.
(3) Not later than thirty days after receipt of the
modifications recommended by the Colorado land use commission, a
local government shall:
(a) Modify the original order in a manner consistent with
the recommendations of the Colorado land use commission and
resubmit the order to the Colorado land use commission; or
(b) Notify the Colorado land use commission that the
Colorado land use commission's recommendations are rejected.
106-7-407. Colorado land use commission may initiate
identification, designation, and promulgation of guidelines for
matters^ of_ state '"interest'. (l) W ^h"eColorado land use
commission may submit a formal request to a local government to
take action with regard to a specific matter which said
commission considers to be of state interest within the local
government's jurisdiction. Such request shall identify the
specific matter and shall set forth the information required in
section 106-7-401 (2) (a) and (2) (b). Not later than thirty
days after receipt of such request, the local government shall
publish notice and hold a hearing within sixty days pursuant to
the provisions cf section 106-7-404, and issue its order
thereunder.
(b) After receipt by a local government of a request from
the Colorado land use commission pursuant to paragraph (a) of
this subsection (1), no person shall engage in development in the
area or conduct the activity specifically described in said
request until the local government has held its hearing and
issued its order relating thereto.
(c) If the local government's order fails to designate such
matter and adopt guidelines therefor, or, after designation,
fails to adopt guidelines therefor pursuant to standards set
forth in this article applicable to local governments, the
Colorado land use commission may seek judicial review of such
order or guidelines by a trial de novo in the district court for
the judicial district in which the local government is located.
During the pendency of such court proceedings> no person shall
engage in development in the area or conduct the activity
specifically described in said request except on such terms and
conditions as authorized by the court.
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PAR I 5
PERMITS FOR DEVELOB1ENT IN ARMAS OP STATE INTEREST AND FOR
CONDUCT OF ACTIVITIES OF STATE INTEREST
106-7-501. Permit for development in area of state interest
or for conduct ofan activity of state interest required.(1)
TO]Anyperson desiring to engage in development in an area of
state interest or to conduct an activity of state interest shall
file an application for a permit with the local government in
which such development or activity is to take place. The
application shall be filed on a form prescribed by the Colorado
land use commission. A reasonable fee determined by the local
government sufficient to cover the cost of processing the
application, including the cost of holding the necessary
hearings, shall be paid at the time of filing such application.
(b) The requirement of paragraph (a) of tnis subsection (1)
that a public utility obtain a permit shall not be deemed to
waive the requirements of article 5 of chapter 115, C.R.S. 1963,
that a public utility obtain a certificate of public convenience
and necessity.
(2) (a) Not later than thirty days after receipt of an
application for a permit, the local government shall publish
notice of a hearing on said application. Such notice shall be
published once in a newspaper of general circulation in the
county, not less than thirty nor more than sixty days before the
date set for hearing, and shall be given to the Colorado land use
commission. The Colorado land use commission may give notice to
such other persons as it determines not later than fourteen days
before such hearing.
(b) If a person proposes to engage in development in an
area of state interest or for conduct of an activity of state
interest not previously designated and for which guidelines have
not been adopted, the local government may hold one hearing for
determination of designation and guidelines and granting or
denying the permit.
(c) The local government may maintain a mailing list and
send notice of hearings relating to permits in a manner similar
to that described in section 106-7-404 (2) (b).
(3) The local government may approve an application for a
permit to engage in development in an area of state interest if
the proposed development complies with the local government's
guidelines and regulations governing such area. If the proposed
development does not comply with the guidelines and regulations,
the permit shall be denied.
(4) The local government may approve an application for a
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permit for conduct of art activity of state interest if the
proposed activity complies with the local government's
regulations ?>nd guidelines for conduct of such activity. If the
proposed activity does not comply with the guidelines and
regulations, the permit shall be denied.
(5) The local government conducting a hearing pursuant to
this section shall:
(X; State, in writing, reasons for its decision, and its
findings and conclusions; and
(b) Preserve a record of such proceedings.
(6) Aftf.r the effective date of this article, any person
desiring to engage in a development in a designated area of state
interest or tn conduct a designated activity of state interest
who doe? not obtain a permit pursuant to this section may be
enjoined by the Colorado land use commission or the appropriate
local govr>7Tur<5nt from engaging in such development or conducting
such activity.
106-7-502, Judicial review. The denial of a permit by a
local government agency shall be subject to judicial review in
the district court for the judicial district in which the major
development or Activity is to occur.
SECTION 2, Article 3 of chapter 106, Colorado Revised
Statutes 1P6", as anvxtf-^., is amended BY THE ADDITION OF A NEW
SECTION to read:
10f-> -$~9. 3 ^atc>-ij^ -vY£vg>'31p for identification of matters of
state ipterei-i: as part_ of local Tand use planning. (T5"J^e"
department ot local ?±fairs shall conduct a statewide program
encouraging counties and rrunicipalities to prepare, as a part, of
the cotiDrehensive plan provided for in section 106-2-5 and
article 59 of charter 139 s C.R.S. 1963, a complete and detailed
identification ?x»d fKsxpn^txcn of all matters of state interest
within each county by June 30, 1976. The general assembly shall
appropriate funds for this purpose to the department of local
affairs for distribution to participating counties. Each county
desiring to nnrticipntc in the identification and designation of
matters of state interest program established by this section
shall be allocated an eoual amount by the department of local
affairs from the funds so appropriated, to be expended by each
county separately or through an organized group of counties or
counties and municipalities. The department of local affairs, in
cooperation with applicable state agencies, shall establish
reasonable standards relative to the scope, detail, and accuracy
of the program pnd shell insure that all information ?s
comparable for each county. Each county shall, after
consultation with the municipality, prepare such identification
and designation for territory located within these municipalities
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which request such preparation and in any municipality which
fails to undertake an identification and designation program.
Bach county shall, upon request of the municipality, assist the
municipality in its identification and designation program.
(2) The general assembly shall appropriate to the
department of local affairs funds to assist counties and
municipalities participating in the identification and
designation of matters of state interest program, where
additional assistance is deemed by the department of local
affairs to be necessary. The department of local affairs shall
also allocate such funds upon request of any county participating
in the identification and designation of matters of state
interest program under subsection (1) of this section for
implementation of supplemental planning in that county, or to any
municipality, based upon priorities established by the department
of local affairs and on the need and capabilities of each county
and niun.icipaJ.ity.
SECTION 3, 106-4-3 (2) (a), Colorado Revised Statutes 1%3
(1971 3upp.)> is amended to read:
106-4-3. Duties of the commission - temporary emergency
power. (2) "[a) Whenever in the normal course of Its "duties "as
set forth in this article the commission determines that there is
in progress or proposed a land development activity which
constitutes a danger of irreparable injury, loss, or damage of
serious and major proportions to the public health, welfare, or
safety, the commission shall immediately give written notice to
the board, of eour.ty correnissioners of each comity involved of the
pertinent factr. and dangers with respect to such activity. If
the said board of county commissioners does not remedy the
situation withir a reasonable time, the commission may request
the governor to teview such facts and dangers with respect to
such activity. If the governor grants such request, such review
shall be conducted by the governor at a meeting with the
commission and the boards of county commissioners of the counties
involved. If, after such review, the governor shall determine
that such activity does constitute such a danger, the governor
may direct the commission to issue its written cease and desist
order to the person in control of such activity. Such order
shall require that such person immediately discontinue such
activity. If such activity, notwithstanding such order, is
continued, the commission may apply to any district court of this
state in which such activity is located for a temporary
restraining order, preliminary injunction, or permanent
injunction, as provided for in the Colorado rules of civil
procedure. Any such action shall be given precedence over all
other matters pending in such district court. 'Hie institution of
such action shall confer upon said district court exclusive
jurisdiction to determine finally the subject matter thereof.
SECTION 4. Article 4 of chapter 106, Colorado Revised
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Statutes 1963, as amended, is amended BY TIE ADDITION OF A NEW
SECTION to read:
106-4-5. Commission staff to assist counties and
municipalities, 'the commission, within available appropriations,
shall assign full-time professional staff members to assist
counties and municipalities in the program established under
article 7 of this chapter and to monitor progress in the same.
No later than February 1, 1975, the commission shall issue its
report to the general assembly as to progress being made in such
program and shall include in its report those items required by
section 106-4-4 (4) (b) and (4) (c).
SECTION 5. Appropriation. (1) There is hereby
appropriated to the department oT local affairs, out of any
moneys in the state treasury not otherwise appropriated, the sum
of two million seventy-five thousand dollars ($2,075,000), or so
much thereof as may be necessary, to implement the provisions of
section 106-3-9, C.R.S. 1963, which moneys shall become available
upon passage of this act and remain available until June 30,
1975, to be allocated as follows: Identification and designation
of matters of state interest program - one million five hundred
seventy-five thousand dollars ($1,575,000); supplemental planning
- five hundred thousand dollars ($500,000).
(2) There is hereby appropriated out of any moneys in the
state treasury not otherwise appropriated, to the Colorado land
use commission, for the fiscal year beginning July 1, 1974, the
sum of three hundred thousand dollars ($300,000), or so much
thereof as may be necessary, to provide assistance to counties
and muncipalities pursuant to section 106-4-5, C.R.S. 1963 (10.0
FTE, five of which shall be full-time professional staff pursuant
to said section 106-4-5).
SECTION 6. Safety clause. The general assembly hereby
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finds, determines, and declares that this act is necessary for
the immediate preservation of the public peace, health, and
safety.
John D. Fuhr Ted L. Strickland
SPEAKER OF THE HOUSE ACTING PRESIDKNT
OF REPRESEOTATIVES OF THE SENATE
Lorraine F. Lombardi Comfort w. Shaw
CHIEF CLERK OF THE HOUSE SECR1-TARY OF
OF REPRESENTATIVES THE SEMTF.
APPROVED
John I). Vandeihoof
GOVERNOR OF THE STATE OF COLORADO
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APPENDIX E
COLORADO EMISSION CONTROL REGULATIONS AND
AMBIENT AIR QUALITY STANDARDS - AS AMENDED
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COMMON PROVISIONS REGULATION
Definitions, Statement of intent and General Provisions applicable to all
emission control regulations adopted by the Colorado Air Pollution Control
Commission.
APPLICABILITY:
Emission control regulations adopted by the Commission apply throughout
Colorado unless otherwise stipulated. The statement of intent, defini-
tions, and general provisions of this regulation apply to all emission
control regulations adopted by the Commission unless otherwise stipulated.
AUTHORITY:
Section 66-31-8 of the Colorado Air Pollution Control Act of 1970 provides;
"As promptly as possible, the Commission shall adopt and promulgate emission
control regulations which require the use of effective practical air
pollution controls for each and every significant source, potential source,
and type of source of air contamination throughout the entire State and
thereafter may modify such regulations from time to time." Sections 66-31-4,
66-31-6 and 66-31-8 of the Act are the general statutory authority for
adoption by the Air Pollution Control Commission of standards and the
specific section of the Act is cited in each instance.
STATE OF COLORADO AIR POLLUTION CONTROL ACT (1970) LEGISLATIVE DECLARATION
(66-31-2)
In order to foster the health, welfare, convenience, and comfort of the
inhabitants of the State of Colorado, and to facilitate the enjoyment of
nature, scenery, and other resources of the State, it is hereby declared
to be the policy of the State to achieve the maximum practical degree of
air purity in every portion of the State. To that end, it is the purpose
of this article to require the use of all available practical methods to
reduce, prevent, and control air pollution throughout the entire State of
Colorado, and to maintain a cooperative program between the State and local
units of government. It is further declared that the prevention, abatement,
and control of air pollution in each portion of the entire State are matters
of statewide concern and are effected with a public interest and that the
provisions of this article are enacted in the exercise of the police powers
of this State for the purpose of protecting the health, peace, safety, and
general welfare of the people of this State.
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INTENT:
To implement the legislative declaration and other sections of the Act, the
Commission declares that it is the intent and purpose of these regulations:
1. To achieve and maintain levels of air quality which will
protect human health and safety, prevent injury to plant
and animal life, prevent damage to property, prevent
unreasonable interference with the public welfare, preserve
visibility and protect scenic, aesthetic and historic
values of Colorado,
2. To require the use of all available practical methods to
reduce, prevent, and control air pollution for the pro-
tection of the health, safety, and general welfare of
the people of the state of Colorado. In order to achieve
air purity consistent with this intent it is necessary,
ultimately to control air contaminant emissions to such
a degree of opacity so that the emissions are no longer
visible,
3. To prevent significant degradation of Colorado's air resource,
4. To prevent odors and other air pollution problems which
interfere with the comfortable enjoyment of life, and
5. To apply the major resources of the Colorado air pollution
control programs toward solving priority air pollution problems.
The Commission recognizes that the growth in the amount and complexity
of air pollution in Colorado is brought about by and incident to population
growth, mobility, increased affluence, industrial development and changing
social values in said State. The Commission believes that the air pollution •
problem is likely to be aggravated and compounded by additional population
growth, mobility, affluence, industrial development, and changing social
values in the future, which are likely to result in serious potential danger -
to the public and the environment. Therefore, the Commission intends to
pursue solutions, in conjunction with other appropriate agencies and interests,
which have a direct interest and capability in solving a growing air pollution
problem in relation to the broader environmental degradation problem. It is
the intent of the Commission to coordinate with industrial, commercial,
agricultural and transportation planning organizations, land use and other
environmental organizations, the public, the legislature, educational organi-
zations, and other major interests in such a manner as to prevent air pollu-
tion in Colorado.
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DEFINITIONS;
The following words and phrases have the following meanings unless
the context in which they are used requires otherwise:
ACT
AIR CONTAMINANT
AIR CONTAMINATION SOURCE
AIR CONTAMINATION SOURCE
(existing)
AIR CONTAMINATION SOURCE.
(new)
AIR POLLUTION
AIR POLLUTION CONTROL
AUTHORITY
AMBIENT AIR
the Colorado Air Pollution Control Act
of 1970, Chapter 64, Colorado Session
laws 1970.
any fume, smoke, particulate matter,
vapor, gas, or any combination thereof,
but not including water vapor or steam
condensate.
any source whatsoever at, from, or by
reason of which there is emitted or
discharged into the atmosphere any
air contaminant.
Any air contamination source, which has
been constructed or for which there is a
binding agreement or contract: providing
for its construction or modification to
be completed within a reasonable time
after the effective date of the regulation
in question.
Any air contamination source which is to
be constructed or modified and which is
other than an existing air contamination
source.
any concentration of one or more air
contaminants in the outdoor atmosphere as
has caused, is causing, or if unabated
may cause injury to human, plant, or
animal life, or injury to property, or
which unreasonably interferes with the
comfortable enjoyment of life or property
or with the conduct of business.
the Division, or any person or agency given
authority by the Division, or a local govern-
mental unit duly authorized with respect to
air pollution control.
is the surrounding outside air.
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MOSPHERE
COMMISSION
DEPARTMENT
DIVISION
DUSTS
EMISSION
EMISSION CONTROL
REGULATION-
FUEL BURNING EQUIPMENT
FUGITIVE DUST
means the air that envelops or surrounds
the earth. For the purpose of this
regulation emissions of air contaminants
from a building or structure not specifi-
cally designed to control air pollution
originating from an air contamination
source or sources within such building or
structure shall constitute an emission to
the atmosphere.
the Colorado Air Pollution Control Commission
created by Section 66-31-4 of the Act.
The Colorado Department of Health.
the Division of Air Pollution Control,
Colorado Department of Health.
minute solid particles released into the
air by natural forces or by mechanical
processes such as crushing, grinding,
milling, drilling, demolishing, shoveling,
conveying, covering, bagging, sweeping, etc.
the discharge or release into the atmosphere
of one or more air contaminants.
any standard promulgated by regulation which
is applicable to all air contamination sources
within a specified area and which prohibits
or establishes permissible limits for specific
types of emissions in such area, and also any
regulation which by its terms is applicable
to a.specified type of facility, process, or
activity for the purpose of controlling the
extent, degree, or nature of contamination
emitted from such type of-facility, process,
or activity, and also any regulation adopted
for the purpose of preventing or minimizing
emission of any air contaminant in potentially
dangerous quantities.
any furnace, boiler apparatus, stack, or
appurtenances thereto used in the process
of burning fuel for the primary purpose of
producing heat or power by indirect heat
transfer.
solid airborne particulate matter emitted
from any source other than an opening which
channels the flow or air contaminants and
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then exhausts the contaminants directly into
the atmosphere. Fugitive dust also includes
solid particles released into the atmosphere
by natural forces or by mechanical processes
such as crushing, grinding, milling, drilling,
demolishing, shoveling, conveying, covering,
bagging, sweeping, etc.
INCINERATORS
Incinerator
Approvable Incinerator
(Effective
May 1, 1973)
any equipment, device, or contrivance
used for the destruction of garbage,
rubbish/ or other wastes by burning, but
not wood wastes burned in devices com-
monly called wigwam waste burners.
any incinerator which is constructed and
is operated so as to meet all the regula-
tions of the Commission pertaining to
incinerators.
Multiple Chamber
Incinerator
any article, machine, equipment, contri-
vance, structure, or part of a structure
used to dispose of combustible refuse by
burning, consisting of three or more re-
fractory-lined combustion furnaces in
series, physically separated by refract-
ory walls, inter-connected by gas passage
ports or ducts, and employing adequate
design parameters necessary for maximum
combustion of the material to be burned.
LAND DEVELOPER
Any person, firm, corporation or governmental
entity who initiates any change in the state
of existing land use. The person, firm,
corporation or governmental entity who contracts
with others for construction services for said
change in land use will be deemed to be the
land developer.
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MODIFICATIONS
OPACITY
OPEN BURNING
OPENING
1. The construction or installation on
the premises of new equipment;
2. The replacement or alteration of
equipment in such a manner as to
either increase or decrease the pro-
duction or control of air contamina-
tion excluding routine adjustments
or maintenance; and
3. the moving of equipment to another
premise.
the degree to which an air contaminant
emission obscures the view of an observer,
expressed in percentage of the obscuration,
or in the degree (percent) to which trans-
mittance of light is reduced by an air
contaminant emission-
fire, where any material is burned in the
open or in a receptacle other than a
furnace, incinerator, or other equipment
connected to a stack or chimney.
any single chimney, conduit, duct, smoke-
stack, flue or other contrivance from
which air contaminants are exhausted into
the atmosphere.
PAKTICULATE MATTER
PERSON
PROCESS OR PROCESS
EQUIPMENT
any material, except uncombined water,
that exists in a finely divided form as
a liquid or solid.
any individual, public or private corpora-
tion, partnership, association, firm, trust
estate, the State or any department, insti-
tution, or agency thereof, any municipal
corporation, county, city and county, or
other political subdivision of the State,
or any other legal entity whatsoever which
is recognized by law as the subject of
rights and duties.
any action, operation, or treatment,
involving chemical, industrial, or manu-
facturing factors, such as heat-treating
furnaces, by-product coke plants, coke-
baking ovens, mixing kettles, cupulas,
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blast furnaces, open hearth furnaces,
heating and reheating furnaces, puddling
furnaces, sintering plants, Bessemer con-
verters, electric steel furnaces, ferrous
and non-ferrous foundries, kilns, stills,
dryers, roasters, and equipment used in
connection therewith, and all other
methods or forms of manufacturing or pro-
cessing that may emit air contamination.
PROCESS UNIT any single process or process equipment
PROCESS WEIGHT the total weight of all materials intro-
duced into a source operation, which
source causes any discharge of air con-
taminants into the atmosphere. Solid
fuels introduced into any specific source
will be considered as part of the process
• weight, but liquid and gaseous fuels and
combustion air will not.
PROCESS WEIGHT RATE a rate established as follows:
(a) for continuous .source operations, the
total process weight for- the entire
period of continuous operation or for
a typical portion thereof, divided by
the number of hours of such period or
portion.thereof, or
(b) for cyclical or batch unit operations,
or unit processes, the total process
weight for a period that covers a
complete operation or an integral
number of cycles, divided by the
hours of actual process operation
during such a period, or
(c) for operations, not specified above,
determine the process weight that
results in a minimum value for
allowable emissions.
SMOKE small gas-borne particles resulting from
incomplete combustion, consisting pre-
dominantly, but not exclusively of carbon,
and other combustible material.
STACK OR CHIMNEY any vertical flue, conduit, or duct
arranged to conduct an effluent to the
open air.
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STANDARD CONDITIONS a gas temperature of 68 degrees Fahren-
heit and a gas pressure of 29.92 inches
of mercury.
DPSET CONDITIONS " an unpredictable equipment failure or
other malfunction which results in the
violation of emission control regulation,
and which is not due to improper or care-
less operation.
WIGWAM WASTE BURNER any burner which consists of a single
(Effective: May 1, 1973) combustion chamber, has the general
features of a truncated cone, and is
used for incineration of wood wastes.
II. GENERAL:
A. TO CONTROL' EMISSIONS LEAVING COLORADO;
"When emissions generated from sources in Colorado cross the state
boundary line, such emissions shall not cause the air quality
standards of the receiving state to be exceeded provided reciprocal
action is taken by the receiving state." (66-31-21(3)).
B. EMISSION MONITORING REQUIREMENTS;
The Division may require owners or operators of stationary air
contamination sources to install, maintain, and use instrumentation
to monitor and record emission data as a basis for periodic reports
to the Division. (66-31-6, 66-31-10(2)(c) and (d)).
C. PERFORMANCE TESTING;
In order to determine compliance with emission control regulations,
the Division may require the owner or operator of any source to
" conduct performance tests in accordance with methods approved by
the Division with the tests being made at the expense of the owner
or operator. The Division may monitor such required performance
tests conducted by the owner or operator and may also conduct
performance tests. (66-31-6, 66-31-10(2)(c) and (d)).
D. UPSET CONDITIONS .AND BREAKDOWNS:
Upset conditions, as defined, shall JiQt_±>e.j3eemed. to be_in violation
of these Regulations provided that the Air Pollution Control Division
is notified as soon as possible ;_but 310"later--.than 2 hours after the:
start of the next working dayr followedi.by .written notice to the . .^~
Division'explaining the cause of theiTQOcurreirce\ and that proper action
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has been or is being taken to correct.the conditions causing said
violation and to prevent such excess emissions in the future.
(66-31-8(4)) .
E. EFFECTIVE DATE;
The effective date of this "common provisions--regulation" is
February 1, 1972.
F. REVOCATION OF TEMPORARY EMISSION _COtCTROL ^REGULATIONS ;
The temporary emission control regulations, identical to provisions
set forth in sections 66-29-5(2) through (6), Colorado revised
Statutes 1963, as amended, are revoked. (66-31-24(1)).
G. CONFLICTS;
Nothing in these regulations is intended to permit any practice
which is a violation of any statute, ordinance or regulation.
(66-31-6).
H. SEVERABILITY CLAUSE;
If any Regulation, Section, clause, phrase, or standard contained
in these regulations shall for any reason be held to be inoperative,
unconstitutional, void or invalid, the validity of the remaining
portions thereof shall not be affected thereby and the Commission
does hereby declare that it severally passed and adopted the
provisions contained therein separately and apart from the other
provisions thereof. (66-31-6).
I. CIRCUMVENTION CLAUSE;
A person shall not build, erect, install, or use any article,
machine, equipment, condition, or any contrivance, the use of
which, without resulting in a reduction in the total release of
air contaminants to the atmosphere, reduces or conceals an
emission which would otherwise constitute a violation of this
Regulation. No person shall circumvent this Regulation by using
more openings than is considered normal practice by the industry
or activity in question. (Sections 66-31-8(1)(a) and (b), and
66-31-8(3)(a)).
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J. COMPLIANCE PLAN INCREMENTS OF PROGRESS;
Any hearing request made in accordance with 66-31-13(4)(a)(iii) or
(iv), or compliance plan that is received by the Division, Variance
Board or Commission, pursuant to any Commission Air Quality Control
Regulation or State Implementation Plan requirement shall contain
the following Increments of Progress:
1. Date of submittal of the source's final control
plan to the appropriate air pollution control
agency;
2o Date by which contracts for emission control systems
or process modifications x^ill be awarded; or date by
which orders will be issued for the purchase of
component parts to accomplish emission control or
process modification;
3. Date of initiation of on-site construction or
installation of emission control equipment or
process changes;
4. Date by which on-site construction or installation
of emission control equipment or process modifica-
tion is to be completed; and
5. Date by which final compliance is to be achieved.
Exceptions:
Sources that are solely indirect sources of air pollution.
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REGULATION NO. 1
(Amended)
Emission Control Regulations for
Participates, Smokes, and Sulfur Oxides
for the State of Colorado
Colorado Air Pollution Control Commission
Adopted : December 9,1971
Effective Date: February 1, 1972
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REGULATION NO. 1
(Amended)
Emission Control Regulations for
Particulates, Smokes, and Sulfur Oxides
for the State of Colorado
I. SMOKE EMISSIONS AND OPACITY REGULATIONS;
A. Stationary Air Contamination Sources:
1. No person shall emit or cause to be emitted into the
atmosphere, from any air contamination source of emission
whatsoever, any air contaminant which is of such a shade
or density as to obscure an observer's vision to a degree
in excess of 20% opacity. Instrumentation which results
in equivalent readings may be used in specific installa-
tions if approved in advance by the Air Pollution Control
Division. (66-31-8(2) (a) and (b).
2. Exceptions:
a. No person shall emit or cause to be emitted into the
atmosphere from any alfalfa dehydrating mill, any
air contaminant for a period or periods aggregating
more than three minutes in any 60 consecutive minutes
which is of such a shade or density as to obscure an
observer's-vision to a degree in excess of 40% opacity.
This emission standard for alfalfa dehydrating mills
shall be in effect up to and including one year from
the effective date of the Smoke Emissions and Opacity
Regulations (Part I, Section A); thereafter, the 20%
opacity limitation provided in_.Part I Section A shall
apply to emissions from alfalfa dehydrating mills.
(66-31-8(3)(a) and (f)).
b. No person shall emit or cause to be emitted into the
atmosphere from any pilot plant and experimental
operation any air contaminant for a"period or periods
aggregating more than three minutes in any 60 conse-
cutive minutes which is'of such a shade or density as
to obscure an observer's vision to a degree in excess
of 40% opacity. This emission standard for pilot
plants and experimental operations shall be in effect
for a period not to exceed 180 operating days, cumulative
total, from the date such operations commence; there-
after, the 20% opacity limitation provided in Part I
Section A of these regulations shall apply to emissions
from pilot plants and experimental operations.
(66-31-8(1)(a)(e) and (f)).
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c. Emissions from fireplaces used for non-commercial or
recreational purposes shall be exempt from Part I
Section A.I of these regulations. (66-31-8(1)(a)
(d)(e) and (f)}.
d. Provisions of I.A.I shall not apply to emissions during
the building of a new fire, cleaning of fires, soot
blowing, start-up, any process modification or adjust-
ment, or occasional cleaning of control equipment, the
shade or appearance of which is not darker than an
equivalent opacity as to obscure an observer's view to
a degree not greater than 40%, for a period or periods
aggregating no more than 3 minutes in any one hour.
e,. The provisions of I.A.I shall not
apply to fugitive dust. See instead
Section II.D. of this regulation.
B. Transportation Sources:
1. Four-cycle gasoline-powered vehicles:
No'person shall emit or cause to be emitted into the
atmosphere for a period greater than 5 consecutive
seconds from any four-cycle gasoline-powered vehicle
whatsoever any visible air contaminant.
2. Two-cycle gasoline-powered vehicles:
No person shall emit or cause to be emitted from any
two-cycle gasoline-powered vehicle into the atmosphere
any visible air contaminant which is of such a shade
or density as to obscure an observer's vision to a
degree equal to or greater than 20% opacity, except
for a period not exceeding 10 consecutive seconds.
3. Diesel-powered vehicles:
a. No person shall emit or cause to be emitted into
the atmosphere from any diesel-powered vehicle
operating below 8,000 feet (mean sea level) any
air contaminant, for a period greater than 10
consecutive seconds, which is of such a shade or
density as to obscure an observer's vision to a
degree in excess of 30% opacity.
(66-31-8(2)(a) and (b) , 66-31-8(3)(a) and (b)).
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No person shall emit or cause to be emitted into
the atmosphere from any diesel-powered vehicle
operating above 8,000 feet (mean sea.level) any
air contaminant, for a period greater than 10
consecutive seconds, which is of such a shade or
density as to obscure an observer's vision to a
degree in excess of 40% opacity.
(66-31-8(2)(a) and (b) and 66-31-8(3)(a) and (b)).
c. Exceptions:
c-1. Emissions from diesel-powered vehicles exceeding
the requirements of Part B Sections 3(a) and (b)
of these regulations shall be exempt for a period
of twenty (20) minutes if the emissions are a
direct result of a cold engine start-up and provided
the vehicle is in a stationary position.
(66-31-8(4)).
c-2. All off-highway heavy duty diesel-powered vehicles
shall be exempt from the provisions of Part B
Sections 3(a) and (b) for nonconsecutive periods
of fifteen (15) seconds. (66-31-8(4).
4. Diesel-Powered Locomotives:
a. Until July 1, 1978 no person shall emit or cause to be
emitted into the atmosphere from any diesel-powered
locomotive any air contaminant which is of such a shade
or density as to obscure an observer's vision to a
degree in excess of 30% opacity below 6,000 feet
(mean sea level) and 40% opacity above 6,000 feet
(mean sea level). (66-31-8(2)(a) and (b), and
66-31-8(3)(a) and (b)).
b. After July 1, 1978 no person shall emit or cause to be
emitted into the atmosphere from any diesel-powered
locomotive any air contaminant which is of such a shade
or density as to obscure an observer's vision to a
degree in excess of 20% opacity below 6,000 feet (mean
sea level) and 30% opacity above 6,000 feet (mean sea
level). (66-31-8(2)(a) and (b), and 66-31-8(3)(a) and
(b)).
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c. Exceptions to Parts I.B.4(a) and (b).
c-1 Opacity emissions as a result of a cold engine
start-up not to exceed thirty (30) consecutive
minutes provided the locomotive is in a stationary
position. (66-31-8(4)).
c-2 Opacity emissions for nonconsecutive periods of
three (3) minutes with an aggregate of not more
than ten (10) minutes in one hour when a loco-
motive engine is being tested, adjusted, rebuilt
or repaired in the maintenance yards.
(66-31-8(4)).
c-3 Opacity emissions for nonconsecutive periods of
four (4) minutes when a locomotive is accelerated
after standing still. (66-31-8(4)).
•
c-4 Until July 1, 1978 when diesel locomotives are
used for switching, opacity emissions are not to
exceed 40% opacity except for nonconsecutive
periods of fifteen (15) seconds; however, opacity
emissions are never to exceed 50% opacity.
(66-31-8(4)).
d. The owner or operator of any diesel powered vehicles
that have been cited for violation of Section I.E.4
of this regulation, but that are unavailable for a
compliance inspection, shall submit to the Division
an affidavit attesting to those abatement measures
which have been completed and shall state in that
affidavit that the vehicles cited have achieved
compliance with this regulation.
SOURCE: Section C - Open Burning,
Repealed and Readopted February 8r 1973, Effective May 1, 1973:
C. Open Burning:
1. No person shall burn or permit to be burned on any open
premises owned or controlled by him, or on any public street,
alley, or other land adjacent to such premises, rubbish,
waste, paper, wood, or other flammable material unless a
permit therefor shall first have been obtained from the
appropriate authority enforcing air pollution control
standards or the designee of the Air Pollution Control
Division. In granting or denying the issuance of any
such permit, said authority shall base its action on the
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location and proximity of such burning to any building
or other structure, the potential contribution of such
burning to air pollution in the area, climatic conditions
on the day or days of such burning, and compliance by the
applicant for the permit with applicable fire protection
and safety requirements of the local authority or area,
and the air pollution control authority is satisfied that
there is no practical alternative method for the disposal
of the material to be burned or to conduct the desired
activity and that the open burning is conducted in such
a reasonable manner so as to minimize emissions including
but not limited to the use of non-approvable incinerators
and air curtain destructors, the use of auxiliary clean
fuel, drying the material prior to ignition and separating.
out for alternate disposal: rubber, tires, plastics, wire,
insulation and other similar smoke-producing material.
(66-31-8(2)(a), (b), (f), and 66-31-20)).
2. Except ions:
a. The provisions of Part I Section C of these regulations
shall not apply to non-commercial burning of private
household trash except
a-1. Inside such air pollution control areas as have
been or shall have been or shall be designated
by the Air Pollution Control Commission. (see
Exhibit No. 1).
a-2. Inside a 2-mile boundary from the corporate
limits of any city or town with a population
of over 500 as determined by the latest Federal
.census and
a-3. Inside any area the Commission has designated as
having a reasonable alternative to open burning
including but not limited to a refuse collection
system and sanitary landfill. (66-31-8(4)).
b. Fires used for non-commercial cooking of food for human
beings or for instructional or recreational purposes
shall be exempt from Part I, Section C of these regu-
lations. (66-31-8(4)).
c. Smokeless flares or safety flares for the combustion
of waste gases shall be exempt from Part I, Section C
of these regulations. (66-31-8(4)).
E-17
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d. Flares used to indicate some danger to the public shall
be exempt from Part I, Section C of these regulations.
(66-31-8(4)).
e. Emissions from fireplaces used for non-commercial,
recreational or aesthetic purposes shall be exempt
from Part I.C.I of this regulation outside those areas
designated in Section C.2.a. hereof. Inside those
areas, fireplace fuel shall be limited to dry wood,
dry paper, or smokeless fuel. (66-31-8(4)).
II. PARTICULATB EMISSION REGULATIONS
A. Fuel-Burning Equipment:
1. No person shall cause or permit to be emitted into the
atmosphere from any fuel-burning equipment, or to pass
a convenient measuring point near any opening, particu-
late matter in the flue gases which exceed 0.5 pounds
per 1,000,000 BTU heat input for fuel-burning units
generating not more than 1,000,000 BTU per hour total
input. For single units generating 1,000,000 BTU per
hour or more total input, Figure 1 on the following
page will be used to determine the allowable particu-
late emission limitation. For fuel-burning equipment
generating 500 million BTU input per hour or more,
particulate matter in the flue gases cannot exceed
0.1 pounds per million BTU heat input. If two or more
units connect to any opening, each unit shall, for the
purpose of computing the maximum allowable emission
rate, be considered a separate entity with the allowable
emission rate for the opening the sum of the individual
computations. (66-31-8(2) and (c), and 66 13-8(3)(a)).
Typical Values from Figure 1 are shown in TABLE I.
E-18
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E-19
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II. A (continued)
TABLE I
Particulate ' Particulate
Fuel Input Emissions Fuel Input Emissions
106 BTU/hr. lbs./106BTU 106 BTU/hr. lbs./106 BTU
0.1 0.50 100 0.15
1.0 0.50 . 500 0.10
10.0 0.27 . 1000 0.10
Interpolation of the data in TABLE I for fuel-burning
equipment shall be by use of the following equations;
PK = 0.5 FI 1.0
' . 0.26 x .
PE = 0.5 (FI) 1.0 / FI / 500.0
PE = 0.1 500.0 ^/ FI
Where: PE = Particulate Emission in pounds per million BTU
FI = Fuel Input in million BTU per hour
£s Less than or equal to (if "FI" is to the left
of the symbol) .
Greater than or equal to (if "FI" is to the
right of the symbol)
*
Method of Measurement :
a. Emission rates shall be measured according to the
American Society of Mechanical Engineer's Power Test
Codes - PTC-27 dated 1957 and entitled, "Determining
Dust Concentrations in a Gas Stream" or any equivalent
method which has been approved by the Air Pollution
Control Division in advance of such measurement.
(66-31-8(2) (a) and (c^ and 66-31-8 (3) (a) ).
E-20
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NOTE: THIS AMENDMENT TO REGULATION NO. 1, SECTION II.B. ENTITLED,
"INCINERATORS" RESCINDS AND REPLACES SECTION II.B. ENTITLED,
"REFUSE BURNING EQUIPMENT."
II.
ADOPTED :
EFFECTIVE:
September 8, 1972
November 30, 1972
B. Incinerators:
1. Permits:
No person shall construct or operate any incinerator without a
permit from the Division. (66-31-10(2)(g) and 66-31-20).
a. A permit to operate will be issued for a one-year
period subject to renewal.
b. No permit shall be granted until the applicant
demonstrates that the incinerator meets the criteria
of Section 66-31-20 of the Act, and is constructed
and operated to meet all the regulations of the
Commission.
c. Inside designated air pollution control areas and
other areas outlined under Section i.e.2.a. of this
regulation, the use or operation of any incinerator
on property devoted to residential use is prohibited
and no permit shall be granted for its use.
2. Exemptions:
a. The prohibition of Section II.B.C. shall not apply
to existing residential incinerators until January
1, 1977.
b. Incinerators without a valid permit may be used for
the non-commercial burning of private household
trash where such open burning is allowed.
(See Section i.e. of this regulation).
E-21
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II. B - (continued)
3. Standard of Design and Performance:
a. Inside designated air pollution control areas (shown
on Exhibit No. 1) no person shall cause or permit an
emission of more than 0.10 grain of particulate matter
per standard cubic foot (dry flue gas corrected to
12% carbon dioxide) into the atmosphere from any new
incinerator. From any existing incinerator, no person
shall cause or permit an emission of more than 0.15
grain of particulate matter per standard cubic foot.
Effective January 1, 1977 existing incinerators shall
meet the grain loading requirement of this section for
new incinerators. (66-31-8 (2) (a) ar.d (c), and
66-31-8(3)(a) and (b).
b. Outside designated air pollution control areas, no
person shall cause or permit an emission of more than
0.15 grain of particulate matter per standard cubic
foot (dry flue gas corrected to 12% carbon dioxide)
into the atmosphere from any incinerator.
4. Method of Measurement:
a. Emission rates shall be measured according to the
American Society of Mechanical Engineer's Power Test
Codes - PTC-27 dated 1957 and entitled, "Determining
Dust Concentrations in a Gas stream" or any equivalent
method which has been approved by the Air Pollution
Control Division in advance of such measurement. The
test data shall reflect particulate gas stream concen-
trations consistent with the rated capacity of the
incinerator, and corrections for carbon dioxide will
be made without the contribution of carbon dioxide
from auxiliary fuel. (66-31-8(3)(a) and (b)).
5. Amendments to this section shall become effective .'November 30, 1972.
E-22
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II.
C. Manufacturing Processes:
No person shall cause or permit any emission into the
atmosphere in any 60 consecutive minutes from any opening
whatsoever, particulate matter in quantities in excess of
the emission rates as shown in Figure 2. If two or more
process units connect to an opening each process unit shall,
for the purpose of computing the maximum allowable emission
rate, be considered a separate entity with the allowable
emission rate for the opening the sum of the individual
computations. (66-31-8(2), (al and (c), and 66-31-8 (3) (a)
(f) and (g)).
Typical Values from Figure 2 are shown in TABLE II.
E-23
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E-24
-------
II.C(continued)
TABLE II
Process
Weight Rate
Ibs . /hr .
50
100
500
1,000
Emission Rate
Ibs . /hr .
0.03
0.55
1.53
2.25
Process
Weight Rate
Ibs./hr.
5,000
10,000
20,000
60,000
Emission Rate
Ibs./hr.
6.34
9.73
14.99
29.60
Process
Weight Rate
tons/hr.
40
60
80
Process
Emission Rate Weight Rate
tons/hr.
Ibs./hr.
31.19
33.28
34.85
100
200
500
Emission Rate
Ibs./hr.
36.11
40.35
46.72
Interpolation of -the data in Table II for the process weight rates
up to 60,000 Ibs./hr, shall be by use of the equation:
E = 3.59 P
0.62
30 tons/hr.
and interpolation and extrapolation of the data for process weight
rates in excess of 60,000 Ibs./hr. shall be by use of the equation:
E = 17.31 P
0.16
30 tons/hr. / P
Where: E = Emissions in pounds per hour.
P = Process weight rate in tons per hour.
/_, Less than or equal to (if "P" is to the left
of the symbol).
Greater than or equal to (if "P" is to the
right of the symbol)
2. Method of Measurement:
Emission rates shall be measured according to the
American Society of Mechanical Engineer's Power
Test Codes - PTC-27 dated 1957 and entitled,
"Determining Dust Concentrations in a Gas Stream"
or any equivalent method which has been approved
by the Air Pollution Control Division in advance
of such measurement. (66-31-8(2)(a) and (c) , and
66-31-8(3)(a), (f) and (g)).
E-25
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D. Fugitive Dust:
1. Effective Date and Affected Areas.
a. The existing Section li.D. of Regulation No. 1 controlling
fugitive dust shall be repealed effective July 31, 1974 and
the new Section II.D as follows shall become effective
August 1, 1974 . This delayed effective date for the new
Section II.D allows time for voluntary compliance with
the new provisions.
b. Sections II.D.3, 4 and 5 shall apply only to Commission
designated air pollution control areas as shown on page
1.13 of this Regulation No. 1.
c. Sections II.D.2, 6, 7, 8, and 9 shall apply statewide.
2. Opacity Regulations for Fugitive Dust Emissions Emanating from
Unenclosed operations .
a. No person shall emit or cause to be emitted from any
source of fugitive dust whatsoever, any particulate
matter which,
(i) at or from the source of said emission, is of
such a shade or density on the property of emission
origination so as to obscure an observer's vision
to a degree in excess of 20% opacity, or
(ii). is visibly transported off the property of emission
origination and remains visible to an observer
positioned off said property when sighting along
a line which does not cross the property of emission
origination.
b. Exceptions from Opacity Regulation Section II.D.2(a).
(i) All unpaved roads and unpaved parking lots
(covered by Section II.D.3).
(ii) Earth and construction-material moving and
excavating activities except for crushing,
grinding, milling, conveying, and bagging
processes. (covered by Section II.D.4).
(iii) Demolition, wrecking, and moving of structures
and explosives detonation activities. (covered
by Section ll.D.5).
E-26
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(iv) Open mining activities. (covered by Section
II.D.6).
(v) Agricultural cultivation activities (regulated
in part by Section II.D.7).
(vi) Sources of fugitive dust which exceed opacity
regulations for a period or periods aggregating
, less than three (3) minutes in any sixty (60)
consecutive minutes.
(vii) Sources of fugitive dust from which dust emissions
exceed opacity regulations when mud velocities
exceed 30 m.p.h. as determined by one or more of
the following practices as approved by the Division:
By a one-hour average at the nearest official station
of the U.S. Weather Service; by interpretation of
surface weather maps by a qualified meteorologist;
or by use of one or more anemometers at the site.
(viii) any other sources as specified by the Commission,
3. Unpaved Roads and Unpaved Parking Areas.
a. All new unpaved roads and unpaved parking areas:
a-1 No person shall construct or operate a new
, unpaved road, or new unpaved parking area
unless a permit therefore has been granted
by the Division pursuant to Section ll.D.8.
a-2 Exceptions:
(i) Any new road or parking area which,
after demonstration to the Division,
will not exceed an average daily
traffic count of 165 vehicles averaged
over any consecutive 3-day period.
(ii) Any new road or parking area associated
solely with housing.or apartment projects
of seven family dwelling units or less.
(iii) Any new road or parking area to be hard
surfaced (concrete or bituminous binder
and rock) within six (6) months of start
of construction, except that the person
E-27
-------
constructing or contracting to construct
said road or parking area shall notify
the Division in advance of commencing
construction of the nature, size, and
location of the hard surfacing project
and the dates on which the road or parking
area construction project is to start and
is to be completed. The person shall use
abatement and preventive measures as out-
. lined in II.D.9 during construction.
a-3 The Division may require the person owning or maintain-
ing any new or existing unpaved road to supply traffic
count information on a regular basis to the Division
as necessary to determine if additional abatement and
preventive measures or changes in the implementation
time schedule are required of the person by the Division.
b. Existing Privately Owned or Maintained unpaved Roads and Unpaved
Parking Areas.
b-1 Any person owning any unpaved road or unpaved parking area
or having a right-of-way easement or possessory right to
use the same, found by the Division to exceed a maximum
allowable traffic count of 165 vehicles per day averaged
over any consecutive 3-day period, shall discontinue and
, prevent use of that road or parking area, unless the
Division has approved a fugitive dust control plan which
includes preventive measures as outlined in II.D.9 and
unless the conditions of the approved plan are met
continually.
c. Existing Publicly Owned or Maintained Unpaved Roads and
Unpaved Parking Areas.
c-1 By July 1 of each year the Division shall submit
to the political subdivision owning or maintaining
unpaved roads or unpaved parking areas and to the
Commission, a report on the nature and degree of
emissions from existing unpaved roads and parking
areas within said political subdivisions which
exceed 165 vehicles per day averaged over any
3-day period based upon traffic count information
as collected by the Division or the political
subdivision.
E-28
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c-2 Said political subdivisions shall submit a plan
and progress report to the Division by October 1
of each year which includes a specified time
schedule for the control of fugitive dust emissions
on unpaved roads and unpaved parking areas as
reported by the Division pursuant to Section II.D.
3 (c-1). Said plans shall be based upon:
(i) availability of existing and new funds
for paving or fugitive dust suppression;
(ii) use of preventive measures applicable to
unpaved roads and unpaved parking areas
as outlined in Section II.D.9.
4. Earth and Construction-Material Moving and Excavating except for
Crushing, Grinding, Milling, Conveying and Bagging Processes.
No land developer of a new, or owner of an existing
construction or land development project shall throughout
the duration of the project, disturb or contract to disturb
by grading, excavating or depositing on more total surface
area than five (5) acres of land (in the aggregate) unless
abatement and preventive measures as outlined in Section
II.D.9 are being met continually. New sources regulated
in this paragraph 4 must be granted a permit from the
Division purusant to Section II.D.8 prior to breaking
ground.
5. Demolition, wrecking and Moving of Structures and Explosives
Detonation Activities.
a. No person shall conduct demolition, wrecking, or
moving of structures of explosives detonation
activities unless a permit therefore has been
granted by the Division pursuant to Section II.D.8
and unless the provisions' of Section II.D.9 are
being met continually.
6. Open Mining Activities:
No developer of a new or owner of an existing open
mining activity shall throughout the duration of the
operation, disturb or contract to disturb by grading,
excavating, or depositing on more total surface area
than one (1) acre of land (in the aggregate) unless
E-29
-------
the provisions of Section II.D.9 are being met con-
tinually. New open mining activities must be granted
a permit from the Division pursuant to Section II.D.8
prior to operation. Open mining shall mean the mining
of natural mineral deposits, limestone, coal, sand,
gravel, and quarry aggregate, by removing the overburden
lying above such deposits and mining directly from the
. deposits thereby exposed. The term includes, but is
'not limited to, such practices as open cut mining, open
pit raining, strip mining, quarrying, and dredging.
7. Complaint Section;
When a complaint of dust or fugitive dust is
registered with the Division by a single complainant
or multiple complainants who allege that any dust or
fugitive dust obstructs or interferes with the
reasonable and.comfortable use of his or their property,
the Division shall investigate and if the Division finds
that such conditions exist, the Division shall issue a
citation to the person or persons from whose land or
aqtivity the objectionable emission emanates and shall
require a fugitive dust control plan containing reasonable
control measures where appropriate according to the
abatement and preventive measures as outlined in Section
II.D.9.
8. New Source Permit Requirements:
a. No permit shall be granted to an applicant unless
the Division determines to its satisfaction that
a plan has been submitted on forms provided by
the Division which includes the following information*
E-30
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a-1
b.
d.
A description of tho nature and scope
of tho activity and of the existing or
new sources of fugitive dust including
but not limited to the following:
excavating
land leveling
repair or alteration
sand blasting
vehicle movement
screening
drying
waste disposal
detonation of explosives
earth moving
construction
demolition
handling
transporting
mining activities
crushing
site preparation
feed lots
'campgrounds
fairgrounds
processing of sand,
gravel and rock
cleaning
mixing
miscellaneous uses of land
storage
quarrying
unpaved roads
unpaved parking areas
a-2
a-3
a-4
Fugitive dust abatement and preventive measures
as outlined in Section II.D.9.
A time schedule for fugitive dust abatement and
prevention.
A description of any monitoring or sampling
methods used for recording and reporting
data to the Division.
e.
The permit mav be granted and renewed for any period of
time as deemed appropriate by the Division.
The permit may be granted to any single applicant for
any single project or combination of projects as deemed
appropriate by the Division.
In the granting of a permit, the Division may impose
any permit condition it deems necessary to attain and
maintain compliance with the provisions of this
Section II.D.
The Division may suspend, revoke, modify, or refuse to
renew or grant a permit under the following conditions:
(i) the requirements of this Section II.D. have
not been met.;
E-31
-------
(ii) the approved compliance or prevention plan
has not been followed as determined by the
Division, or
(iii) the permit conditions are not met.
Any appeal by an applicant of a denial or revocation of
a permit shall be conducted in accordance with the
provisions of Sections 66-31-12(4)(f), (g), and (h) of
the Act.
9. List of Abatement and Preventive Measures.
a. Unpaved Roads and Unpaved Parking Areas.'
a-1 Abatement and preventive measures shall be
approved by the Division and may include but
shall not be limited to frequent watering,
addition of dust palliatives, detouring,
paving, closure, speed control, or other
means such as surface treatment with
penetration chemicals (ligninsulfonates,
oil, water, cutbacks, etc.) or methods of
equal or greater effectiveness in reducing
the air contamination produced.
b. Demolition, Wrecking and Explosive Detonation Activities;
Earth and Construction Material Moving, Mining and
Excavation Activities.
b-1 Abatement and preventive fugitive dust control
measures shall be approved by the Division and
may include, but shall not be limited to;
wetting down, including pre-watering;
landscaping and replanting with native
vegetation;
covering, shielding or enclosing the area;
paving, temporary or permanent;
treating, the use of dust palliatives and
chemical stabilization;
detouring;
restriction of the speed of vehicles on sites;
prevention of the deposit of dirt and mud on
improved streets and roads and other such
effective means of dust control as the
Division may deem necessary;
disturbing less topsoil and reclaiming as
soon as possible.
E-32
-------
b-2 Sequential blasting shall be employed whenever or
wherever feasible to reduce the amounts of unconfined
particulate matter;
b-3 Such dust control strategies as re-vegetation, delay
of surface opening until demanded, or surface
compaction and sealing, shall be applied.
b-4 Haulage equipment shall be washed or wetted down,
treated, or covered when necessary to minimize the
amount of dust emitted in transit and in loading.
b-5 These measures shall also be enforced during periods
when actual construction work is not being conducted,
such as on weekends and holidays.
3. When not fewer than five complaints of objectionable fugitive
dust are registered with the Division, and earlier at the
option of the Division, it shall be the responsibility of the
Division to investigate the complaints to determine if a
violation of this regulation has occurred and to identify the
source or sources of the fugitive dust and the circumstances
surrounding its emission.
111. SULFUR DIOXIDE EMISSION REGULATIONS;
A. Ground Level Concentrations:
1. No person shall cause or permit any emission of sulfur
dioxide which causes a 5-minute average ground level
concentration greater than 0.25 parts per million
(by volume) more frequently than once in any 8 hours;
or a 1-1.our avenge ground level concentration greater
than 0.1 parts per million (by volume 1 more frequently
than once in any 4 days; or a 24-hour average ground
level concentration greater than 0.,05 parts per million
(by volume) more frequently than once in any 90 days.
Such limitations shall not apply to ground level concen-
trations occurring on the property from which the emission
occurs, provided such property, from the emission point
to the point of any such concentration, is controlled by
the person responsible for the emission.
(66-31-8(2)(a) and (d)).
SOURCE: Section B, Source Emission Concentrations,
Amended February 8, 1973, effective May 1, 1973:
E-33
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B. Source Emission Concentrations:
1. No person shall emit or cause to be emitted sulfur dioxide
emissions in excess of 500 ppm from any process unit.
2. Effective January 1, 1978, no person shall emit or cause to
be emitted sulfur dioxide emissions from a process unit.
a. in excess of 500 ppm from any opening and,
b. greater than 5 tons SCu per day from any process unit.
3. The limitations of Section III.B.2 shall not apply to
emissions of sulfur dioxide of less than 150 ppm.
4. On or before July 1, 1975, all owners and operators of
existing sources of sulfur dioxide, which can not show
to the Division by that date that their source or
sources are in compliance with Section III.B.2 or 3 of
this Regulation, shall submit an acceptable compliance
plan pursuant to Regulation No. 3 (Authority to Construct
and Permit to Operate) designed to meet Section III.B.2
or 3 by January 1, 1978.
5. New air contamination sources to be constructed or
contracted for construction after January 1, 1975,
shall meet the 1978 emission standard provided herein
even if operation commences prior to 1978.
E-34
-------
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C. Method of Measurement
1. For the purposes of Section A of this Regulation, measure-
ments of sulfur dioxide shall be made by the most recent
published method of the Intersociety Committee for a Manual
of Methods for Ambient Air Sampling and Analysis' ((See
e.g., Health Laboratory Science 7 (1) 4-12 (1970)) or any
equivalent method which has been approved by the Air
Pollution Control Division in advance of such measurement.
2. For the purposes of Section B of this regulation, measure-
ments of sulfur dioxide shall be made by "An Absorption-
Titration Method" ((e.g., J.S. Fritz and S.S. Yamamura,
Analytical Chemistry 27 (9) 1461 (1955) and E.B. Seidman,
Analytica 1 Choiristry 30 (10) 1680 (1959)) or any equivalent
method v/hieh has been approved by the Air Pollution Control
Division in advance of such measurement.
D. Related Compounds containing sulfur in oxidized states:
1. For the purposes of this Regulation, all oxidized forms
of sulfur (including, but not restricted to, 803, SOC^r
H2SO4 mist) shall be considered as sulfur dioxide.
2. Quantities of such oxidized sulfur compounds, as measured
by procedures established in Section C above, shall be
converted on a molar basis to an equivalent quantity of
sulfur dioxide. The total of all such quantities, parts
per million by volume sulfur dioxide plus parts per million
by volume sulfur-dioxide-equivalents of other oxidized
forms, shall be interpreted as "parts per million by
volume sulfur dioxide" as used in Sections A and B above.
IV. EFFECTIVE DATE:
These Regulations as adopted amend and supersede Commission
Regulation No. 1 upon the effective date hereof, to wit:
February 1, 1972.
E-36
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^TSfT-ft! iVlO 9
•'"4 i i^U'i^i S\i
-------
COLORADO DEPARTMENT OF HEALTH
Air Pollution Control Commission
4210 East llth Avenue
Denver, Colorado 80220
Adopted : March 11, 1971
Effective Date; April 20, 1971
REGULATION 2
ODOR EMISSION REGULATIONS
Pursuant to Section 66-31-8(2)(e) of the Colorado Air Pollution Control
Act of 1970, the following Emission Regulations are issued:
A, No person, wherever located, shall cause or allow the emission of
odorous air contaminants from any single source such as to result in
detectable odors which are measured in excess of the following limits:
(1) For areas used predominantly for residential or commercial
purposes it is a violation if odors are detected after the
odorous air has been diluted with seven (7) or more volumes
of odor free air.
(2) In all other land use areas, it is a violation if odors are
detected after the odorous air has been diluted with
fifteen (15) or more volumes of odor free air.
(3) (a) When the source is a manufacturing process or agricultural
operation, no violation of Subsections (1) and (2) shall
be cited by the Division, provided that the best practical
treatment, maintenance, and control currently available
shall be utilized in order to maintain the lowest possible
emission of odorous gases and, where applicable, provided
there is compliance with Item 4r of the Colorado Depart-
ment of Health Pasteurized Fluid Milk and Milk Products
Regulation adopted 18 April 1967. in determining the best
practical control methods, the Division shall not require
any method which would result in an arbitrary and unreasonable
taking of property or in the practical closing of any lawful
business or activity, if such would be without corresponding
public benefit.
(b) For all areas it is a violation when odors are detected
after the odorous air has been diluted with one hundred
twenty-seven (127) or more volumes of odor free air in
which case provisions of Paragraph A(3)(a) shall not be
applicable.
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B. For the purposes of this Regulation, two odor measurements shall
be made within a period of one hour, these measurements being
separated by at least fifteen (15) minutes. These measurements
shall be made outside the property line of the property from
which the emission originates.
C. For the purposes of this Regulation, personnel for evaluating odors
shall be selected using an "intensity rating test" as outlined in
"Selection and Training of Judges for Sensory Evaluation of the
Intensity and Character of Diesel Exhaust Odors." USPHS Pub.#999-
AP-32.
D. The Barnebey Cheney Scentometer, suitably calibrated, or any other
instrument, device, or technique designated by the Colorado Air
Pollution Control Division, may be used in the determination of
the intensity of an odor and may be used as a guide in the enforce-
ment of this Regulation.
E. The provisions of this Regulation shall apply throughout the State
of Colorado.
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REGULATION NO. 3
Regulation Governing Authority to Construct
and
Permit to Operate
Colorado Air Pollution Control Commission
Adopted : December 9,1971
Effective Date: February 1, 1972
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Adopted : December 9, 1971
Effective Date: February 1, 1972
REGULATION NO. 3
Regulation Governing Authority to Construct
and
Permit to Operate
I. INSTRUCTIONS, PROCEDURAL GUIDELINES, AND SAMPLE FORMS FOR FILING AN
AIR CONTAMINANT EMISSION NOTICE:
The Act requires an "air contaminant emission notice" be filed
with the Department prior to the emission of an air contaminant from
any facility, process, or activity. The Commission has defined
insignificant sources exempted from filing a, notice as listed in
IV.A of Regulation No. 3. Any facility, process, or activity which
is altered and results in an" increase in emission of air contaminants
must also file an "air contaminant emission notice" with the Department
with respect to such proposed emission. A revised emission notice is
required and shall be filed whenever a significant change in emissions
shall have occurred. (See instructions)
Effective July 10, 1970, no person shall discharge, or cause to
be discharged, 3nto the atmosphere any air contaminant if an "air
contaminant emission notice" has not been filed. Failure to comply
with this provision of the Act is punishable by a fine of not more
than one hundred dollars ($100).
The Air Contaminant Emission Notice may be obtained from the
Colorado Department of Health (see below) or from any local air
pollution control agency in Colorado.
The Air Contaminant Emission Notice is to be completed in tripli-
cate and all copies mailed to:
COLORADO DEPARTMENT OF HEALTH
AIR POLLUTION CONTROL DIVISION
4210 East llth Avenue
Denver, Colorado 80220
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AIR CONTAMINANT EMISSION NOTICE
I. INSTRUCTIONS ;
A. GENERAL SOURCE INFORMATION:
To be completed in detail by all persons that are required
to file the "Air Contaminant Emission Notice. "
B . PROCEDURES :
1. The Air Contaminant Emission Notice shall be prepared
in accordance with the requirements of Section
66-31-12(2) of the Act.
"Each notice shall specify the location at which the
of the person operating or owning such facility,
process, or activity, and the nature of such facility,
process, or activity, and an estimate of the quantity
and composition of the expected emission. The Division
shall make available at all air pollution control
authority offices appropriate forms on which the infor-
mation required by this section shall be furnished."
2. The person filing the Notice shall use forms provided
by the Division in supplying the necessary information.
The person must make a reasonable effort to answer all
applicable questions and to supply any pertinent infor-
mation even though the forms and questions do not
specifically request the information.
3. If the Division finds the Emission Notice to be incom-
plete or not filed with information as required in
Section 66-31-12 of the Act, the Division may require
in writing the required information.
4. The Division may require chemical analysis of a sample
of any raw materials, fuels, or emissions which may help
determine the identity and quantity of significant air
contaminants .
C. FUEL COMBUSTION INFORMATION:
1. List the fuel used in the appropriate space provided
and the percent used for space heating and for process
heat.
2. List the type of fuel-burning equipment, collection
equipment, or control equipment used and the expected
efficiency of collection or control equipment; for
example, boiler, boiler cyclone, 80" collecting
efficiency .
3. Give rated BTU input.
4. Stack height information must be submitted.
5. Check your fuel bills for meter readings to determine
natural gas usage.
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D. BASIC PROCESS OR EQUIPMENT USED:
1. For basic process equipment, only that equipment
which is a source of air contaminant (controlled
or uncontrolled) should be listed; for example,
dryer solvent extractor, grinder, etc.
2. Under this section, list only that equipment which
is associated with, or a part of, the listed basic
process equipment in Section D.I above; for example,
boiler, kiln, scrubber, grinder, baghouse, dryer,
cyclone, solvent extractor, afterburner, etc.
3. The amount of air contaminants should be tabulated.
Where precise data is not available, an estimate
subject to later verification may be made.
E. MANUFACTURING ACTIVITIES INFORMATION:
If the reporting of raw material or product data reveals
confidential infcarnation," indicate so on the form and
submit under separate cover appropriately identified as
confidential information. Only report products manufactured
if the product results directly in the emission of an air
contaminant.
1. Principal row materials should be listed; for
example, units of rock crushed, chemicals consumed,
materials processed, etc., per year.
2. Principal products manufactured might include number
of bricks, cubic yards of concrete, barrels of fuel,
etc., produced per year.
F. REFUSE DISPOSAL INFORMATION:
Indicate the method of disposal and the amounts per year
for each method.
G. PROCESS FLOW DIAGRAM, ETC.:
May be a simple line drawing showing those points in the
process involved with the emission of air contaminant.
Indicate volumes, temperatures, and estimated quantities
of the expected emission on the diagram as well as any
supplemental information. Where space is limited submit
a key to diagram on a separate form.
H. SOLVENT EVAPORATION AND LOSSES:
List the types of solvents used and the estimated quantities
of solvents lost bo the air because of evaporation.
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AIR CONTAMINANT EMISSION NOTICE
INSTRUCTIONS
This form shall include information relating to a single stack or vent. The process, fuel, and control informa-
tion included shall relate to the emissions from this stack. Separate forms shall be filed for each stack or source
of emissions.
A. General Information:
Record the city and county where the equipment is located, number of employees, land urea, operating time, and
percent throughput.
B. Stack Information:
This information must be completed by the applicant. The stack height shall be the measured height from ground
level to the top of the stack or vent. Flow rate shall be given in actual cubic feet per minute at stack exit
temperature and pressure.
C. Fuel Information:
Type of Unit:
Design Rate:
Fuel Used:
Consumption:
Heating Value:
Percent Annual
Use:
This shall be the equipment that burns the fuel. Ex^Ti^fe : oil burner, coal burner, gas
burner, or any other unit that utilizes f>*Vl or involves combustion.
Capacity of each fuel burning equipment (BTB
Name the fuel used and print in t<^eO\a,e, in line wxth the equipment that uses the fuel.
Print the amount of fuel use^ per yeX^$ n units like tons/year, gallons/year, 106 SCF/year.
This shall be given in VfCNJi'l^C\?f fuel.
This information
D. Process Informction:
Process
Equipment:
Raw Materials,
etc.
Units/year:
Design Rate:
Finished
Products:
E. Control Equipment:
Primary.and
Secondary
Controls:
Collection
Efficiency:
Estimated
Emissions:
Method of
Estimation:
List the IT
stack or ven
e giv-En for each fuel used separately, to total 100% per year.
OCGES equipment that causes or contributes to the emissions from this
List all niaterials used during each process.
List amount of these materials used in proper units/year.
This shall be the design rate of usage of raw materials of the process equipment and shall
be given in proper units per hour.
Name the finished products from these processes and print the units/year.
All air pollution control equipment used on the emissions released by this particular stack
or vent shall be reported. When two or more controls are used, the first type of control
equipment in line will be the primary collector, and the others will be secondary controls.
This shall include the total efficiency of all the above control equipment.
This figure shall be estimated at the exit end of the stack or vent in tons/year.
(e.g., source test, emission factors, experience with similar sources, or guesswork)
This submittal should include a simple block figure flow Jugram showing all process equipment, flow of
materials, and all emission joints with emission estimates. Include manufacturers' brochures, if available.
Mail tills information to:
Air Pollution C'ontrol Division
Colorado Department of Health
42JO East llth Avenue
Denver, Colorado 80220
APC-200A (11-72-20)
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tice No.
Colorado Department of Health
AIR CONTAMINANT EMISSIONS NOTICE
Date
rm Name
il Address
ant Address
ntact Person
neral Nature of Business
Title
Zip
_Zip_
Tel
Original
Follow Up
Complaint
Inventory
New Plant
Ex. Plant
Alteration
is line for Health pept use only
UTM Coord in? tv;; •
QCR
Grid No.
Plant ID
Point ID
SIC
IPP Process
Horizontal Vertical
GENERAL
Citv County
No. Emolovees Land Area Normal Operation
% Annual Thru Put
Hr./Day I uay/Vk.
Wk./Yr.
Win.
Spr.
Sura. !rail
glitrt)
^it Diaiuoter
(ft)
Temperature °F
Flow Rate (ACFM)
Moisture Content
?ype of
Unit
Design Race
OTll/hr.
'
Fuel
Used
Consumption
Units/ Yr.
3
\
A.
^, NSi>
Heating
Value
^
^
%
Sulfur
% Annual Use
Win.
Spr.
Sun.
Fall
Sor-cc
t;3=lt
&r
P r oc: c <-• -; K n ". ; i n me n t
L-p.scrir/cion
-/^
cq
Raw Matei'^uls ,N^5A vents ,
Cleanir.^ Y^nts ,^Wc-iste
^^\>
c\ ^
> v^
0)
Units
Per Year
Design Rate
Units/Hr.
FinTS^f^ci P^CX' "^^"^
Units/Yr.
— • —
llutants
rticulate
SO
N°v
HC
CO
her
pecify)
Ty*-'-i of Control EcraipiAent
Primary
Secondary
Collection
Efficiency
Est. Emissions
Tons/Yr.
Method of
Estimation
Installation
Date
Cose
Signature of Person
Supplying Data_
COLORADO DEPAR'JKliNT OF IDiALTH
AIR POLLUTION CONTROL DIVISION
4210 E.- llth Ave.
Denver, Colorado 80220
1-303-388-6111 ext. 241
C-200A-20
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II. AUTHORITY TO CONSTRUCT:
A. GENERAL
No person shall construct or modify any new air contamination
source mentioned in II.B without receiving written authorization
from the Division.
B. Classes of machines, equipment, articles, or contrivances for
which authority is required are the following:
1. Basic equipment.
This class includes any machine, equipment, article or
other contrivance associated with operations except as
exempted in IV-A, the use of which may cause the emission
of air contaminants.
2. Air pollution control equipment:
This class includes any machine, equipment, article, or
other contrivance associated with operations or processes
except as exempted in IV.A, the use of which may eliminate
or reduce or control the emission of air contaminants.
C. Applications:
Appl' cations for authority to construct shall be prepared on
appropriate application forms supplied by the Division and
filed as outlined in IV.B.
D. Standards and Procedures for Granting or Denying Applications:
1. No authority to construct or modify shall be granted to the
applicant unless the Division determines to its satisfaction
that:
a. The new air contamination source is so designed and
will be constructed or modified to operate without
causing a violation of the emission control regulations
of the Commission, and any applicable national or
local air pollution emission control ordinances and
regulations.
b. The new air contamination source is designed, built, and
equipped in accordance with the best available practical
methods to reduce, prevent, and control air pollution.
c. The new air contamination source, as designed or modified
does not significantly endanger maintenance or attainment
as determined by criteria set forth in IV.C.2, of any
ambient air quality standards of the Commission, and any
more stringent national or local ambient air quality
standards.
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E. Conditional Approval of Applications:
1. An authority to construct or modify may be issued to an
applicant owning or operating any new air contamination
source subject to conditions which will make the equipment
operate within the emission control regulations and ambient
air quality standards of the Commission or applicable
national or local air pollution control ordinances and
regulations, and ambient air quality standards, in which
case the conditions will be specified in writing. Commencing
work under such an authority to construct shall be deemed
acceptance by the applicant of all conditions specified.
2. The Division may impose conditions upon the applicant in the
authority to construct or modify which require owners or
operators of air contamination sources to install, maintain,
and use instrumentation to monitor and record emission data
as a basis for periodic reports to the Division.
F. Expiration of Authority to Construct:
The Division may cancel an authority to construct or modify if
the construction or modification is not begun within six (6)
months from the date construction is to be started as stated
in the application, or if the work involved in the construction
or modification is suspended for six (6) months or more. An
applicant may secure an extension of the expiration date by
written request to the Division stating the reasons for the
request. Extensions may be granted for a period of not more
than six (6) months.
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III. PERMIT TO OPERATE:
A. No person shall begin operation of any new air contamination
source mentioned in II.B of this Regulation without notifying
the Division at least thirty (30) days prior to operation.
B. No person shall cause or permit the operation of any new air
contamination source mentioned in II.B of this Regulation
without applying for a permit to operate from the Division.
C. After January 1, 1975 no person shall cause or permit the use
or operation of any existing air contamination sources mentioned
in II.ii ol Lhiu j-egul^tion without first having been granted a
permit to operate from the Division.
D. The requirement for a permit to operate shall be waived during
the term of a variance.
E. No owner or operator shall cause or permit the operation of a
new or existing air contamination source if the Division denies
or revokes a permit to operate.
F. Applications:
Applications for permit to operate shall be prepared on
appropriate application forms supplied by the Division and
filed as outlined in IV.B.
G. Standards and Procedures for granting or denying Permit to Operate:
1. No permit to operate shall be granted unless the applicant
shows to the satisfaction of the Division that the emissions
of the air contamination source will satisfy the require-
ments of the emission control regulations of the Commission
or any applicable national or local air pollution control
ordinances and regulations and has been constructed,
installed, or modified in accordance with the requirements
and conditions contained in the authority to construct or
mod i fy.
2. After January 1, 1975 no existing air contamination source
shall be granted a permit to operate unless the Division
has determined to its satisfaction that said air contamination
source will operate in such a manner so as not to significantly
endanger maintenance or attainment as determined by the criteria
set forth in IV.C.2 of any ambient air quality standards of the
Commission, and any more stringent national or local ambient air
quality standards.
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3. Before a permit to operate is granted, the applicant, if
required by the Division, shall conduct performance tests
in accordance with methods approved by the Division with
the tests being made at the expense of the applicant. The
Division may monitor such required performance tests
conducted by the applicant and may also conduct performance
tests.
4. The Division may impose conditions upon the applicant in
the permit to operate which require the owners or operators
of air contamination sources to install, maintain, and use
instrumentation to monitor and record emission data as a
basis for periodic reports to the Division.
5. Prior to meeting the requirements of III.B and III.C. the
Division may grant a temporary permit to operate to new or
existing air contamination sources not to exceed six (6)
months for the purpose of developing operational procedures,
modifying equipment or facilities or to assess the impact
of emissions to meet emission control regulations, ordinances
and ambient air quality standards as determined by criteria
set forth in IV.C.2.
H. Suspension or Revocation of Permit:
1. The Division may suspend or revoke a permit to operate if
the requirements of Sections III and IX7 and any conditions
specified in the permit to operate are not met on a contin-
uous basis. Any order of the Division denying, suspending or
revoking a permit to operate shall become final within ten
(10) days from the receipt of the notice, unless the permittee
shall have made a written application to the Commission for a
hearing. The Commission may elect to refer the matter to the
Variance Board for a decision as to whether the permit shall
be granted, denied, or reinstated, or the operation be continued
under the terms and conditions of a variance.
2. Whenever an air pollution emergency has been declared the
permittee shall cease operating at such time after notice
as shall have been stated in the permit to operate. Injunctive
procedures may be instituted for failure to halt or curtail
operation within the time specified in the permit, (66-31-11(1).
3. A permit to operate which has been revoked pursuant to these
regulations shall be surrendered forthwith to the Division.
I. Renewal:
A permit to operate will be issued for a two-year period subject
to renewal.
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IV. COMMON PROVISIONS APPLICABLE TO BOTH AUTHORITY TO CONSTRUCT AND
PERMIT TO OPERATED
A. Exemptions:
An Air Contaminant Emission Notice, Authority to Construct, and
Permit to Operate shall not be required for:
1. Structures used solely as residential dwellings and
which do not exceed seven family units;
2. Retail and wholesale establishments where no processing
or incineration occurs and where solid or liquid fuel
is not burned;
3. Air conditioning or ventilating systems not designed
to remove air contaminants generated by or released
from equipment;
4. Fuel-burning equipment, other than smokehouse generators,
which use gas as a fuel having a BTU input of not more than
500,000 BTU per hour;
5. Fireplaces used for -inside or outside recreational purposes;
6. Fires used for non-commercial cooking of food for human beings;
7. The installation or alteration of an air contaminant detector,
or air contaminant recorder.
8. Laboratory equipment used exclusively for chemical or physical
analyses;
9. Flares used to indicate some danger to the public;
10. Normal agricultural cultivation operations.
11. Internal combustion engines are exempt except that emission
notices and permit to operate are required for engines of
greater than 1,000 horsepower.
12. Commercial laundries are only required to submit an air
contaminant emission notice.
13. Other sources of minor significance as specified by the Commission,
*(a) Natural gas-fired indirect heat exchangers used as
separators and known as heater treaters when used
in oil and gas field operations when sweet gas is
burned.
*(b) Multi-family dwellings, industrial and commercial
establishments, (1) which have no emissions other
than products of combustion from space heating by
the use of natural gas, and (2) where no solid or
liquid fuel is burned.
*Adopted June 8, 1972
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B. Preparing and filing an application:
1. Separate applications are required for authority to construct
or modify and permit to operate.
2. Applications shall be signed by the individual legally responsible
and authorised to do so, and he thereby covenants that the appli-
cant will ei hher construct or modify the emission source in
accordance with the requirements for granting applications as
outlined in this regulation.
3. Prior to granting an authority to construct or permit to
operate by the Division the applicant must submit, in triplicate,
Form 200A entitled, "Air Contaminant Emission Notice."
4. Each application for authority to construct shall be accompanied
by two copies of the complete data, siting (location) information,
plans, descriptions, specifications and drawings sufficient in
scope to allow an engineering evaluation to be made to determine
whether appropriate air pollution control regulations, and
ordinances and ambient air quality control standards will be met.
For certain classes of equipment, special instruction forms are
available which detail the information required. These forms can
be identified as the Form 200B series.
5. Each application for permit to operate shall be accompanied by
such performance teats results, information and records as may
be required by the Division to determine whether the requirements
of this regulation are met. Such information may also be required
by the Division at any time when the source is being operated to
determine compliance with applicable emission control regulations
and ambient air quality standards.
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C. Standards and Procedures for granting or denying applications:
1. Upon receipt and review of the application, but in no case later
than twenty (20) days, the Division shall grant or deny, or request
specific information from the applicant. Upon receipt of an appli-
cation acceptable to the Division, within (20) days the Division
shall either grant or deny permission to the applicant to construct,
modify, or operate the new source.
2. If an authority to construct or permit to operate is granted the
Division shall state, in writing, to the applicant and maintain
a record of the maximum allowable emission levels the new or
existing air contamination source must meet to comply with II.D.
1.(c), if II.D.l.(c) requires a more stringent degree of emission
control than II.D.I.(a).
3. In the event of a denial of an application the Division shall
not accept a further application unless the applicant has complied
with the objections specified as reasons for denial.
4. Prior to the applicant being notified, in writing, of denial a
conference between the Division and the applicant may be held
to discuss the reasons for denial.
5. TSio authority to construct or permit to operate shall be granted
to an applicant until the Division has determined to its satis-
faction that acceptable halt or curtailment procedures which
conform with the requirements of Section 66-31-11 of the Act have
been submitted by the applicant. Such procedures shall state the
times in which the applicant shall halt or curtail activities
upon being notified of the declaration of an air pollution emergency.
Adopted : December 9, 1971
Effective: February 1, 1972
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Emission Control Reguiations for
Existing Wigv/am Waste Burners
Colorado Air Pollution Control Commission
Adopted: May 25, 1972
Effective date: August 1, 1972
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REGULATION NO. 4
Emission Control Regulations for
Existing Wigwam Waste Burners
A. Effective August 1, 1972 through December 31, 1975, all existing
wigwam waste burners shall be exempt from the provisions of
Section I.A and II.B of Regulation No. 1 of the Commission and
this Regulation No. 4 regarding wigwam waste burners shall apply
instead. Commencing January 1, 1976, this Regulation No. 4 shall
be terminated and Sections I.A and II.B of Regulation No. 1 shall
again become effective.
B. New wigwam waste burners shall not be exempt from any portion of •
• Regulation No. 1. The definition of existing wigwam waste burners
shall include the addition of more effective devices for control-
ling air pollution to an existing wigwam waste burner; the replace-
ment of an existing burner with a burner that emits less air
contamination at the same location; or the resumption in the use
of a phased out burner provided practical alternatives to the use
of the burner do not exist.
C. No owner or operator of any existing wigwam waste burner shall
cause or permit its use or operation after August 1, 1972 without
a valid conditional permit to operate from the Division. This
permit requirement shall remain effective through December 31, 1972.
1. No conditional permit to operate shall be granted
until the applicant has clearly stated in writing
to the satisfaction of the Division, consistent
with any guidelines developed by the Division, the
optimum state of maintenance and the operating
procedures for that burner to operate so as to emit
minimum air contaminants.
2. If the Division determines that practical alternatives
to the use of a wigwam waste burner exist they may
deny the permit to operate.
3. Any failure to meet the terms and conditions of the
conditional permit to operate shall invalidate the
permit and a cease and desist order shall be issued.
D. Effective January 1, 1973 through December 31, 1975, no person
shall emit or cause to be emitted into the atmosphere, from
any existing wigwam waste burner, any air contaminant for a
period or periods aggregating more than three minutes in any
sixty (60) consecutive minutes which is of such a shade or
density as to obscure an observer's vision to a degree in
excess of 20?0 opacity. Instrumentation which results in
equivalent readings may be used in specific installations
if approved in advance by the Air Pollution Control Division.
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E. Section D shall not apply to the start-up time necessary for the
building of fires in wigwam waste burners. Start-up time shall
not exceed sixty (60) consecutive minutes, once every twenty-four
(24) hours. The Division may further limit start-up time if
practical methods exist.
F. Wood wastes shall be transported to the burner by continuous-flow
conveying methods. Continuous-flow conveying methods means the
transport of materials at uniform rates of flow, or at the rates
generated by the production process.
G. In lieu of modifying burners to meet the requirements of Section D
of this Regulation by January 1, 1973, the burner owner or operator
may elect to cease burning. If the owner or operator intends to
cease burning as opposed to meeting the opacity requirements by
January 1, 1973, the owner or operator shall submit a burning
cessation plan and schedule to the Variance Board prior to January
1, 1973, and the Variance Board may grant reasonable time, up to
one year, for burning cessation beyond January 1, 1973.
H. During September of 1972, the Division and each owner or operator
of a wigwam waste burner shall report, individually or cooperatively,
before a joint meeting of the Commission and the Air Pollution
Variance Board, the progress in meeting Section D of this Regulation
which becomes effective January 1, 1973.
I. This regulation shall not apply to the use of a wigwam waste burner
for the incineration of other than production process wood wastes.
Wigwam waste burners used in whole or in part for the incineration
of other than wood waste products shall be controlled in accordance
with Regulations No. 1 and No. 3.
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TIME SCHEDULE FOR THE IMPLEMENTATION OF REGULATION NO. 4
August 1, 1972 to December 31, 1975;
Existing wood waste burners are exempt from Section
l.A and II.B of Regulation No. 1 and Regulation
No. 4 shall apply.
August 1, 1972 to December 31, 1972;
Existing wood waste burners need a valid conditional
permit to operate.
January 1, _1973 to December 31, 1975;
Burners must meet 20% opacity except for start-up
time and three minutes in any one hour, unless the
owner chooses to cease burning.
*
January 1, 1973;
If an owner chooses to cease burning, but cannot by
this date, he may apply to the Variance Board for
auditional "reasonable" time, not to exceed one year.
September, 1972;
Joint meetings with the Commission and Variance Board
January 1, 1976:
Regulation No. 4 terminates.
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STATEMENT OF POLICY TO THE
AIR POLLUTION CONTROL DIVISION
ON
EXISTING WIGWAM WASTE BURNERS
To ease the administrative burden of granting individual
conditional permits and possible field inspections prior to the
granting of conditional permits, as required in Regulation No. 4,
permit granting guidelines may be developed by the Division in
conjunction with the Commission. These guidelines should meet
the,requirements of Section C.I of Regulation No. 4, and should
be developed by considering decisions of the Variance Board
affecting wigwam waste burners and by meeting with a represent-
ative sample of the industry affected by this regulation. These
guidelines should be available for the permit applicants by
July 1, 1972 for use in preparing their permit applications.
After January 1, 1973, when Section D of Regulation No. 4
becomes effective, the Division may allow an owner or operator
of a burner an exception above the 20*1 opacity requirement, but
only during adverse operating conditions; such as, severe weather,
and only if the burning meets the 20% opacity requirement most of
the tirnt and only if best practical controls have been installed,
properly operated and maintained.
The Division shall encourage all owners or operators contem-
plating cessation under Section G of Regulation No. 4, to complete
such plans prior to the joint meeting of the Commission and the
Variance Board scheduled for September, 1972.
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STATEMENT OF POLICY TO THE
COLORADO AIR POLLUTION VARIANCE BOARD
ON
EXISTING WIGWAM WASTE BURNERS
This Statement of Policy is to apply to the administration of
Regulation No. 4 of the Commission regarding existing wigwam waste
burners.
On May 8, 9, and 11, 1972, the Commission held public hearings
on proposed Regulation No. 4 - "Emission Control Regulations for
Wigwam Waste Burners." At these hearings, the wood products industry
opposed the use of the 20% opacity requirement, but only under adverse
operating conditions; such as, during cold weather and when wet
material must be burned. Otherwise, the proposed regulation received
favorable comment. Before adopting this regulation, the Commission
considered some of the information presented to the Variance Board by
the wood products industry, and in addition, contacted the State air
pollution control programs of Arizona, Montana, New Mexico, Oregon,
and Idaho regarding wigwam waste burners and their control. It is the
conclusion of the Commission that Regulation No. 4 as adopted, takes
into account the economical and technological achievability by the
wood products industry, and is necessary to obtain better air quality
in Colorado, considering the number of burners in operation.
One of the main considerations in adopting Regulation No. 4 was
to avoid the necessity of having to cite each violation with subsequent
hearings before the Variance Board. The Variance Board has consumed
much of its time on wigwam waste burner hearings and the Commission
intends, pursuant to Regulation ?To. 4, to allow time, through regulation,
for burner owners or operators to design, construct, and make operational,
adequate control systems.
THEREFORE, THE COMMISSION RESOLVES THAT IF AN OWNER OR OPERATOR
OF A WIGWAM WASTE BURNER REQUESTS A VARIANCE FROM REGULATION
NO. 4 AFTER JANUARY 1, 1973, SAID VARIANCE SHALL ONLY BE GRANTED
FOR A SITUATION BEYOND THE REASONABLE PLANNING CAPABILITY OR THE
CONTROL OF SAID OWNER OR OPERATOR.
The purpose of the joint meeting September, 1972 is for:
1) determining the progress that the owners or
operators have made to meet the January 1,
1973 requirements on schedule,
2) determining whether the owners or operators
are making a good faith effort to meet the
requirements, and
3) determining the adequacy of Regulation No. 4
to achieve good air quality in the vicinity
of wigwam waste burners.
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REGULATION MO. 5
Emission Control Regulations for
Existing Alfalfa Dehydration Plants
Colorado Air Pollution Control Commission
Adopted: June 8, 1972
Effective date: August 1, 1972
E-59
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REGULATION NO. 5
Emission Control Regulations for
Existing Alfalfa Dehydration Plants
A. Effective August 1, 1972 through April 30, 1973, all existing alfalfa
dehydration plants shall be exempt from the provisions of Section I.A
of Pegulation No. 1 of the Commission and this Regulation No. 5,
regarding alfalfa dehydration plants, shall apply instead. Commencing
May 1, 1973, this Regulation No. 5 shall be terminated and Section I.A
of Regulation No. 1 shall again become effective.
B. No owner or operator of any alfalfa dehydration plant shall cause or
permit the use or operation of any existing air contamination source
within that plant after August 1, 1972 without having a valid conditional
permit to operate from the Division, This permit requirement shall remain
effective through April 30, 1973.
1. No conditional permit to operate shall be granted until
the applicant has clearly stated in writing to the
satisfaction of the Division, consistent with any guide-
lines developed by the Division, the optimum state of
maintenance and the operating procedures for that source
to operate so as to emit minimum air contaminants.
2. Any failure to meet the terms and conditions of the
conditional permit to operate shall invalidate the
permit and a cease and desist order shall be issued.
C. During September of 1972 and March of 1973, the Division and each alfalfa
dehydration plant owner or operator shall report, individually or cooper-
atively, before a joint meeting of the Commission and the Air Pollution
Variance Board, the progress in meeting Section I.A of Regulation No. 1
of the Commission which becomes effective May 1, 1973.
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STATEMENT OF POLICY TO THE
AIR POLLUTION CONTROL DIVISION
ON
EXISTING ALFALFA DEHYDRATION PLANTS
To ease the administrative burden of granting individual
conditional permits and possible field inspections prior
to granting of conditional permits as required in Regu-
lation No. 5, permit granting guidelines may be developed
by the Division in conjunction with the Commission.
These guidelines should meet the requirements of Section
B.I of Regulation No. 5 and should be developed by meet-
ing with a representative sample of the industry affected
by this Regulation. These guidelines should be available
for the permit applicants by July 1, 1972 for use in pre-
paring their permit applications.
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STATEMENT OF POLICY TO THE
COLORADO AIR POLLUTION VARIANCE BOARD
ON
EXISTING ALFALFA DEHYDRATION PLANTS
This Statement of Policy is to apply to the administration of
Regulation No. 5 of the Commission regarding existing alfalfa dehydration
plants.
On May 8, 9, and 11, 1972, the Commission held public hearings on
proposed Regulation No. 5 - "Emission Control Regulations for Alfalfa
Dehydration Plants." In addition to information the Commission received
at hearings, other information on the control of emissions from these
plants has been submitted to the Commission by the alfalfa dehydration
industry and the Division. The alfalfa dehydration industry did not
oppose the proposed Regulation No. 5 at these public hearings. It is the
conclusion of the Commission that Regulation No. 5 as adopted, takes into
account the economical and technological achievability by the alfalfa
dehydration industry and is necessary in obtaining better air quality in
Colorado.
In adopting Regulation No. 5, the Commission's action was based upon
certain considerations which include:
1) allowing the industry to experiment with various air
pollution control systems during the 1972 growing
season and have adequate control systems installed
by May 01: 1973 so as to comply with Regulation No. 5
on schedule, and
2) avoiding the necessity of having to cite each violation
with subsequent hearings before the Variance Board.
THEREFORE, THE COMMISSION RESOLVES THAT IF AN OWNER OR OPERATOR
OF AN ALFALFA DEHYDRATION PLANT REQUESTS A VARIANCE FROM REGU-
LATION NO. 5 AFTER MAY 1, 1973, SAID VARIANCE SHALL ONLY BE
GRANTED FOR A SITUATION BEYOND THE REASONABLE PLANNING CAPABILITY
OR CONTROL OF SAID OWNER OR OPERATOR.
The purpose of the joint meetings September 1972 and March 1973 is for:
1) determining the progress that the owners or operators
have made to meet the May 1, 1973 requirements on
schedule,
2) determining whether the owners or operators are making
a good faith effort to meet the requirements, and
3) determining the adequacy of Regulation No. 5 to achieve
good air quality in the vicinity of alfalfa dehydration
plants.
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Regulation No. 6
Standards of Performance for
New Stationary Sources
Colorado Air Pollution Control Commission
Effective: May 1,1973
E-63
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REGULATION NO. 6
STANDARDS OF PERFORMANCE FOR NEW STATIONARY SOURCES
The Standards of Performance for New Stationary Sources within the
State of Colorado are set forth and published in Volume 36, Number
247, Part II of the Federal Register, dated December 23, 1971, with
the following amendments and exceptions thereto:
(a) The word "Administrator" as used therein shall
mean the Air Pollution Control Division of the
Colorado Department of Health or its authorized
representative.
(b) The words "Environmental Protection Agency" as
used therein shall mean the Colorado Air Pollution
Control Commission.
(c) Section numbered 60.10 contained therein shall be
deleted in its entirety.
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RULES AND REGULATIONS
Title 40—PROTECTION OF
ENVIRONMENT
Chapter I—Environmental Protection
Agency
SUBCHAPTER C—AIR PROGRAMS
PART 60—STANDARDS OF PERFORM-
ANCE FOR NEW STATIONARY
SOURCES
On August 17, 1971 (36 F.B. 15704)
pursuant to section 111 of the Clean Air
Act as amended, the Administrator
proposed standards of performance for
steam generators, Portland cement
plants, incinerators, nitric acid plants,
and sulfuric acid plants. The proposed
standards, applicable to sources the con-
struction or modification of which was
initiated after August 17, 1971, included
. emission limits for one or more of four
pollutants (participate matter, sulfur
dioxide, nitrogen oxides, and sulfuric
acid mist) for each source category. The
proposal included requirements for per-
formance testing-, stack gas monitoring,
record keeping and reporting, and pro-
cedures by which EPA will provide pre-
construction review and determine the
applicability of the standards to specific
sources.
Interested parties were afforded an
opportunity to participate in the rule
making by submitting comments. A total
of more than 200 interested parties, in-
cluding Federal, State, and local agen-
cies, citizens groups, and commercial nnd
industrial organizations submitted com-
ments. Following a review of the pro-
posed regulations and consideration of
the comments, the regulations, includ-
ing the appendix, have been revised and
are being 'promulgated today. The prin-
cipal revisions are described below:
1. Particulate matter performance
testing procedures have been revised to
eliminate the requirement for impingers
in the sampling train. Compliance will be
based only on material collected in the
dry filter and the probe preceding the
filter. Emission limits have been adjusted
as appropriate to reflect the change in
test methods. The adjured standards re-
quire the same degree of particulate con-
trol as the originally proposed standards.
2. Provisions have been added whereby
alternative test methods can be used to
determine compliance. Any person who
proposes the use of an alternative
method will be obliged to provide evi-
dence that the alternative method is
equivalent to the reference method.
3. The definition of modification, as it
pertains to increases m production rate
and changes of fuels, has been clarified.
Increases in production rates up to design
capacity will not be considered a modifi-
cation nor will fuel switches if the equip-
ment was originally designed to accom-
modate such fuels. These provisions will
eliminate inequities where equipment had
been put into partial operation prior to
the proposal of the standards.
4. The definition of a new source was
clarified to include construction which
is completed within an organization as
well as the more common situations
where the facility is designed and con-
structed by a contractor.
5. The provisions regarding requests
for EPA plan review and determination
of construction or modification have been
modified to emphasize that the submittal
of such requests and attendant informa-
tion is purely voluntary. Submittal of
such a request will not bind the operator
to supply further information; however,
lack of sufficient information may pre-
vent the Administrator from rendering
an opinion. Further provisions have been
added to the effect that information sub-
mitted voluntarily for such plan review
or determination of applicability will be
considered confidential, if the owner or
operator requests such confidentiality.
6. Requirements for notifying the Ad-
ministrator prior to commencing con-
struction have been deleted. As proposed,
the provision would have required notifi-
cation prior to the signing of a contract
for construction of a new source. Owners
and operators still will be required' to
notify the Administrator 30 days prior to
initial operation and to confirm the
action within 15 days after startup.
7. Revisions were incoporated to per-
mit compliance testing to be deferred up
to 60 days after achieving the maximum
production rate but no longer than 180
days after initial startup. The proposed
regulation could have required testing
within 60 days after startup but defined
startup as the beginning of routine
operation. Owners or operators will be
required to notify the Administrator at
least 10 days prior to compliance testing
so that an EPA observer can be on hand.
Procedures have been modified so that
the equipment will have to be operated
at maximum expected production rate,
rather than rated capacity, during com-
pliance tests.
8. The criteria for evaluating perform-
ance testing results have been simplified
to eliminate the requirement that all
values be within 35 percent of the aver-
age. Compliance will be based on the
average of three repetitions conducted in
the specified manner.
9. Provisions were added to require
owners or operators of affected facilities
to maintain records of compliance tests,
monitoring equipment, pertinent anal-
yses, feed rates, production rates, etc. for
2 years and to make such information
available on request to the Administra-
tor. Owners or operators will be required
to summarize the recorded data daily
and to convert recorded data into the
applicable units of the standard.
10. Modifications v/ere made to the
visible emission standards for steam.
generators, cement plants, nitric acid
plants, and sulfuric acid plants. The
Rmgelmann standards have been de-
leted; all limits will be based on opacity.
In every case, the equivalent opacity will
bo at least as string-ent as the proposed
Ringelmann number. In addition, re-
quirements have been altered for three
of the source categories so that allowable
emissions will be less than 10 percent
opacity rather than 5 percent or loss
opacity. There were many comments
that observers could not accurately
evaluate emissions of 5 percent opacity.
In addition, drafting errors in the pro-
posed visible emission limits for cement
kilns and steam generators were cor-
rected. Steam generators will be limited
to visible emissions not greater than 20
percent opacity and cement kilns to not
greater than 10 percent opacity.
11. Specifications for monitoring de-
vices were clarified, and directives for
calibration were included. The instru-
ments are to be calibrated at least once
a day, or more often if specified by the
manufacturer. Additional guidance on
the selection and use of such instruments
will be provided at a later date.
12. The requirement for sulfur dioxide
monitoring at steam generators was
deleted for those sources which will
achieve the standard by burning low-sul-
fur fuel, provided that fuel analysis is
conducted and recorded daily. American
Society for Testing and Materials
sampling techniques are specified for
coal and fuel oil.
13. Provisions were added to the steam
generator standards to cover those in-
stances where mixed fuels are burned.
Allowable emissions will be determined
by prorating the heat input of each fuel,
however, in the case of sulfur dioxide, the
provisions allow operators the option of
burning low-sulfur fuels (probably
natural gas) as a means of compliance.
14. Steam generators fired with lignite
have been exempted from the nitrogen
oxides limit. The revision was made in
view of the lack of information on some
types of lignite burning. When more in-
formation is developed, nitrogen oxides
standards may be extended to lignite
fired steam generators.
15. A provision was added to make it
explicit that the sulfuric acid plant
standards will not a,pply to scavenger
acid plants. As stated in the background
document, APTD 0711, which was issued
at the time the proposed standards were
published, the standards were not meant
to apply to such operations, e.g., where
sulfuric acid plants are used primarily
to control sulfur dioxide or other sulfur
compounds which would otherwise be
vented into the atmosphere.
1G. The regulation has been revised
to provide that all materials submitted
pursuant to these regulations will be di-
rected to EPA's Office of General En-
forcement.
17. Several other technical changes
have also been made. States and inter-
ested parties are urged to make a careful
reading of these regulations.
As required by section 111 of the Act,
the standards of perfonnance promul-
gated herein "reflect the degree of emis-
sion reduction which (taking into ac-
count the cost of achieving such reduc-
tion) the Administrator determines has
been adequately demonstrated". The
standards of performance are based on
stationary source testing conducted by
the Environmental Protection Agency
and'or contractors and on data derived
from various other sources, including the
available technical hteriture. In the com-
ments on the proposed standards, many
questions were raised as to costs and
FEDERAL REGISTER, VOL. 36, NO. 247—THURSDAY, DECEMBER 23, 1971
E-65
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RULES AND REGULATIONS
demonstrated capability of control sys-
tems to meet the standards. These com-
ments have been evaluated and investi-
gated, and it is the Administrator's
judgment that emission control systems
capable of meeting the standards have
been adequately demonstrated and that
the standards p-omuleatcd herein are
achievable at reasonable costs.
The regulations establishing standards
of performance for steam generators, in-
cinerators, cement plants, nitric acid
plants, and sulluric acid plants are here-
by promulgated effective on publication
and apply to sources, the construction or
modification of which was commenced
after August 17, 1971.
Dated: December 16, 1971.
WILLIAM D. RUCKELSHATJS,
Administrator,
Environmental Fromciion Agency.
A new Part 60 is added to Chapter I,
Title 40, Code of Federal Regulations, as
follows:
Subport A—General Provisions
See.
601 Applicability.
60.2 Delinltlons.
60.3 Abbreviations.
60.4 Address.
60.5 Determination of construction or
modification.
60.6 Review of plans.
60.7 Notification and recordkeeping.
60.8 Performance tests.
60.9 Availability of Information.
60.10 State authority.
Subpart D—Standards of Performance for
Fossil Fuel-Fired S'eam Generators
60.40 Applicability and resignation of af-
fected facility.
60.41 Definitions.
60.42 Standard lor particulatc matter.
O0.43 Standard for e-ulfur dioxide.
60.44 Standard for nltropen oxides.
60.45 Emission and fiiel monitoring.
60.46 Test methods and procedures.
Subpart E—Standards of Performance for
Incinerators
60.50 Applicability and designation of af-
fected facility.
60.51 Definitions.
60.62 Standard for participate matter.
60.53 Monitoring of operations.
60.54 Test methods and procedures.
Subpart f—Standards of Performance for
Portland Cement Plants
60.60 Applicability and designation of
affected facility.
60.61 Definitions.
60.62 Str.-idard for participate matter.
60,63 Monitoring of operations.
60.64 Test methods and procedures.
Subpart G—Standards of Performance for Nitric
Acid Plants
60.70 Applicability and designation of af-
fected facility.
60.71 Definitions.
60.72 Standard for nitrogen oxides.
60.73 Emission monitoring.
60.74 Test methods and procedures.
Subpart H—Standards of Performance for Sulfuric
Acid Plants
60.80 Applicability aud designation of »t-
fected facility.
00.81 Definitions.
Sec.
GO 82
60.83
CO 84
6085
Standard for sulfur dioxide.
Standard for acid mast.
Emission monitoring.
Test methods and procedures.
APPENDIX—TEST METHODS
Method 1—Sample and velocity traverses for
stationary sourcos
Method 2—Determination of stack gas veloc-
ity and volumetric flow rate (Type S
pitot tube).
Method 3—Gas analysis for carbon dioxide,
excels air, and dry molecular weight.
Method 4—Determination cf moisture In
stack gases.
Method 5—Determination of partlculate
emissions from stationary sources.
Method G—Determination of sulfur dioxide
emissions from stationary sources.
Method 7—Determination of nitrogen oxide
emissions from stationary sources.
Method 8—Determination of sulfurlc acid
mist and sulfur dioxide emissions
from stationary -ouices.
Method 9—Visual determination of the opac-
ity of emissions from stationary
sources.
AUTHORITY: The provisions of this Part 60
Issued under sections 111, 114, Clean Air Act;
Public Law 91-604, 81 Stat. 1713.
Subpart A—General Provisions
§ 60.1 Applicability.
The provisions of this part apply to
the owner or operator of any stationary
source, which contains an affected facil-
ity the construction or modification of
which is commenced after the date of
publication in this part of any proposed
standard applicable to such facility.
§ 60.2 Definitions.
As used in this part, all terms not
deiined herein snail have the meaning
given them in the Act:
(a) "Act" means the Clean Air Act
(42 U.S.C. 1857 et seq., as amended by
Public Law 91-C04, 84 Stat. 1676).
(b) "Administrator" means the Ad-
ministrator of the Environmental Pro-
tection Agency or his authorized repre-
sentative.
(c) "Standard" means a standard of
performance proposed or promulgated
under this part.
(d) "Stationary source" means any
building, structure, facility, or Installa-
tion which emits or may emit any air
pollutant.
(e) "Affected facility" means, with
reference to a stationary source, any ap-
paratus to which a standard is applicable.
(f) "Owner or operator" means any
person who owns, leases, operates, con-
trols, or supervises an affected facility
or a stationary source of which an af-
fected facility is a part.
(g) "Construction" means fabrication,
erection, or installation of an affected
facility.
(h) "Modification" means any physical
change in, or change in the method of
operation of, an affected facility which
increases the amount of any air pol-
lutant (to which a standard applies)
emitted by such facility or which results
in the emission of any air pollutant (to
which a standard applies) not previously
emit ',;, except that:
(1) Routine maintenance, repair, and
replacement shall not be considered
physical changes, and
(2) The following shall not be consid-
ered a change in the method of
operation:
(i) An increase in the production
rate, if such increase does not exceed the
operating design capacity of the affected
facility;
di) An increase in hours of operation;
(iii) Use of an alternative fuel or raw
material if, prior to the date any stand-
ard under this part becomes applicable
to such facility, as provided by § 60.1,
the affected facility is designed to ac-
commodate such alternative use.
(i) "Commenced" means that an own-
er or operator has undertaken a con-
tinuous program of construction or
modification or that an owner or opera-
tor has entered into a binding agree-
ment or contractual obligation to under-
take and complete, within a reasonable
time, a continuous program of construc-
tion or modification.
(j) "Opacity" means the degree to
which emissions reduce the transmission
of light and obscure the view of an object
in the background.
(k) "Nitrogen oxides" means all ox-
ides of nitrogen except nitrous oxide, as
measured by test methods set forth in
this part.
(1) "Standard of normal conditions"
means 70° Fahrenheit (21.1° centi-
grade) and 29.92 in. Hg (760 mm. Hg).
(m) "Proportional sampling" means
sampling at a rate that produces a con-
stant ratio of sampling rate to stack gas
flow rate.
(n) "Isokinetic sampling" means
sampling in which the linear velocity of
the gas entering the sampling nozzle is
equal to that of the undisturbed gas
stream at the sample point.
(o) "Startup" means the setting in
operation of an affected facility for any
purpose.
§ 69.3 Abbreviations.
The abbreviations used In this part
have the following meanings In both
capital and lower case:
B.t.u —British thermal unit.
cal.—calorie(s).
c.f.m.—cubic feet per minute.
COj—carbon dioxide.
g.—gram(s).
gr.—grain (s).
ing.—milligram(s).
mm —millimeter (s).
1.—liter(s).
nm.—nanometcr(s), —10-' meter.
Ag.—microgram(s), lO-8 gram.
Hg.—mercury.
In.—inch (ee).
K—1,000.
Ib.—pound (s).
ml.—mllliliter(s).
No.—number.
%—percent.
NO—nitric oxide.
NCX—nitrogen dioxide.
NO^—nitrogen oxides.
NM i—normal cubic meter.
s.cJ.—standard cubic feet.
SO,—sulfur dioxide.
H..SO,—sulfnrlc acid.
SO,—sulfur trioxide.
FEDERAL REGISTER, VOL. 36, NO. 247—THURSDAY, DECEMBER 73, 1971
E-66
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RULES AND REGULATIONS
It1—cubic feet.
ft.5—square Icet.
inin.—minutc(6).
hr.—hour(u).
§ 60.1 Address.
All applications, requests, submissions,
and reports under this part shall be sub-
mitted in triplicate and addressed to the
Environmental Protection Agency, Oifica
of General Enforcement, Waterside Mall
SW., Washington, DC 20460.
§ 60.5 Determination of construction or
modification.
When requested to do so by an owner
or operator, the Administrator will ma'.ve
a determination of whether actions taken
or intended to be token by such owner or
operator constitute construction or modi-
fication or the commencement thereof
within the meaning of this part.
§("•0.6 Review of plans.
(a) When requested to do so by an
owner or operator, the Administrator will
review plans for construction or modifi-
cation for the purpose of providing
technical advice to the owner or operator.
(b) (1) A separate request shall be
submitted for each pfleeted facility.
(2) Each request shall A notification of the actual date
of initial startup of an affected facility
within 15 days after such date.
(b) Any owner or operator subject to
the provisions of this part shall maintain
for a period of 2 years a record of the
occurrence and duration of any startup,
shutdown, or malfunction in operation of
any affected facility.
§ 60.8 Performance teMs.
(a) Within GO days after achieving the
maximum production rate at which the
affected facility will be operated, but not
later than 180 days after initial startup
of such facility and at such other times
as may be required bv the Administrator
under section 1M of the Act, ulie owner
or operator of such facility shall conduct
performance tesUs) and furnish the Ad-
ministrator a written report of the results
of such performance test(s).
(b) Performance tests shall be con-
ducted and results reported in accord-
ance with the test method set forth in
this part or equivalent methods approved
by the Administrator; or where the Ad-
ministrator determines that emissions
from the affected facility are not sus-
ceptible of bsing measured by such
methods, the Administrator shall pre-
scribe alternative test procedures for
determining compliance with the re-
quirements of this part.
(c) The owner or operator shall permit
the Administrator to conduct perform-
ance tests at any reasonable time, shall
cause the affected facility to be operated
for purposes of such tests under such
conditions as the Administrator shall
specify based on repiescmative perform-
ance of the affected facility, and shall
make available to the Administrator
suth records as may be necessary to
determine such performance.
The owner or operator of an
affected facility shall provide the Ad-
mmistiator 10 days prior notice of the
performance test to afford the Admin-
istrator tile opportunity to have an ob-
server present
ic' The owner or operator of an
affeciM facility shall provide, orc-iu.se to
be provided, perfoimance testing facil-
ities as follows:
'!> ^ampluig pork Pdequal? for test
methods applicable to such facility.
12> Safe sampling platform is).
• 3 Safe access to sampling plat-
form (si.
(4 Tjiihties for sampling and testing
equipment.
(f> Each performance teot shall con-
si.--1, of three repetitions of the applicable
test method. For the purpose of deter-
mining compliance with an applicable
slandaid of performance, the average of
results of all repetitions shall apply.
§ 60,9 A\ail.iliility of information.
(a) Emission data provided to, or
otherwise obtained by, the Administra-
tor in accordance with the provisions of
this part shall be available to the public.
' b i Except PS provided in paragraph
(a) of this section, any records, reports.
or information provided to, or otherwise
obtained by, the Administrator in accord-
ance with the provisions of this part
shall be available to the public, except
that (1) upon a showing satisfactory to
the Administrator by any person that
such records, reports, or information, or
particular part thereof (other than
emission data), if made public, would
divulge methods or processes entitled to
protection as trade secrets of such per-
son, the Administrator shall consider
such records, reports, or information, or
particular part thereof, confidential in
accordance with the purposes of section
1905 of title 18 of the United States
Code, except that such records, reports,
or information, or particular part there-
of, may be ' "--losM t.i o^h^r facers, «a-
ployrt-s, or tsuthwised rcprct-ew.itlves of
the United States concerned with catry-
ing out the provisions of the Act or v hen
relevant in any proceeding under the
Act; and (2) information received by the
Administrator solely for the purpore.s 01
§560.5 and 60.6 shall not be disclosed
if it is identified by the owner or opera-
tor as being a trade secret or cvn:-
mercial or financial information which
such owner or operator considers
confidential.
Subparl D—Standards of Performance
for Fossil-Fuel Fired Steam Generators
§ 60. JO Applicability and designation of
all'eried facility.
The provisions of this subpart are ap-
plicable to each fossil fuel-fired steam
generating unit of more than 250 million
B.t.u. per hour heat input, which is the
affected facility.
§60.11 Definitions.
As used in this subpart, all terms net
defined herein shall have the meaning
given them in the Act, and in Subpart
A of this part.
i a) "Fossil fuel-fired steam generat-
ing unit" means a furnace or boiler used
:n the process of burning fossil fuel
for the primary purpose of producing
steam by heat transfer.
(b) ''Fossil fuel" means natural gas,
petroleum, coal and any form of solid,
liquid, or gaseous fuel derived from
such materials.
(c) "Particulate matter" means any
finely divided liquid or solid material,
other than uncombined water, as meas-
uied by Method 5.
§ 60.42 Standard for particulale matter.
On and after the date on which the
performance test required to be con-
ducted by § 60.8 is initiated no owner
or operator subject to the provisions of
this part shall discharge or cause the
discharge into the atmosphere of par-
ticulate matter which is:
(a) In excess of 0.10 Ib. per million
B.t.u. heat input (0.18 g. per million cal )
maximum 2-hour average.
(b) Greater than 20 percent opacity,
except that 40 percent opacity shall be
permissible for not more than 2 minutes
in any hour.
(c) Where the presence of uncom-
bined water is the only reason for fail-
ure to meet the requirements of para-
graph (b) of this section such failure
shu.ll not be a violation of this section.
FEDERAL REGISTER, VOL. 36, NO. 247—THURSDAY, DECEMBER 23, 1971
E-67
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RULES AND REGULATIONS
§ 60.43 Stamford for sulfur dioxide.
On and after the date on which the
performance test required to be con-
ducted by § 60.8 is initiated no owner
or operator subject to the provisions
of this part shall discharge or cause the
discharge into the atmosphere of, sulfur
dioxide in excess of:
(a) 0.80 Ib. per million B.t.u. heat in-
put (1.4 g. per million cal.), maximum 2-
hour average, when liquid fossil fuel is
burned.
(b) 1.2 IDS. per million B.t.u. heat input
(2.2 g. per million cal.), maximum 2-
hour average, when solid fossil fuel is
burned.
(c) Where different fossil fuels are
burned simultaneously in any combina-
tion, the applicable standard shall be
determined by proration. Compliance
Phpll he determined using the following
formula :
y (0.80) 42(1.2)
•where:
x is the percent of total heat input derived
Irom gaseous fossil fuel and,
y is the percent of total heat input derived
from liquid fossil fuel and,
z is the percent of total heat input derived
from solid fossil fuel.
§ 60.1 1 Standard for nitrogen oxides.
On and after the date on which the
performance test required to be con-
ducted by § 60.8 is initiated no owner or
operator subject to the provisions of this
part shall discharge or cause the dis-
charge into the atmosphere of nitrogen
oxides in excess of:
(a) O.SO Ib per million B.t.u. heat in-
put (0.36 g. per million cal.) , maximum
2-hour average, expressed as NO.., when
gaseous fossil fuel is burned.
(b) 0.30 Ib. per million B.t.u. heat in-
put (0.54 g. per million cal.), maximum
2-hour average, expressed as NO., when
liquid fossil fuel is burned.
(c) 0.70 Ib. per million B.t.u. heat in-
put (1.26 g. per million cal.), maximum
2-hour average, expressed as NO^ when
solid fossil fuel (except linrute) is burned.
(d) When different fossil fuels are
bumed simultaneously in any combina-
tion the applicable standard shall be de-
termined by proration. Compliance shall
be determined by using the following
formula :
x(o 20H-y(o 30 H Z(°j2£l
x + y-fz
where :
x is the percent of total heat input derived
from gaseous fossil fuel and,
y is the percent of total heat inpvit derived
from liquid fossil fuel and,
z is the percent of total heat input derived
from solid fossil fuel.
§60.13 Kmi>Mon and fuel inoniloriiifr.
(a) There shall be installed, cali-
brated, maintained, axid operated, in any
fossil fuel-fired steam generating unit
subject to the provisions of this part,
emission monitoring instruments as
follows:
(1) A photoelectric or other type
smoke detector and recorder, except
where gaseous fuel is- the only fuel
burned.
(2) An instrument for continuously
monitoring and recording sulfur dioxide
emissions, except where gaseous fuel is
the only fuel burned, or where compli-
ance is achieved through low sulfur fuels
and representative sulfur analysis of
fuels are conducted daily in accordance
with paragraph (c) or (d) of this section.
c^'i An instrument for continuously
monitoring and recording emissions of
nitrogen oxides.
(b) Instruments arid sampling systems
installed and used pursuant to this sec-
tion shall be capable of monitoring emis-
sion levels within _:20 percent with a
confidence level of 95 percent and shall
be calibrated m accordance with the
method (s) prescribed by the manufac-
ttirer(s) of such instruments; instru-
ment.-; shall be rubje'.-tfd to manufactur-
ers recommended zero adjustment and
calibration procedures at least oner- per
24-hour operating period unless the man-
ufacturer^) specifics or recommends
calibration at shorter intervals, in which
case such specifications or recommenda-
tions shall be followed. The applicable
method specified in the appendix of this
part shall be the reference method.
(c) The sulfur content of solid fuels,
as burned, shall be determined in accord-
ance with the following methods of the
American Society for Testing and
Materials.
(\~< Mechamr-al sampling by Method
D 2231065.
(2) Sample preparation by Method D
2013-65.
(3) Sample analysis by Method D
271-63.
(d) The sulfur content of liquid fuels,
as burned, •shall be determined m accord-
ance with the Aincnc °n Society lor I eat-
ing and Materials Methods D 1551-68, or
D 129-Gt, orD 1552-C1.
(e) The rate of fuel burned for each
fuel shsll be measured daily or at shorter
intervals and recorded. The heating
value and ash content of fuels shall be
ascertained at l?ast once per week and
recorded. Where the steam generating
unit is used to generate electricity, the
average electrical output and the mini-
mum and maximum hourly generation
rate shall be measured and recorded
daily.
For each repetition, the average
concentration of particulate matter shall
be determined by using Method 5.
Traversing during sampling by Method 5
shall be according to Method 1. The
minimum sampling time shall be 2 hours,
and minimum sampling volume shall be
60 ft." corrected to standard conditions
on a dry basis.
(2) For each repetition, the SO. con-
centration shall be determined .by using
Method 6. The sampling site shall be the
same as for determining volumetric flow
rate. The sampling point in the duct
shall be at the centroid of the cross
section if the cross sectional area is less
than 50 ft.5 or at a point no closer to the
walls than 3 feet if the cross sectional
area is 50 ft." or more. The sample shall
be extracted at a rate proportional to the
gas velocity at the sampling point. The
minimum sampling time shall be 20 min.
and minimum sampling volume shall be
0.75 ft.' corrected to standard conditions.
Two samples shall constitute one repeti-
tion rnd shall be taken at 1-hour
intervals.
'3) For each repetition the NO, con-
centration shall be determined by usim;
Method 7. The sampling site and point
shall be the 5-ame as for SO... The sam-
pling time shall be 2 hours, and four
samples shall be taken at 30-minute
intervals.
(4) The volumetric flow rate of the
total effluent shall be determined by using
Method 2 and traversing according to
Method 1. Gas analysis shall be per-
formed by Method 3, and moisture con-
tent shall be determined by the con-
denser technique of Method 5.
(d) Heat input, expressed in B.t u. per
hour, shall be determined during each 2-
hour testing period by suitable fuel flow
meters and shall be confirmed by a ma-"
terial balance over the steam generation
system.
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RULES AND REGULATIONS
<2) For SO', C--SO-. concentration in
lh.,ft,.\ ara"japh (e> (2> of this section, cor-
rected l.o standard condition",, dry basis.
Ci) For NCK, c NO, concentrntion in
Ib. It.3, a., determined in accordance with
para^iaph (cM,J> ol tliis section, cor-
rected to standard conditions, dry basis.
Subpciil E — Stcindcrds of Performance
for Incineiators
§ 60. .^0 .Vpplir.'.iiilily and de^ijinntion of
all cried 1'aciiilj .
The provisions of this subpart are ap-
plicable to each incinerator of more than
50 tons I't-r day charging rate, which is
the a fleeted facility.
As used in this subpart, all terms not
defined herein shall have the meaning
given them in the Act and in Subpart A
of this part.
(a) "Incinerator" means any furnace
used in the process of burning solid waste
for the primary purpose of reducing the
volume of the waste by removing com-
bustible matter.
(b) "Solid waste" means refuse, more
than 50 percent of which is municipal
type waste consisting' of a mixture of
paper, v.-ood, yard wastes, food wastes,
pla-s'ics, leather, rubber, and other com-
bustibles, and nonccmbustible materials
such as ulass and rock.
Cc)"Day" means 24 hours.
(d) "Particulate matter" means any
fineiy divided liquid or solid material,
other than imcGrr.bmod water, v^ meas-
ured by Method 5.
§ 60.32 Slamlard for jiiirliciilale matter.
On and after the ctote on which the
performance test reoM'-ed to be con-
ducted by § 60.8 is initiated, no owner
nr oreiT.tor subject to th 3 provisions of
this part fc.lit.ll discharge or cause the
dischaitie into the atmosphere of par-
ticulate matter which is 111 excess of 0 03
gr./s.c.f. (0.18 g./NM") corrected to 12
percent CO_., maximum 2-hour average.
§ 60. ,~,3 M'KJ'loriiigr of o->cra!ion-..
Tlie owner or operator of any In-
cinerator subject to the provisions of this
part sliill maintain a file of c^.ily burn-
ing rates and ho'j-s of operation aru: r.ny
particulfile emission measureiaents. The
burning rates and hours of operation
shall be summr.rizod monthly The
record <;0 and summary shall be retained
for at least 2 ycrrs f.-liowm~ the date of
such records and sum manes.
§ 60..* !• Trst nu'tliotls nnd procedures.
(a) The provisions of this section arc
applicable to performance tests for de-
termining emissions of participate matter
from incinerators.
(b) All p.'iioimance tests shall be
conducted v.hile the affected facility is
opera tin? at or above the maximum
refu=e charging rate at which such facil-
ity will be operated and the solid waste
burned shall be representative of normal
operation and under such other relevant
conditions as the Administrator shall
specify based on representative per-
formance of the ndected facility
(c) Test methods set foith in the ap-
pendix to this part or equivalent methods
approved by the Administrator shall be
used as follows:
CD For each repetition, the average
concentration of particulate matter shall
bo detenvjned by using Method 5. Tra-
versing dvinn" sampling by Method 5
shall be according to Method 1. The mini-
mum sampling t'rr.c shall be 2 hours and
the mirnuru'n sampling volume sbaii be
GO ft.3 coirected to standard conditions
on a drv basis.
(2) Gai, analysis shall be performed
uiing the integrated sample techmoue of
Method 3, and moisture content shall be
determined by the condenser technique
of Method 5. If a wet scrubber is used,
tho gas analysis sample shall reflect flue
gas conditions niter the scrubber, allow-
ing- for the effect of carbon dioxide ab-
sorption.
'd) For each repetition particulate
matter emissions, expressed in gr./s.c.f.,
shr.ll be determined in accordance with
paragraph (c) (1) of this section cor-
rected to 12 p?reent CO,, dry basis.
Subparf F—Standards of Performance
for Portland Cement Fiants
§ 60.60 Ar.V'JicflfoilHy and designation of
aSi'ccUMi facility.
The provisions of the subpart are ap-
plicable to the following affected facili-
ties in Portland cement plruts: kiln,
clinker cooler, raw mill s>si-jro, finish
null sy.-tcm, rav; i:nil dryer, rav,' material
storage, clinker storage, firushcd prod-
uct storage, conveyor transtf-r T)o:ijts,
bygging and bulk loading and unloading
systems.
g 60.61 Definitions.
As v.-;ed m this subnart, r,ll ternis not
defined herein shall have the meaning
sueri them in the Act and in Subpart A
of this part.
(a) "Portland cement plant" means
any facility manufacturing Portland ce-
ment by either the wet or dry process.
(b) "Particulrte matter" means any
finely divided liquid or solid material,
other then uncombined water, ;-.s meas-
ured by Method 5.
S 60.62 .'JtnndnrcJ for pniticiilale matter.
(a) On and after the date on which
the performance lest required to be con-
ducted by 5 bO.S is initiated no owner
or operator subject to the pro'.isicns of
this part shall discharge or cause the
discharge into the atmosphere of par-
ticulate matter from the kiln which is:
U) In excess of 0.30 Ib. per ton of fe?d
to the kiln (0.15 KJJ. per metric ton),
maximum 2-hour average.
(2) Greater than 10 percent opacity,
except that whcie the presence of uncorri-
,bmed water is the only reason for failure
to meet the requirements for this sub-
paragraph, such failure shall not be s
violation of this section.
(b) On and after the date on which
the performance test required to be con-
ducted by § GO.8 is initiated no owner
or operator subject to the provisions of
this part shall discharge or cause the dis-
charge into the atmosphere of particulaf e
matter from the clinker cooler which is:
(1) In excess of 0.10 Ib. per ton of feed
to the l:iln (0.000 K5. per metiic ton)
maximum 2-hour averase.
(2) 10 percent opacity or greater.
(c) On and after the date on which -the
performance test required to be con-
ducted by § GO.8 is initiated no owner
or operator subject to the provisions of
this part shall discharge or cause the
discharge into the atmosphere of partic-
ulate matter from any affected facility
other than the kiln and clinker cooler
which is 10 percent opacity or greater.
§ 60.63 Monitoring; of operations.
The owner or operator of any Portland
cement plant subject to the provisions
of this part shall maintain a file of daily
production rates and kiln feed rates and
any paniculate emission measurements.
The production and feed rates shall be
summarized monthly. The record(s) aiid
summary shall be retained for at least
2 years following the date of such records
and summaries.
g 60.61 Test methods and procedures.
(a) The provisions of this section are
applicable to performance tests for de-
termining emissions of particuJnto mrt-
ter from portland cement plant kilns
and clinker coolers.
(b) All performance tests shall be
conducted while the affected facility is
opcT.tiri!? at or above the rniximvan
production rate at which such fre!i:;y
v.ill be operated anil mcler such oihrr
rslevr.nt conditions a1! the Acmir.istivlcT
r-hall n.ccify baccd on rcRrrrxrJ.-~V.-e per-
formance of the all'ected facility.
(c) Test methods set lorth in the ap-
pendix to this part or eqirivalcnt meth-
ods approved by Uie Administrator Lhall
be usod as follows:
(1) For each repetition, the average
concentration of particulate matter shall
be determined by using Method 5. Tra-
versing during sampling by Method 5
shall be according to Method 1. The mini-
mum sampling time shall be 2 hours and
the minimum sampling volume shr.ll be
GO ft.1 corrected to standard conditions
on a dry basis.
(2) The volumetric flow rate of tho
total efiluent shnll be determined by us-
in-r Method 2 and traversing according to
Method 1. Gas analysis shall be per-
formed luing the integrated sample! t cch-
nique of Method 3, and moisture content
shall be determined by the condenser
technique of Method 5.
(d) Total kiln feed (except fuels), ex-
pressed in tons per hour on a dry basis,
sh.oll be determined during each 2-hour
to&thiK penod by suitable flow meters
and .shall be confirmed by a material
balance over the production system.
(e) For each repetition, particulate
matter emissions, expressed in Ib./ton of
kiln feed shall be determined by dividing
the emission rate in Ib./hr. by the kiln
feed. Tho emission rr.te shall be deter-
mined by the equation, Ib./hr.—Q-.XC,
FEDERAL REGISTER, VOL. 36, NO. 247—THURSDAY, DECEMBER 23, 1971
E-69
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RULES AND REGULATIONS
whore Q.—volumetric flow rate of the
total effluent in f t.'/hr. at standard condi-
tions, dry basis, as determined in a.c-
cordanco with paragraph (c) (2) of this
section, and, c=part!culate concentra-
tion in Ib./ft.1, as determined in accord-
ance with paragraph (c)(l) of this
section, corrected to standard conditions,
dry basis.
SubpartG—Standards of Performance
for Nitric Acid Plants
§ 60.70 Applicability and designation of
affected facility.
The provisions of this subpart arc
applicable to each nitric acid production
unit, which is the affected facility.
§ 60.71 Definitions.
As used in this subpart, all terms not
dc fined herein shall h°.ve the meaning
given them in the Act and in Subpart A
of this py-rt.
(a) "Ninic acid production unit"
means any facility producing weak nitric
acid by either the pressure or atmos-
pheric pressure process.
(b) "Weak nitric acid" means add
which is 30 to 70 percent in strength.
§ 60.72 Standard for nitrogen oxides.
On and after the date on which the
performance test required to be con-
ducted by § GO.8 is initiated no owner
or operator subject to the provisions of
this part shall discharge or cause the
discharge Into the atmosphere of nitro-
gen oxides which are:
(a) In excess of 3 Ibs. per ton of acid
produced (1.5 kg. par metric ton),
maximum 2-hour average, expressed as
NO,.
(b) 10 percent opacity or greater.
§ 60.73 Emission monitoring.
(a) There shall be installed, cali-
brated, maintained, and operated, in any
nitric acid production unit subject to
the provisions of this subpart, an instru-
ment for continuously monitoring and
recording emissions of nitrogen oxides.
(b) The Instrument and sampling
system installed and used pursuant to
this section shall be capable of monitor-
Ing emission levels witnii ±20 percent
with a. evidence level of 95 percent and
shall be calibrated in accordance with
the method (s) prescribed by the manu-
facturer(s) of such instrument, the
Instrument shall be subjected to
manufacturers recommended zero ad-
justment and calibration procedures tvt
least once per 24-hour operating period
unless the manufacturer's) specifies or
recommends calibration at shorter in-
tervals, in which case such specifications
or recommendations rhall be followed.
The applicable method specified in the
appendix of this part shall be the ref-
erence method.
(c) Production rate and hours of op-
eration shall be recorded daily.
(d) The owner or operator of any
nitric acid production unit subject to the
provisions of this part .shall maintain
a file of all measurements required by
this subpart. Appropriate measurements
shall be reduced to the units oi the
standard daily and summarized monthly.
The record of any such measurement
and summary shah be retained for at
leant 2 years following the date of such
measurements and summaries.
§ 60.74 Te.^t methods and procedures.
(a) The provisions of this section are
applicable to performance tests for de-
termining emissions of nitrogen oxides
from nitric acid production units.
(b) All performance tests shall be
conducted while the affected facility is
operating at or above the maximum acid
production rate at which such facility
will be operated and under such other
relevant conditions as the Administra-
tor shall specify based on representa-
tive performance of the affected facility.
(c) Test methods set forth in the ap-
pendix to this part or equivalent methods
as approved by the Administrator shall
be used as follows:
(1) For each repetition the NO, con-
centration shall be determined by using
Method 7. The sampliag site shall be
selected according to Method 1 or.,1 the
sampling point rhall be the centroid of
the stack or duct. The sampling time
t-hall be 2 hours and four samples shall
be tiken at 30-minute intervals.
(2> The vo'u "Tic trie flow rate of the
total effluent shall be determined by
using Method 2 and traversing accord-
ing to Method 1. Gas analysis shall be
performed by using the integrated
sample technique of Method 3, and
moisture content shall be determined by
Method 4.
(d) Acid produced, expressed in tons
per hour of 100 percent nitric acid, shall
be determined during each 2-hour test-
ing period by suitable flow meters and
shall be confirmed by a material bal-
ance over the production system.
(e) For each repetition, nitrogen
oxides emissions, expressed in Ib./ton
of 100 percent nitric acid, shall be de-
termined by dividing the emission rate
in Ib./hr. by the acid produced. The
emission rate saall be determined by
the equation, lb./hr.=QsXc, where
Qs=volumetric flow rate of the effluent
to ft.'/hr. at standard conditions, dry
basis, as determined in accordance with
paragraph (c) (2) of this section, and
c=NO, concentration in Ib/ft.', as de-
termined in accordance with paragraph
(c) (1) of this section, corrected to stand-
ard conditions, dry basis.
Subpart H—Standards of Performance
for Sulfuric Acid Plants
§ 60.80 Applicability and designation of
afTocled facility.
The provisions of this subpart are ap-
plicable to each sulfuric acid production
unit, which is the affected facility.
§ 60.81 Definitions.
As used in this subpart, all terms not
defined herein shall have the meaning
given them in the Act and in Subpart A
of this part.
(a) "Sulfuric acid production unit"
means any facility producing sulfuric
acid by the contact process by burning
elemental sulfur, alkylation acid, hydro-
gen sulfide, organic sulfides and mer-
captans, or acid sludge, but does not in-
clude facilities where conversion to sul-
furic acid is utilized primarily as a means
of preventing emissions to the atmos-
phere of sulfur dioxide or other sulfur
compounds.
(b) "Acid mist" means sulfuric acid
mist, as measured by test methods set
forth in this part.
§ 60.82 Standard for sulfur dioxide.
On and after the date on which the
performance test required to be con-
ducted by § C0.8 Is initiated no owner or
operator subject to the provisions of this
pait shall discharge or cause the dis-
charge into the atmosphere of sulfur
dioxide in excess of 4 Ibs. per ton of acid
produced (2 kg. per metric ton), maxi-
mum 2-hour average.
§ 60.83 Standard for acid mist.
On and after the date on which the
performance test required to be con-
ducted by § 60.8 is initiated no owner or
operator subject to the provisions of this
part shall discharge or cause the dis-
charge into the atmosphere of acid mist
which is:
(a) In excess of 0.15 Ib. per ton of acid
produced (0.075 kg. per metric ton),
maximum 2-hour average, expressed as
H,SO,.
(b) 10 percent opacity or greater.
§60.81 Emission monitoring.
(a) There shall be installed, cali-
brated, maintained, and operated, in any
sulfuric acid production unit subject to
the provisions of this subpart, an In-
strument for continuously monitoring
and recording emissions of sulfur dioxide.
(b> The instrument and sampling sys-
tem installed and used pursuant to this
section shall be capable of monitoring
emission levels within ±20 percent with
a confidence level of 95 percent and shall
be calibrated In accordance with the
FEDERAl REGISTEt, Yd. >6, NO. 247—THURSDAY, DECEMBER 23, 1971
E-70
-------
RULES AND REGULATIONS
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E-71
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RULES AND REGULATIONS
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t— r— .
«5 CO
*3- CO
r— r—
cn o
1O CM
r— Oi
0 UD
OJ CM
CD Lft
l/> LT»
cj n
CM CO
*d- in
CO ^O
t>- VD
h^. o
U3 CO
ro to
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co en
in u>
.- ^i-
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CO •—
r— in
CM CM
VD ^O
CO Cv%
CM CM
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CO 1-^.
CNJ n
UD ^f-
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co to
to o
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to vo
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G\
CM 0>
to co
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ro o
CM CO
8 G
in "r-~
CM i—
i — en
co en
ro .CM
CM CO
CD CO
co in
en o>
en o
CO 00
CM en
co ro-
ro r-,
en o
CO t£)
CM «sh
*— en
to to
«*• «3-
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0 1-
CO CO
r^ co
if r—
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CO 01
ro en
CO t--
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CM hs.
o t~
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co ro
to »•*.
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E-72
-------
RULES AND REGULATIONS
222 For rectangular stacks divide the
cro- -j .secUo.'i into :c, ninny wjuaj rectangular
a'.'f-a-s an traverse point,",, such that the ratio
ot the length itt the width erf the elemental
areas is between one and two. I*)cate the
traverse point,1; at the centroid of each equal
area according to Fj;;ure 1-3.
3. Hefercnces.
Determining DuiA Concentration In a Gas
Stream, ASMU Performance Test Code —27,
New York, K.Y , 1037.
Dcvor):in, Ho ward, et al., Air PolH'tion
Source Teslin," M->ni_'.il, Air 1'ullution Control
District, Lcvi Angeles, Calif. November 1063.
Methods for Pel nmination of Velocity,
Volume, Dust ai-d 1111-! Content of Gasos,
Western FrecipiU.uoii Division of Joy Manu-
facturing Co., IBJS Ange'es, Caiif. Bulletin
WP-50, 19CO.
Standard Method for Sampling; Stacks for
Particuiate MaUtr, In. 1971 Book, of ASTM
Stand aids. Part 23, Philadelphia, Pa. 1971,
esignation D--2928-7JL
METHOD 2 - DETnF.MIN'ATTOW OF STACK GAS
VELOCITY AND VOI.VMKTRIC FLOW RA1E (TYPE
S PITOT TUBE)
• 1. Principle and applicability.
1.1 Principle. SU.ck fras velocity is deter-
mined from the E,:,S density and from mea.s-
urement of the velocity he^d using a Type S
(Stauscheibe or reverse type) pitot tube.
1 2 Applicability. Tilts method should be
applied only when specified by the test pro-
cedures for determining compliance with the
New Source Performance Standards.
2. Apparatus.
21 Pitot tube—Type S (Figure 2-1), or
equivalent, with a coefficient within ±5%
over the iwxrkint; range.
22 Ditfeiential pressure gauge—Inclined
manometer, or equivalent, to measure velo-
city head to within 10% of the minimum
value.
2 3 Temperature gauge—Thermocouple or
eqxuvalent, attached to the pitot tube to
measure st.'vck temperatuie to within 1.5% of
tho minimum absolute stack temperature.
2 4 Procure tuuif;e—Mercury-filled U-tu'oe
manometer, or equivalent, to measure stack
pressure to vvithin 0 1 m. H^
2.5 Bnromoter—To measure atmospheric
pressure to within. 0.1 in. Hg.
2.6 G a,', anal y?.er—To ana) yze pas composi -
tion for determining molecular weight.
2.7 Pitot txibe—Standard type, to cali-
brate Type S pitot tube.
3. Procedure.
S.I Set up the apparatus as shown in Fig-
ure 2-1. M.ike sure ail connodions are Up-lit
and leak free. Measure the velocity head and
temperature at the traverse points specified
by Method 1.
3 2 Measure the static pressure in the
stack.
3.3 Determine the stack gas molecular
weight by gas analysis and appropriate cal-
culations as indicated in Method 3.
PIPE COUPLING
TUBING ADAPTER
4. Calibration.
4.1 To caJibrate the pitot tube, measure
the velocity head at some point In a flowing
gas stream with both a Type S pitot tube and
a standard type pitot tube with known co-
efficient. Calibration should be done In the
Inborabory and the velocity of the flew in 3 ras
stream should be varied over the normal
v/orking range. It Is recommended that the
cahbiation be repeated after use at each field
site,
4 2 Calculate the pitot tube coefficient
using equation 2-1.
„
equation 2-1
where:
Ci'iost— Pitot tube coefficient or Type S
pitot tube.
Cnsta=Pitot tube coefficient of standard
type pitot tube (if unknown, use
0.99).
Ap>td= Velocity head measured by stand-
ard type pitot tube.
Apt«st = Velocity head measured by Type S
pitot tube.
1 3 Compare the coefficients of the Type S
pitot tube deteraiiued first with one leg and
then the other pointed donrnKtrea.nx Use the
pitot tube only if the two coefficients differ by
no more than 0.01.
5. Calculations.
Use equation 2-2 to calculate the stack gas
velocity.
where-
C's
Equation 2-2
, =Srack gns velocity, /eel per second (f p s ).
_=M teJ^. ( -- —^- ----V^Hlion tljfsc units
b. iuolc-°R/
arc used
Cp~Pitot tube cofMTHiont. dimens
(T,),v8.-Avoi,iKe absolute stack t;,is
°
.
(V'AP),,, =Avo':i.'
oad ot stack <. 3
P,=AljFotutti 5Uc!c C?.K fir<'5--{ire. i'lrho,s Hi-'
M1--Mol'Viil'!r wfii'ht of stuik gas (wet h i.->~;,
Ib./lb -r.iiU>
ftlj(l-H,«)+l'iB.o
Md = Dry ^uilocnlar weight of stack p,is (fuun
Mctliod 3).
Bwo = Piopoui(>n by volume, of ^vater vapor in
tlic pas stteam (from ^letliod 4)
Figure 2-2 shows a snmple recording sheet
for velocity traverse data. Use the a\ erases
In the last two eolurnns of Figure 2-2 to de-
termine tho average stack gas velocity from
Equation 2-2.
Use Equation 2-3 to calculate the stack
gas volumetric flow rate.
'Figure 2-1. Pitot tube-manometer assembly.
Equation 2-3
wbcre:
Q.=VoUimotrlc flow late, dty basis, standaid condi-
tions, ft Mir.
A=Cro.*s-snct!onal nrca of stack, ft.'
Titd= Absolute tomperatore at standard conditions,
630° K.
P.u=Absolute prcKsuro at standard conditions, 20 02
Inches 11 g.
FEDERAL REGISTER, VOL 36, NO. 247—THURSDAY, DECEMBER 23, 1971
E-73
-------
RULES AND REGULATIONS
6. References.
Mark, L. S., Mechanical Engineers' Hand-
book, McGraw-Hill Book Co., Inc., New York,
N.Y., 1951.
Perry, J. H., Chemical Engineers' Hand-
book, McGraw-Hill Book Co., Inc., New York,
N.Y., 19CO.
Shigehara, R. T., W. P. Todd, and W. S.
Smith, Significance of Errors In Stack Sam-
pling Measurements. Paper presented at the
Annual MecUng of the Air Pollution Control
Association. St. Louis, Mo., June 14-19, 1970.
Standard Method for Sampling Stacks for
Paniculate Matter, In: 1971 Book of ASTM
Standards. Part 23, Philadelphia, Pa., 1971,
ASTM Designation 0-2020-71.
Vemiiird, J. K., Elementary Fluid Mechan-
ics, John Wiley & Sons, Inc., New York, N.Y.,
1947.
PLANT_
DATE
RUN NO.
STACK DIAMETER, in.
BAROMETRIC PRESSURE, in. Hg.
STATIC PRESSURE IN STACK (P ). in. Hg.
OPERATORS
SCHEMATIC OF STACK
CROSS SECTION
Traverse point
number
Velocity head,
in. H20
Stack Temperature
AVERAGE:
Figure 2-2. Velocity traverse data.
FEDERAL REGISTER, VOL. 36, NO. 247—THURSDAY, DECEMBER 23, 1971
E-74
-------
RULES AND REGULATIONS
MLTT'OD 3- 0^«, ANALYSTS FOn CARnnPi DIOXtDr,
l.XCrsS /11'., A!JD DTT MOLk.CUI.AR Wt.lOHT
1. Principle and applicability.
1.1 Principle. An integrated or grab gas
sr.mplc is extracted fron. u sampling point
r.i.d a'lr-lvi'cd lor its components using an
Oi-at, ui .ilyyer.
1 1 An) l.-'.oility. This method should be
applied only when sncciflcd by the test pro-
cedures lor i!o,or;mjiirn; compliance with the
New Source lYnormp.nce Standards. The tost
procedure v. ill indicate whether a grab sam-
ple or an integrated t.r.mple is to be used.
2. Apparatus.
'2 1 Grab sample (Figure 3-1).
21.1 Probe— Stainless steel or Pyrex'
pla's, equipped with a lUter to remove partic-
ipate milter.
2.1.2 Pump—One-way squeeze bulb, or
equivalent, to transport gas sample to
ansJyzer. "
1 Trade name.
2 ? Integrated sample (Figure J-?).
2.21 Probe—Stainless sicel or Pyrex *
pi am, c^ulpptd with a filter to remove par-
tioulpte matter
2 23 Air-cooled condenser or equivalent—
To remove any excess moisture.
223 Needle valve—To adjust flow rate.
2.2 \ I'ump—Ltnk-free, diaphragm type,
or equivalent, to pull pas.
2 2 5 Ifate meter—To measure a flow
range from 0 to 0 035 cfm.
2 2 G Fiexible bag—Tedlar,1 or equivalent,
with a capacity of 2 to 3 cu. ft. Leak test the
bag in the laboratory before using.
2.2 7 Pilot tube—Type S, or equivalent,
attached to the probe so that the sampling
flow rate can bo regulated proportional to
tho .stack: gas velocity when velocity is vary-
ing \vith time or a .sample traverse is
conducted.
2.3 Analysis.
2 3.1 Orsat analyzer, or equivalent.
PROBE
FLEXIBI E WJBING
TO ANALYZER
FILTER (GLASS WOOL)
3. Procedure.
3.1 Grab t?mplln{t.
3 1.1 Set up tho equipment as shown in
Figure 3-1, mxklng sure all connectic/na aro
leak-free-. Place the probe In the Rt..u:k :a n
sampling point and purge the srjnphiif; line.
3 1.2 Draw tample into the analyzer.
32 Integrated sampling.
321 Evacuate the flexible bag. Set up the
equipment !'.s shown. In Figure 3- 2 with the
bag disconnected. Place the probe in thn
stack ana purge tho sampling llrio. Connect
the bag, making sure that all connections are
tight and that there are no leaks.
3.3.2 S.unple at a rate proporl,o«al to the
stack velocity
3 3 Analysis
3.3 1 Determine the CO.. O,, and CO con-
centrations !is boon as possible. 'Mike as many
pastes as are necessary to give constant read-
ings. If more than ten passes ore neces.ary,
replace the absorbing solution.
3.3 2 For grab sampling, repeat the scm-
phng and analysis until three cor-.ecutive
samples vary no more than 0.5 percent by
volume for each component being analyzed
3.3.3 For integrated sampling, repcr.t the
analysis of the sample until three corwcu-
tivo analyses vary no more than 02 p.rcent
by voltime for each component being
analyzed.
4. Calculations.
4.1 Carbon dioxide Average the three con-
secutive runs and report the result to the
nearest 0.1% CO.,
4.2 Excess air. Use Equation 3-1 to calcu-
late excess aar, and average the runs. Report
the result to the nearest 0.1% excess air.
. _
0.204 (
Rgure 3-1, Grab-sampling irain.
RATE METE!?
VALVE
. AIR-COOLED CONDENSER / PUMP
PRODE
FILTER (GLASS V/OOLJ
QUICK DISCONNECT
.BAG
RIGID CONTAINER'
Figure 3-2. Integrated gas • sampling train.
_ _
% CO) X U
ct]uation 3—1
where :
?;EA — Percent excess air.
c,'c Oj — Percent oxygen by volume, dry basis.
rcNa=;Fercent nitrogen by volume, dry
basis.
% CO = Percent carbon monoxide by vol-
ume, dry basis.
0.264 = Ratio of oxygen to nitrogen in air
by volume.
4.3 Dry molecular weight. Use Equation
3-2 to calcxUate dry molecular weight and
average the runs. Report the result to the
nearest tenth.
Md = 0.44(%CO,) +0.32(%O,)
-f 0.28(%N,-f
-------
RULES AND REGULATIONS
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E-76
-------
RULES AND REGULATIONS
lOCATfON
OPERATOR
PA If
RUN' NO
E DOI I,'O_
D'"f f.O _
ASSLWED MOISTURE. %__
HEA1ER K)I SETTINO
PftO« LENGTH, m.
iI VATIC Of STACK C",
lRAVt">r! POINT
TOTAt
AX.«At.-
.
IT,). "F
PT'F ".I'AL
o-ncc
l»'ll.
(Vml 1lJ
GAS 'jV.iPlt
I'.ILT
IT1" Io I. *F
A-.^
Avg
Avg.
<.
OF r,M
4 2 Sample recovery. Exercise care m mov-
ing the collection tram from the test site to
the sample recovery aro.i to minimise the
loss of collected sample or the pam ol
extraneous paniculate matter. Set aside a,
portion ot the acetone used in the sample
recovery as a blank for analysis Measure the
volume of water from the first three 1m-
pingcrs, then discard. Place the samples in
containers as lollows:
Container No 1. Remme the filter from
its holder, place in tins container, and seal.
Container No. .!. 1'l^ce loose paniculate
matici ai.-J nc.tone \ .^11114,5 f/.irn ail
;,,".mp!e-eypo'ea txufaces prior to the filter
in tins container and seal. Ube a razor bU'de,
blush, or rubber policeman to lo-e adhering
particles.
Contuinrr No 3 Transfer the silica gel
from the fourth impinger to the original con-
tainer and seal. 'Ui.e a rubber policeman as
an Rid in removing Silica gel from the
impinger.
4.3 Analysis Record the data required on
the example sheet shown in Figure 5- 3.
Handle eac'-i sample container as follows.
Container No. 1. Transfer the filter and
any loose particulatu matter from the sample
container to a tared f'.ass weighing di.-,h,
desiccate, and dry to a constant weight. Re-
port results to the iieaiest, 0 5 m't.
Container No. 2. Transfer the acetone
washings to a tared beaker and evaporate to
dryness at ambient temperature and pres-
sure Desicc 06 and dry to a constant weight.
Report results to the nearest 05 mg.
Container No. 3. Weigh the spent silica gel
and report to the nearest gram,
5 Calibration.
Use methods and equipment which have
been approved V>y the Administrator to
calibrate the orifice meter, pitot tube, dry
gas meter, and probe heater. Recalibrate
after each test scries.
6. Calculations.
6 1 Average dry gas meter temperature
and average orifice precsuie drop. See data
sheet (Figure 5-2).
C 3 Dry gas volume Correct the sample
volume meauired by the dry fc..-s meter to
standard conditions (70° P . 29 92 Inches Hg)
by using Equation 5—1.
/P 4-AU
(•r \ I rfc»'~r , ., R
l,td\ la.b
T " I \ -- P
•1m / \ Iiti
equation 5-1
e:
,td = Volume of gas sample through the
dry gas meter (standard condi-
tions) , cu. ft.
V,,,™ Volume of gas sample through the
drj gas meter (meter condi-
tions), cu.'ft.
slll" Absolute temperature at standard
conditions, 530° R.
Tm- Average dry gas meter temperature,
°R.
Pblr-- Barometric pressure at the orifice
meter, inches Ilg.
AH— Average pressure drop cicro- vt,lunT-of\v.il« v.ipor in tl:r- .MS
)lC (-( IM'l . d
^ wdi :^-^ oluine of \satT in the !ui^ ?anip!o v-
ivuidil ions), LU. tt.
^ '"dtd— Voluntcof ^ras .-un'.i'l'1 1 '"out.!1 thodrj, {"^ in, f> r
(ht.wdcinH'oiiditMMSj. cu. ft.
6.5 Total particulate weight. Detonjnne
the total particulate catch Iro-n the ia.ii of
the weights on the analysis data rheet
(Figure 5-3).
6.6 Concentration.
C.G.I Concentration in gr /s c.f .
equation 5-4
where:
c',-Concontiatlon of pmticulato matter in st.i'k
ca3, gr./s.^.(p, diy basis.
^fB —Total amount of participate matter rollcct -5,
niK.
1 ",id=Volume of p.is Cample through dry gas inrlor
(btundaid conditions), cu. ft.
FEDERAL REGISTER, VOL. 36, NO. 247—THURSDAY. DECEMBER 23, 1971
E-77
-------
RULES AND REGULATIONS
4 2 Gas volume.
°R /V T> \
17 71 - I - ™ — I
in. IIg\ Tm /
equation 4-2
where:
Vme —Dry gas volume through meter at
standard conditions, cu. ft.
Vm —Dry gas volume measured by meter,
cu. ft.
Pm = Barometric pressure at the dry gas
meter, inches Hg.
P.td^Pressine ut standard conditions, 29. D2
inchco Hf*.
T.idr=Absolute temperature at standard
conditions, 530' B.
Tm =Ab;.olute temperature at meter (°F +
460), °R.
4.3 Moisture content.
equation 4-3
where:
Bwo = Proportion by volume of water vapor
in the gas stream, dimensionlefas.
V»c = Volume of water vapor collected
(standard conditions) . cu. ft.
Vmt —Dry gas volume through meter
(standard conditions) , cu. ft.
B«M=r Approximate. volumetric proportion
of water vapor in the yas stieam.
leaving the impinge r.-, 0 025.
5. References
Air Pollution Engineering Manual, Daniel-
EOii, J. A (e..i.). U^.S. DHDW, PHS, National
Center for Air Pollution Control, Cincinnati,
OMo, PITS Publication No. 993-AP-40, 1937.
Dovorkm, Howrrd, et al., Air Pollution
Source Testing Manual, Air Pollution Con-
trol District, Los Angele.-, Calif.. November
1963.
Method", for Determination of Velocity.
VoUn-.e, Du.-t and Mi.,t route.' t 'f G.i.ie-,
Western Precipitation Division of . ->y Manu-
facturing Co , Ij0s Angeles, C..uf., Bulletin
WP-50, iocs.
METHOD 5 — DrrrnKiNiTtow or PAKTICULATE
L'MISSIOKS I-'rtoM WTAHOXARY SOURCES
1. Principle applica-
ble for the dcieimination of partieulate emis-
sions from stationary sources only when
specified by the test procedures for determin-
ing compliance with New Source Perform-
ance S'-andard.-.
2. Apparatus.
2.1 Sampling trrm. The design specifica-
tions of the partieulate sampling train used
by J,.?A (Figure ii-1 > are describee' in APTD-
0581. Coinmerci.il models of this train are
available
21.1 Nozxle— S'amless steel (31C) with
sharp, tapered leading edge.
21.2 Probe — P\ rex ' glass with a heatin™
system capable of maintaining a minimum
pas temperature of 250° F. at the exit end
during sampling to prevent condensation
from occurring When length limitations
(greater than about 8 ft.) are encountered at
temperatures le-s than 000° F., Incoloy 825 ',
or eqtm alenl, may be used. Probes for sam-
pling gas stream, at temperatures in excess
of COO" F. must h,.ve been approved by the
Administrator.
21.3 Pilot tube — Type S, or equivalent,
attached to probe to monitor stack gaa
velocity.
' Tr.ido i, rune.
2.1.4 Filter Holder—I-yrex • glass with
beating system capable of maintaining mini-
mum tt>?u.perature of 225 • F.
2.1.5 Implngcra/Condr-n-ser—Four Impin-
gers connected In series -with glass ball joint
fitt.in!js. The first, third, and fourth impln-
Cers are of the Greenburg-Smlth design,
modilied by replacing the tip with a '^-inch
ID gla^s tube extending to one-half inch
from the bottom c/f the ila.~k. The second 1m-
pinrer Is of the Grcenburg-Smith design
with the r.tancinrd tip. A condenser may be
used in place of the irnpingers provided that
the moisture content of the stack gas can
Si*:ll be determined.
2 1.6 Metering system—Vacuum gauge,
leak-free pump, thermometers capable of
measuring temperature to within 5' P., dry
gas rr.cier with Zc,'e accuracy, and related
equipment, or equivalent, a.s required to
maintain an Isoklnetic sampling rate and U>
determine sample volume.
2.1.7 Barometer—To measure atmospheric
pressure to ±0.1 inches Hg.
2 2 Sample recovery.
PROBE
REVtRSF-TYPE
P1TOT TUGE
221 Probe brush—At least as long as
probe.
2.2 2 Glass wash bottles—Two.
2.2.3 Glass sample storage containers.
2 2.4 Graduated cylinder—250 ml.
2.3 Analysis.
2.3 1 Glass weighing dishes.
2.3 2 Desiccator.
233 Analytical balance—To measure to
±01 mg.
234 Trip balance—300 g. capacity, to
measure to ±0 05 g.
3. Reagents.
3.1 Sampling.
3 1.1 Filters—Glass fiber, MSA HOC BH',
or equivalent, numbered for Identification
and preweighed.
3.1.2 Silica gel—Indicating type, 6-16
mesh, dried at 175° C. (350° F.) tor 2 hours.
3.1.3 Water.
3.1.4 Crushed ice.
3 2 Sample recovery.
3 2.1 Acetone—Reagent grade.
3 3 Analysis.
3.3.1 Water.
IMPINGES TRAIN OPTIONAL. MAY BE REPLACED
BY AN EQUIVALENT CONDENSER
HEATED AREA FJLTER HOLDER / THERMOMETER CHECK
-VALVE
^VACUUM
LINE
PI TOT MANOMETER
ORIFICE
IMPINGEnS ICE BATH
BY-PASS VALVE
VACUUM
GAUGE
MAIN VALVE
DRY TEST METER
AIR-TIGHT
PUMP
Figure 5-1. Particulate-sampling train.
3 1 a Deslccant—Drleute,1 indicating.
4 Procedure.
•i 1 Sampling
4 1.1 After selecting the sampling site and
Oo ir.immum number o! .^ tmplm;.: poiiuv
determine the clack pressure, temperature,'
moisture, and range of velocity head.
4.1 a Prepp ration of collection train.
Weigh to the nearest, gram approximately 200
p oC silica E;el. Label a filter of proper diam-
eter, desiccate= for at least'2-1 hours and
weifh to the Leaie>t 0 5 r.u; m a room \\h"ie
the relative humidity is loss than 50'r. Place
100 ml. of water in each of the nrst two
imp infers, leave the thud impinger empty,
and place approximately 200 g. of pr^weighed
silica gel 111 toe fotiitli impinger. Set up the
train without the probe as in Figure 5-1.
Leak ehec'K the sampling tram at the sam-
pling site by pluming up the inlet to the fil-
ter holder and pulling a '..'3 in 11.7 vacuum. A
leal;a:>c rate not in excess ol 0 02 c f m. at a
vacuum of 15 in. Hj,' is acceptable. Attach
the piobe and adjust the heater to provide a
gas temperature ol about 250° F. at the probe
outlet. Turn on the filter heating system.
Place crushed ice around the irnpmgcrs. Acid
a l 70 F.± 10 F.
more ice during the run to keep the temper-
ature of the gases leavirg the last impinger
as lo\v as possible and pielerably at 7U F
or less. Temperatures above 70° F. may rcsuli
in damage to the dry gas meter from either
moisture condensation or excessive heat.
413 Partieulate train operation. For eaen
run, record the data required on the example
sheet shown in Figure 5-2. Take readni^i ,-t
each sampling point, at least every 5 minutes.
and when Mgniflcant changes 1:1 stacl: con-
ditions necessitate additional adjustments
in flow rate. To begin sampling, position the
nozzle at the first traverse point with the
tip pointing directly into the gas stream.
Immediately st.irt the pump and adjust the
flow to isckmetic conditions. Sample for at
least 5 minute^ at each traverse po,nt, sarr.-
phn^ time must be the same for each p,-.'\i.
Maintain isokmetic sampling throughout the
sampling period. Nomographs are availabl*
which aid in the rapid adjustment of il-e
sampling-rate without other computation,
APTD-057G details the procedure for using
these nomographs. Turn off the pump at the
conclusion of each run and record the final
readings Remove the probe and nestle l:_m
the sf:>ek and handle in neeordance with th-*
f,:nnp!e recovery pi.,cess dc cnbed in -ec 10.1
FEDERAL REGISTER, VOL. 36, NO. 247.—THURSDAY, DECEMBER 23, 1971
E-78
-------
EULES AND REGULATIONS
PLANT.
DATE
RUN NO,
CGNTA'MSR
Nur/.:e«
— - ., ,
1
2
WEIGHT OF f ARTICULATE COLLECTED.
mg
FINAL WEIGHT ! TARE WEIGHT
i
i
WEIGHT GAIN
TOfAL } JI^^^CT.. ! ~J^^-t!c 'nmpltnj?
'iotal vo'uuie o/ liquid oolleitfil in I
find si.-ira fl (-Sen Kip. £-3), ml.
H = Hlc,.
VCJ -=V/)lun)C of K,I.'. S.UiipIo through tliedry ,"os rr<< l'-r
(nii-tfr coii'IltlMi1!), cu H.
Tm^Al^'jiulo ,iv T.'t-.f dry K.IS motor temperature
t.-.'criimsS-'.!), °1{.
r,,. -i! • i-iieins puvsure at sampling Mtn, Indus
J !L*
ATI— '• v, ;;;^c pm-^iirp drop across the orifice (s^c
i'k-. 5 2j,lml..-a I ho.
Ti=Ar/ol:i'.i: avnr.K'e stjr-k gas temperature (?>>e
ri? 5 2;,°K.
S = Tut u s n.pliiv time, mi-n.
V,.-.M;M.^ ,.,-, ywity c.ilc u utcd by MilliO'l 2,
triu.-itu.il 2-2, ft ,'s«-.
P,^Abs.)lu!e stur'k MS prf^bitrc, inohoo Ilg.
AQ — CIL^-L" :tio!iul .\reu of no/zlf , sq. ft.
6 8 Acceptable results. The following
range sets the limit on acceptable Isokinctic
Bampliri^ results:
If 90c,c < I < 110%, the results are acceptable,
otherwise", reject the results and repeat
the test.
7. Reference.
Addr-ndum to Specificfitloiis for Incinerator
Testing at Federal Facilities, PHS, NCAPC,
Dec. 6, 1967.
Martin, Robert M., Construction Details of
Isoklnetic Source Sampling Equipment, En-
vironmental Protection Afency, APTD-OjOl.
Eom, Jerome J., Maintenance, Calibration,
and Operation of Isokinetic Source Sam-
pling Iquip-.nent, Environmental Protection
Agency, AiTD-OoTG.
Smith, W. S., B. T. Shi^ehara, and W. F.
Tocld, A Method of Interpietrng Stacx Sam-
pling Dato, Paper presented at the 63d An-
nual Meeting of the Air Pollution Control
Association, St. l/oula. Mo., June 14—1G, 19'/0.
Smith, W. S., et al., Scac:: Gas San^ln.s
Imj.rovcJ and Si:npUl"ie
-------
RULES AND REGULATIONS
equation
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E-80
-------
RULES AND REGULATIONS
nitrous oxide, aie m'r«ure eoloriinctijral'y
using tht phc!iCldifu!/cmic RCiU (PUP-)
procedure
1.2 Applic.ibllHy. This n."!!iod '.- applica-
ble; for the inc;i .ure-nent of nllroj-^n oxides
frc.n btr.'lumiry souuos only when specified
by tie to t i>'.jc?ti",re3 for Ueleimining COTA-
plia'ice -V'Ui JNev, P-ov:rcc JV.IormaJ'OT
Stai. tard:,.
21 fa- •: pli'ir Ktc F,;,i'rr7-1
2.1.1 1'r, Lc-P.rre^ ' flass, heated, with
filter to rcn-o.e paniculate loatfer. Heating
Is uiin^c, : av li t>.s prube remains dry dur-
ing the pri ;r ;p-jnod.
21.2 C./1-ctioTi f:.-,sk—Tv.-u-)ller, Pyrex,1
round l:ott,Jir» v Uh r.hort nock and 24/40
Ktun'iirJ (r.fxT f.-p*nJn;;, protected against
Implo. Ion or breakage.
1 Trade name.
I 1 LI Flask vplvc—T-borc stopcock coa-
iicnoc1 to a 24/40 standard taper joint.
'J \ 4 Temperature nau<;e—Dial-typo ther-
mometer or equivalent, capable of mcntur-
Ing 2' V. In .cnv.'.s from 25' to 125* I1.
0 1 5 Vr.c.u.im line—Tubing capable of.
VvKrutandtrtr fi vacuum of 3 Inciies lit; abso-
luU pi?.'svic, v,ith "T" connection aiirt T-bore
fci opc^ck, or equivalent.
216 Pressure £au^e—U-tube manometer,
30 inches, with 01-inch divisions, or
equivalent.
2.1 7 Kurr.p—C"rnb!e of producing a vac-
xuiui of 3 incht"= lip; absolute prtt-sure.
£ 1.3 Squce/c bulb—One way.
?2 Sample recovery.
2 2.1 Pipr-tte or dropper.
:'..2 2 Gla^s storage containers—Cushioned
for shipping.
EVACUATE
V-V4' W/ /
'^ \i'' r~—'-^—• r-'^-\v f--'—:/'j""*:^
cr.ou:.a cuss CO-;E,
sr/, .•o;.,ui/.i-ir,
Jtli'.VEMO.ZI'W
tOIL'N'G n ASK -
2 LIISR. R'5u;'D-r,,1TTO>J SHORT >it
V/ITH J Si I CVL NO. 24 40
e 7-1. Comphrj luu.l, tt;:'-. val
e, and Mask
2.2.3 Olats vash bottle.
2.S Analyfeis.
2.3.1 Svcim bp.th.
2^.2 EcaVrirs or casseroles—250 ml., one
for e.-ich. sample find ttandrird (ulaa!:).
2 3.3 %'clr/.-ctric pipette-—1. T, r.;:d 10 ml.
2 3.4 Tr,\ns,n-r pipc-ao—10 nil. v.'jln 0.1 ml.
diilrionf.
2.3.5 Volun-,Ptr:o fiask—100 ml., one for
each sample, and 1,000 ml. for the standard
(blank).
2.". 6 Sptvirophotometer—To measure ab-
Korb^nce r11 4?'Mte solid reacent frrade.
3H3 Sulfunc acid—Concnntrated rea^tnt
fr. c'e.
3.7 4 Btr.ndPrd solution—Dissolve 0 5495 g.
potassium nitrate (KNO3) in distilled water
and dilute to 1 liter. For the working sland-
rrd solution, dilute 10 ml of 15.e if.ultir.s
solution to 100 ml. with distilled water. One
ml. of the vcT'-iIi1;: standard solution is
e-quivalent to 23 /tfr. nitrogen dioxide.
C.3.5 Witcr—Deionized, distilled.
3.3 6 l-'aenotdlsu!foiiic acid solution—
nissolve 25 g. of pure white phenol In. 150 ml.
concentrated sulfuric acid on a steam bath.
Cool, add 75 ml. fuming sulfuric acid, and
heat at 100° C. for 2 hours. Store in a dark,
stoppered bottle.
4. Procedure.
4 1 Sampling
4.1.1 Pipette 25 nil. of nbsorbing solution
Into a sample fia^k. Insert the flask valve
stopper into the flfwsk with the valve In the
"purgo" position. Assemble the sampling
train as shown In Figure 7-1 and place the
probe at the sampling point. Turn the flask
valve and the pump valve to their "evacuate"
positions. Evacuate the flask to at lca->t 3
Inches Hn absolute pressure. Turn the pump
valve to its "vent" position nnd turn ofl the
pump. Check the manometer for finy fluctu-
ation in the rnTcury level. If there li a visi-
ble chmr;o over the span of one mlnutf,
cheek lor iraks. Record the Initial volurue,
temperature, and barometric pressure. Turn
the l\a;>k vaive to its "purt^c" position, arid
then, do the sama with the pump vr ire.
Par.-'» the prob" and the vacuum tube u-;ini^
tl-.a s'juee/e bulb. If condensation occurs in
the piobe and f!ask valve ar"n, heat 1he probe
and purre u'ltll the concl?nruiion dipp.'nei-rs.
ThCfi turn tiic pump valve to itr> "\'cnt" p«. i-
tion. Turn the flcn,k valve to Its "wmple"
position and allow sample to enter the itr" k
for about 15 seconds. Alter collecting the
ffimple, turn the flask valve to Its "puiee"
position and disconnect the flask from th.?
saniplins train. Shake the uaik for 5
rmnntcs.
4 2 Sample recovery.
42.1 I-ct tr.e flask set for a minimum of
16 hoars and then shake the contents for 2
minutes. Connect the flask to a rrr-re;iry
fiilccl U-tube manometer, open the valve
Irora the flask to the manometer, r.nd rec.->rd
the flask pre- ,ure and temperature n;rin'j
with the. baro:ni;ric pressure. Transfer th:-
fiask cent outs to a container for shipment
or to a 250 ml beaker for anplyfis. RIns-e the
flask with t-.vo portions of a.ftilletl w.ifr
(appioTimntcly 10 ml.) and ;,c'd rinse vrrer
to the snripl^ For a blank xr.e 2o ml. of ab-
sorbing solution r.nd the some volume of dis-
tilled, water as u=.ed in rin-in,^ th? ilask P/ior
to shipping or rniiK.i!-, add sociiuni hvdiox-
ide (IN) ciro'Vi ,e into botli t^o 5'imnlp raid
the blank until nl!:aline t'.> Utmus paper
(about 2o t^> MS drojis in each).
4 3 Anal j'.is.
4.31 If 1he sample has been shipped in
a container, transfer the contend to r. 230
ml berker iisiup; a small amc-.iut of dirdllecl
wate^. }^\.ipora1e the soUition to dryr.c1-- ou a
steam bn.Ui r.nd tilcn cool Ac;,I 2 nil. pLcnoi-
di'ul'oni; r,c:cl : olution to t'.t dried ics^dr.c
e.ud tr;tume t.bcrougiily v.ith a glass r<.,rtacts all the icsi-
dvie. Add 1 ml distilled wr.ter and four drop-,
of cor-crntvaied sulfuric acid
. the
tion on a slcom 'oath for 3 miiiuies v j'h oc-
casional btirnng. Cool, add 20 ml. cu^t.iled
water, rn,x well by stirring, ;,id add conct-n-
trated^A'iiiioinum hydroxide dropwise v ith
constSfnt stirim<; tintil alkaline to litmus
paper. Transfer the solution to a 100 ml.
volumetric f.V.sk and wash the ber.ker three
tunes with 4 to 5 ml. portions of distilled
water. Dilute to the mark one! mi^c thor-
oughly It' the sample contain:- solids, tms-
fcr rt portion of the solution to p. clc :i ctry
centn:':co tube, and ctr.trifivjf, or ii'ic" a
portion of the solution treasure the ai;~'jrb-
ance of each sample at 420 nm. us^ng tue
blank solution as a zero. Dilute the sample
and the blank with a suitable amount rf
distilled Wiit^r if iib-erbance fulls outside the
ranpe of cniibrauon.
5. Calibration.
5 1 riask volume Assemble the flask and
fiask volve and nil with water to the stop-
cock, Mepsuro the volume of water to ± 10
ml. Number and record the volume on the
flask
5 2 Pij^ctrophotonieter Add 0 0 to 1C.O ml.
of standard solution to a series of beakers. To
each beaker add ::5 ml. of absorbing solution
and add podium hydroxide (1A') drop-Also
until alkaline to litmus paper (about 25 to
35 drops). Follow the analysts procedure of
Efvtion 4.3 to collect enouph data to draw »
calibration curve of concentration In ,sg.
per caniplo versxis absorbance,
6. Calculations.
6 1 Sample volume.
FEDERAL REGISTER, VOL. 36, NO. 247—THURSDAY, DECEMBER 23, 1971
E-81
-------
RULES AND REGULATIONS
22 Sample recovery.
" \ ny of
V,c— Simple volume ftt staidaid concH- the rio-jip-n sDteifie&tlons of thH rampllng
tlons (dry batis) , ml. tram u-c ar-scribed !n APTD-CoGl.
7. Bf/cr<>nr-es. 2.1 1 No;-. IF — .Stainless f>tcel (31C) with
Stancli.rU :\rethods of Chemical Analysis, fharp, tape.-.-d leading edt*e.
6th ed. 1,'j^r Yo-k, D. Van Nostrand Co., Inc. 2-L-2 rrobe— 1'yrex * plr^s with a h»atln»
1932, \jl. J, p. Si 9-330. system to prevent visible condensation dur-
Standr.rci Melhod of TC.VCT.L. ilon D--l(..)3-t,0, 2 !•* Fntci' holder— Pyrcx ' glasp.
p, Y25 -'(":>"*. U.1.5 IirvpiTjf^Cj'.. — Four a^j s'lovrn iri Figure
Jacob, M. I1 , The Che:u:,.vl Analy, is of Air fi-1. The f.r-,t and tl.ird O.TC of \}\ ; r;rCL-aVai;;-
tfuii.-, Nc-iV i'or-i.Js Y., interwience J'ub- Smith des'cn witu btan'UirJ tip _i:f second in 100 ml. distilled waiter.
3.1.4 iGopropnnol, 80% — Mix 600 ml. of
lsopropr.no! with 200 ml. of dc:oru'/ed, ciic-
tlllecl v. at-r.
3.1 5 KvdroT?n peroxide, 3 Co — Dilute Jf-0
ml. of SOlc- hydrcp.en peroxide to 1 liter vuh
delon'Ecd, o;:Uiiled water.
3.1 0 Cr.rhedico.
3 2 Sample recovery.
3 2.1 V.T.ter— Deionirc-d, distilled.
3.2.2 Ijrpiopaiiol, 80%.
3.3 Analysis.
331 V.'ater— Df-loniMd, distilled.
lisheiH, Inc., li/W, vol. 10, n. 351-356.
METHOD 8 V'JTKRMINATION Of bULn'IlIC ACIB
MiriT ATTD CTiI.c-CB HIOXIOL rMlESIOWS I'BOM
and fourtli :.i'3 'I i!:e Cicenbur--;
ci((;n, modiijcd bv rcpii.cir^K tbj .-.iMi
V-iUl n V,, -inch 'iD ^U'i.S tlii'.t' CX'U:
one-half in: 11 in i'i the b .;i^m <. i
plnjrtr fl;: .k. »Si-r.Har coi!<'.;t!o-x
v, meh hrivo L-'^r rtpprovod by U.e A
tritor, nv^y o,: -- '.;'..
''IS ?.;..•' i riT'; svs-Lenv— V:\> x-"!~i
Hrk-frcf! pun'p, tbermorDc-ttri c. .'
m-'Lisunr.^ t-?!'\;:.\ t'ire tx^ vifuia ^
1. PrincipL' c.nd applicability.
1.1 Pr'; \clt;'c. / ivis iLi'nnie lr extiac
from c, b.'.mpJjn • puiat in ii--.- stuck u.io
acici 1 li.'A IIK-UIUSU; suH'ui aioMus: lo ; c
ratc-U /join su'Iur ciiox'de p.r--'n frivetrii:--;.
inr-ivsuvf a n pr.rarsly by the bnntim-thoi-jn e^ur.imcrt, or ' ... -. t.;eat, v', noun..! to
titrtition ?T ;-tb^vl. ^(iiiitNXin t..ii i'.c'iiij-'Uc ^ninpllrj/ mto &nd
1-2 f.r; !!'p-)i»t-.-. Tins ni.-thod i.i rnplica- lo Jrier::nuo !.-.m u; vc.lup.c. "
bio to t'-f-r.iT>ir.iu-n of tMUuric ncui io:.-t 21.7 B.-.ro:n - ot'r -'j.o ir.eaoiire atmospheric
(including cullvir trloxde) and sulfur diox- presstu-e to ±0.1 inch Kg.
Ide tr.-in stationary sources only when ppe- ^
clued by the test procedures for determining i Trade name.
r,li ce- 3 3't r;.M-nim pc-rchlon.te (00!W)—D. -
.'•i t.p B-jlve 1 r;5 :? of Iwiuum j.-cfchln.,ix: [La
-n;* to (CO,) 3 II O| in 200 ml. disulled water rr..i
1(5 ii"i- d'Uivc to 1 liior ^-jtli iBopropvnol. StandattK, -j
ilsiiis, vuh .v.iliarc acid.
uiii-ja- 30;, (j-ururic acid st •if^i.-'l fCOl.Vi —
Piurna oor c-nndnrc)l."<3to rlr 000"'2.Vr. -T -.
r.-ure, (i,;.] ;./ :sr,.Oii ',,h!c'Q b 13 prcvi-•;.••-:v . ;.
•lift Of ..-t^r,-! ,r<-:
'XTTI ,rc;.7-d o/jv.n,-:t' prirn.iry
.t :nTii :>_o'j nht
A r.-;T,'(/.:/-c.
4.1 S:cipling.
PROLc
STACK
WALL
FILTER HOLDER
f
THERMOMETER
CHECK
•^VALVE
ICE DATH IMP1NGEP.S
BY-PAS3 VALVE
I ""f"\"
LsUI IK
GAUGE
_
T*m-TlGHT
PUMP
rnv TEST WTEn
Fljjuro 0-1. Sulfyrlc acid miot f.?,r-.;;
FEDERAL REGISTER, VOL. 36, NO. 247—THURSDAY, DECEMBER 23, 1971
rnojsLure, ftnri ran^e of velocity rie.ifi,
4-.1 2 Prcpara'.ion oj cjllftc-ion tr;:r,
Placo 10O ml. of PO'.o LiC'propcujol in the nr-_t
impinjter, 100 i^l. of 3 % h-,c!ror:'"n peroxide ia
botn the Eecosid and third implnircrs, and
about 200 g. of silica rrel in the So .-.-tii i:r.-
pin^er. Retain a- portion Oi txio i-^-ii,'^ t-.r
u ,e fU3 bj.'iLk r^lulJotLS. /xSti-mole "Ji.^ t".1. .11
vathC'uL t.'ie prco^ ar, s>iown jr. I': ".ire r-".
•Rr.'.i i-ac iul';?.- Lecwcen Lie i-ri' • :.'- z<..-\—J.
impinf.^rs. Lc-ik cl-cck tiio s. "-:••-. 'hrq t: :i.
at 11,0' soir-plm;' site by p''!7;"nr; v;e ir.:_i • j
the flii, iinpmger itnd pulK_ .; a 1 ;"•-::: ch 1"^
vao.HU'i. / l^ikr^-e ratn not in ":c."c--.s ot 0 .;.i
ca.ra. c.i a vocutim of LJ LV.UI-J I.; is i.:-
cept.a'nle AurcJi the probe r.iu! tvrr ot. T -.?
proba hvjiitlnsj system. AUjii^t t.u» pi.'j;
te.i'cr sottiTi;; d'irinfr ui.;.p;,ii; to p.-e.i..'.
any vicllilu condensation, 3'r.ce cn;;-i' a . c=
orcimcl the implnsers. Add rrore ice d\:;."T
tiic mil 10 keep the te rrjpi turc of the vr^c^
lea\H.ii3 tlie last nnpmger at 70* P. cr less.
4..1 " Train operation. I-'or each ri.i: i.1-
cord the data required on the ex", ^pjc ..:.:;
shown ui Figure B-2. T.ikc re;>caii~j at c >._!
hampliii? point at lca;,t every 5 Minutes r.:. -1
when si^tulicant ch a 115*03 in t,;,iok eor.i'.i.H-i.s
neces-Miato additional iLClju^'vintnts u\ ii.;\v
rate. To bf-srin suiiplinc. pj=i;!oii the- r.,,/ Ic1
n.t the 'irst viavc-r.se point \.ith t'-.e tip pc '.u.-
Ing directly into the f,:\s strc.un. ;- .irt :.,3
pump r.nd iianitJ.in.tcly adjust The How to
Isokinetic conditions. Maintaiu ^ok.iiciic
E-82
-------
RULES AND REGULATIONS
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E-83
-------
RUIES AND REGULATIONS
Tfoin, Jerome .1 , Maintenance, Onlil>rati"n,
and O; oration of look.nelic Source Sam-
pling VXimpment, Environmental Protection
Agency. Air Pollution Control Oitico Publl-
caliouNo APTD-O.V7G.
Shell Development Co. Analytical Depart-
ment, Determination of Stihur Dloxirte and
Su'Lfur Tnoxicle m S'.acs Dates, E.neryvilla
Method Series, 4516/59a.
MF.THOP o—VISTM, mrrntMTNATio:; or THE
OI'AOTY OF EMISSIONS 1 KOll STSTION'Ar.Y
SOURCES
1. Principle and up,n"'i'1}'! •!!.'.
1.1 Principle The ieiai,ue opacity of an
ojni.->,i(ni from o MilionprY source is de-
termine;! •visually toy a qualified oTrervcr.
1 2 Applicnbiliry. This meilitxl is appli-
cable for the det"rmluauoii o£ the relative
opacity of visible omissions from stationary
sources only when M>oci:ic;d Ly tc&t/ proce-
dures for cleterminiijg rciiipha.ice with the
New Sourcf Peifoiiiianri'- ^tancJrutls.
2. Procedure.
k.1 'Hie qiitijiuod
-------
REGULATION NO. 7
Regulation to Control the Emissions
of Hydrocarbon Vapors
Air Pollution Control Commission
E-85
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Adopted: September 13, 1973
Effective Date: November 28, 1973
REGULATION NO. 7
Regulation to Control the Emissions of
Hydrocarbon Vapors
A. AFFECTED AREAS:
1. Sections F and G shall apply Statewide.
2. Sections B, E, H, I, and J, shall apply only to designated
air pollution control areas.
3. Sections C and D shall apply only to the designated Denver-
Metro air pollution control area.
4. All "references to designated air pollution control areas,
throughout this regulation, shall be as shown on page 1.13
of the Commission Regulation No. 1.
B. PETROLEUM PRODUCT STORAGE:
1. The storage of any type of petroleum distillate in any stationary
tank, reservoir, or other container of more than 40,000 gallons
(152,000 liters) shall be in a pressure tank capable of maintaining
working pressures sufficient at all times to prevent vapor loss to
the atmosphere. Said tank, reservoir, or other container shall be
equipped with one or more of the following, properly installed, in
good working order, and properly maintained:
(a) A pontoon-type or double deck-type floating roof, or
internal floating cover, which shall rest on the
surface of the liquid contents and shall be equipped
with a closure seal or seals to close the space
between the roof edge and tank wall. This control
equipment shall be acceptable for said tanks, reservoirs,
or other containers only if any type of petroleum
distillate has a vapor pressure not exceeding 11 pounds
per square inch absolute (568mm.Hg) under actual storage
conditions. All gauging or sampling devices shall be
vapor-tight, except when tank gauging or sampling is
taking place; or
(b) A vapor recovery system, consisting of a vapor gathering
system capable of collecting the hydrocarbon vapors
discharged, together with a vapor disposal system capable
of processing such vapors so as to prevent their emission
to the atmosphere. All gauging and sampling devices shall
be vapor-tight except when gauging or sampling is taking
place.
E-86
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(c) Other equipment of equal control efficiency, provided the
design and effectiveness of such equipment as documented
is submitted to and approved by the Division.
2. This Section B.I shall also apply to the storage of crude oil
within the designated Denver-Metro air pollution control area.
3. Propane or butane and similar products shall be stored in pressure
. tanks maintaining working pressures sufficient at all times to
prevent hydrocarbon vapor loss to the atmosphere, or at refrigerated
low temperature, or in low pressure storage equipped with vapor
collection and compression equipment designed to prevent the loss
of hydrocarbon vapor to the atmosphere.
4. The storage of any petroleum distillate in any stationary storage
vessel of more than 3,500 gallons (13,300 liters) capacity shall
be in a vessel equipped with a permanent submerged fill pipe or
with a vapor recovery system.
C. PETROLEUM DISTILLATE LOADING INTO TANK TRUCKS, TRAILERS, AND OTHER
TRANSPORT VEHICLES:
1. The loading of any type of petroleum distillate into any tank truck,
trailer, or other transport vehicle shall be from a loading facility
equipped with a vapor collection and disposal system or its equivalent,
properly installed, in good working order, and properly maintained.
Also, the loading facility shall be equipped with a loading arm with
a vapor collection adaptor. Said system must also have pneumatic,
hydraulic, or other equivalent mechanical means to force a vapor-tight
seal between the adaptor and the hatch. A means shall be provided to
prevent drainage of petroleum distillate from the loading device when
it is removed from the hatch of any tank truck, trailer, or other
transport vehicle, or to accomplish complete draining before the
removal. When loading is effected through means other than hatches,
all loading and vapor lines shall be equipped with fittings which
make vapor-tight connections and which close automatically when
disconnected.
2. Vapor recovery may be accomplished by one or more of the following:
(a) A vapor-liquid absorber system where vapor emissions do not
exceed 1.5 pounds (1,000 gallons loaded at 70°F, 1 Atmosphere)
(b) Bottom loading (closed hatches) at terminal racks where vapor
emissions do not exceed 1.5 pounds (1,000 gallons loaded at
70°F, 1 Atmosphere).
(c) Other equipment where vapor emissions do not exceed 1.5
pounds (1,000 gallons loaded at 70°F, 1 Atmosphere) and as
approved by the Division.
E-87
-------
3. This section C shall apply only to petroleum distillate loading
facilities where 40,000 gallons or more, averaged over the work
days of any month, are loaded in any one day. Facilities loading
under 40,000 gallons per day, such as bulk plants, shall install
telescoping top-loading equipment, or a demonstrated equivalent,
to provide 97% submerged fill.
4. For the purpose of this regulation, "loading facility" means any
aggregation or combination of petroleum distillate loading equipment
which is (1) owned or operated by one person, and (2) located so
that all the petroleum distillate loading outlets for such aggregation
or combination of loading equipment as encompassed within a circle of
300 feet in diameter.
D. WATER SEPARATION FROM PETROLEUM PRODUCTS:
1. Single or multiple compartment oil and effluent water separation
equipment which receives effluent water containing 200 gallons
(760 liters) or more a day or more of any petroleum product or
mixture of petroleum products from any equipment used for processing,
refining, treating, storing, or handling of petroleum products having
a Reid vapor pressure of 0.5 pound or greater, shall be equipped with
one or more of the folj.owing vapor loss control devices, properly
installed, in good working order, and properly maintained:
(a) A solid cover with all openings sealed and the liquid
contents totally enclosed. All gauging and sampling
devices shall be vapor-tight except when gauging or
sampling is taking place.
(b) A pontoon-type or double deck-type floating roof, or
internal floating cover, resting on the surface of the
contents and equipped with a closure seal or seals to
close the space between the roof edge and container
wall. All gauging and sampling devices shall be vapor-
tight except when gauging or sampling is taking place.
(c) A vapor recovery system consisting of a vapor gathering
system capable of collecting the hydrocarbon vapors
discharged and a vapor disposal system capable of
processing such hydrocarbon vapors so as to prevent
their emission to the atmosphere. All container gauging
and sampling devices shall be vapor-tight, except when
gauging or sampling is taking place.
(d) Other equipment of equal or greater efficiency, provided
the design and effectiveness of such equipment as documented
is submitted to and approved by the Division.
2. This section D shall also apply to oil and effluent water separators
used in conjunction with the production of crude oil.
E-88
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E. PUMPS AND COMPRESSORS:
1. No person may build, install, or permit the building or installation
of any rotating pump or compressor handling any type of petroleum
distillate unless said pump or compressor is equipped with mechanical
seals or other equipment of equal efficiency. If reciprocating-type
pumps and compressors are used, they shall be equipped with packing
glands properly installed, in good working order, and properly main-
tained so no emissions occur from the drain recovery systems.
2. This section E shall also apply to pumps and compressors handling
crude oil within the designated Denvej:-Metro air pollution control
area.
F. WASTE GAS DISPOSAL:
Any waste gas stream containing hydrocarbon compounds from any polymer
process emission source shall be burned at 1,300°F (704°c.) for 0.3
second or longer, in a direct-flame afterburner or an equally effective
device. The emissions of hydrocarbon vapors from a vapor blowdown
system or emergency relief shall be burned in smokeless flares, or
equipment of equal efficiency, provided the design and effectiveness of
equipment, as documented, is submitted to and approved by the Division.
G. ORGANIC SOLVENTS:
1. No person may discharge into the atmosphere more than 15 pounds of
organic materials in any one day, nor more than 3 pounds thereof in
any one hour, from any article, machine, equipment or. other contri-
vances in which any organic solvent or any material containing
organic solvent comes in contact with flame or is baked, heat-cured,
or heat-polymerized, in the presence of oxygen, unless said discharge
has been reduced by at least 85 percent. Those portions of any
series of articles, machines, equipment, or other contrivances designed
for processing a continuous web, strip, or wire which emit organic
materials and use operations described in this subsection 1 shall be
collectively subject to compliance with this subsection.
2. No person may discharge into the atmosphere more than 40 pounds of
organic materials in any one day, nor more than 8 pounds in any one
hour, from any article, machine, equipment, or other contrivance used
under conditions other than described in section 1, for employing,
or applying, any photochemically reactive solvent, as defined in
subsection 10 of this section, or material containing such photo-
chemically reactive solvent, unless said discharge has been reduced
by at least 85 percent. Emissions of organic materials into the
atmosphere resulting from air or heated drying of products for the
first 12 hours after their removal from any article, machine,
equipment, or other contrivance described in this section G shall be
included in determining compliance with this section. Emissions
resulting from baking, heat-curing, or heat-polymerizing as described
in subsection 1 of this section shall be excluded from determination
of compliance with this section. Those portions of any series of
articles, machines, equipment, or other contrivances designed for
processing a continuous web, strip, or wire which emit organic
materials and use operations described in this subsection 2 shall be
collectively subject to compliance with this subsection 2.
E-89
-------
3. No person may, after December 31, 1974, discharge into the atmosphere
more than 3,000 pounds of organic materials in any one day, nor more
than 450 pounds in any one hour, from any article, machine, equipment,
or other contrivance in which any non-photochemically reactive organic
solvent or any material containing such solvent is employed or applied,
unless said discharge has been reduced by at least 85 percent. Emissions
of organic materials into the atmosphere resulting from air or heated
drying of products for the first 12 hours after their removal from any
. article, machine, equipment, or other contrivance described in this
section G shall be included in determining compliance with this
subsection 3. Emissions resulting from baking, heat-curing, or heat-
polymerizing as described in subsection 1 of this section shall be
excluded from determination of compliance with this subsection. Those
portions of any series of articles, machines, equipment, or other
contrivances designed for processing a continuous web, strip, or wire
which emit organic materials and use operations described in this
subsection 3 shall be collectively subject to compliance with this
section.
4. Emissions of organic materials to the atmosphere from the clean-up,
with photochemically reactive solvent as defined in subsection 10 of
this section, of any article, machine, equipment, or other contrivance
described in subsections 1, 2, or 3, of this section G shall be included
with the other emissions of organic materials from that article,
machine, equipment, or other contrivance for determining compliance with
this section G.
5. Emissions of organic materials into the atmosphere required to be
controlled by subsections 1, 2, and 3 of this section G shall be reduced
by:
(a) Incineration, provided that 90 percent or more of the carbon
in the organic material being incinerated is oxidized to
carbon dioxide,
(b) Adsorption, or
(c) Processing in a manner to be not less efficient than (a) or
(b) above, provided said processing and equipment, as documented,
is submitted to and approved by the Division.
6. A person processing organic materials pursuant to this section G shall
provide, properly installed, in good working order, and properly main-
tained devices as specified in the authority to construct and the permit
to operate, or as otherwise specified by the Division, for indicating
temperatures, pressures, rates of flow, or other operating conditions
necessary to determine the degree and effectiveness of air pollution
control.
7. Any person using organic solvents or any materials containing organic
solvents shall supply the Division, upon request and in the manner
and form prescribed by it, written evidence of the chemical composition,
physical properties, and amount consumed for each organic solvent used.
E-90
-------
8. The provisions of this section G shall not apply to:
(a) The manufacture of organic solvents, or the transport
or storage of organic solvents or materials containing
organic solvents.
(b) The use of equipment for which other requirements are
specified by subsections 1, 2, and.3, of this section G
this regulation, or which are exempt from air pollution
control requirements.
(c) The spraying or other employment of insecticides,
pesticides, or herbicides. .
(d) The employment, application, evaporation, or drying of
• saturated halogenated hydrocarbons, perchloroethylene, or
trichloroethylene, provided the emission of organic
materials is controlled to less than 40 pounds per day
or 8 pounds per hour.
(e) The use of any material, in any existing article, machine,
equipment or other contrivance described in subsections
1, 2, 3, or 4, of this section G or the use of any material
in any new or substantially modified article, machine,
equipment, or other contrivance described in these sections,
if the organic solvent or any material containing organic
solvent does not come into direct contact with flame, and
if the total volatile content of the material is not photo-
chemically reactive as defined in section 10 of this
regulation, and it meets any one of the following conditions:
(i) The total volatile content contains not more than
20% by weight organic solvent, and the remainder
consists only of water, or
(ii) the total volatile content does not exceed 20% by
weight, and a substantial portion of which
evaporates before reaching the first heated zone, or
(iii) the total volatile content does not exceed 5% by
weight.
9. For the purposes of this section G, organic solvents include diluents
and thinners and are defined as organic materials which are liquids
at standard conditions and which are used as dissolvers, viscosity
reducers or cleaning agents,, except that such materials which exhibit
a boiling point higher than 220°P at 0.5 millimeter mercury absolute
pressure or having an equivalent vapor pressure shall not be considered
to be solvents unless exposed to temperatures exceeding 220°F.
E-91
-------
10. For the purposes of this Regulation No. 7, a photochemically reactive
solvent is any solvent with an aggregate of more than 20 percent of
its total weight composed of the chemical compounds classified below
or which exceeds any of the following individual percentage composition
limitations, referred to the total weight of solvent.
(a) A combination of hydrocarbons, alcohols, aldehydes, esters,
ethers, or ketones having an olefinic or cyclo-olefinic type
of unsaturation: 5 percent;
(b) A combination of aromatic compounds with eight or more carbon
atoms to the molecule, except ethylbenzene: 8 percent;
(c) A combination of ethylbenzene, ketones having branched
hydrocarbon structures, trichloroethylene or toluene:
20 percent.
Whenever any organic solvent or any constituent of an organic solvent
may be classified from its chemical structure into more than one of
the above groups of organic compounds, it shall be considered as a
member of the most reactive chemical group, that is, that group having
the least allowable percent of the total volume of solvents.
11. For the purposes of this section G, organic materials are defined as
chemical compounds of carbon excluding carbon monoxide, carbon dioxide,
carboric acid, metallic carbides, metallic carbonates, and ammonium
carbonate.
For the purpose of this section G the terms "baked, heat cured, or
heat polymerized" refer to coatings and other organic, solvent
containing materials which;
(a) have been heated in devices in which the air temperature
exceeds 175°F (80°C), and
(b) which have become insoluble in solvents in which they were
soluble before being subjected to heat.
H. ARCHITECTURAL COATINGS:
1. No person may sell or offer for sale for use in containers of
one quart capacity or larger, any architectural coating containing
photochemically reactive solvent, as defined in subsection 10 of
section G of this regulation.
2. No person may employ, apply, evaporate or dry any architectural
coating, purchased in containers of one quart capacity or larger,
containing photochemically reactive solvent, as defined in
subsection 10 or section G of this regulation.
E-92
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3. No person may thin or dilute any architectural coating with a
photochemically reactive solvent, as defined in subsection 10
of section G of this regulation.
4. For the purposes of this section H, an architectural coating is
defined as coating used for residential or commercial buildings
and their appurtenances, or industrial buildings.
I. DISPOSAL AND EVAPORATION OF SOLVENTS:
^No person may, during any one day, dispose of a total of 1 quart capacity
or larger, any photochemically reactive solvent as defined in subsection
10 of section G of this regulation, or of any material containing 1 quart
or more of any such photochemically reactive solvent by any means which
will permit the evaporation of such solvent into the atmosphere.
J. DRY CLEANING SOLVENTS:
1. No person may operate a drycleaning operation unless the uncontrolled
organic vapor emissions -from such operation have been reduced by at
least 85 percent. Drycleaning operations emitting less than 3 pounds
per hour and less than 15 pounds per day of uncontrolled organic
vapors are exempt from this section J.
2. Any owner or operator of a source subject to this section j shall
achieve compliance with the requirements of subsection 1 of this
section J by discontinuing the use of photochemically reactive
solvents as defined in subsection 10 of section G of this regulation.
3. If incineration is used as a control technique, 90 percent or more
of the carbon in the organic compounds being incinerated must be
oxidized to carbon dioxide.
K. DECREASING OPERATIONS:
No person may use for a degreasing operation any photochemically reactive
solvent as defined in subsection 10 of section G of this regulation unless
the emission of organic materials is controlled to less than 40 pounds per
day or 8 pounds per hour.
L. EFFECTIVE DATE:
Except as otherwise stated in this regulation, said regulation shall become
effective November 28, 1973, as to new sources of hydrocarbon vapor emissions
and effective December 31, 1974 as to existing sources, except that acceptable
compliance schedules and permit applications for all existing sources affected
by this regulation must be received by the Division by no later than March 1,
1974.
E-93
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NOTE: THE FOLLOWING DEFINITIONS ARE TO BE ADDED TO THE COMMON PROVISIONS
REGULATIONS, SECTION I, ENTITLED, "DEFINITIONS."
Adopted :
Effective Date:
September 13, 1973
November 1973
AMENDMENT
TO
COMMON PROVISIONS REGULATIONS
I. DEFINITIONS:
DECREASING
The operation 'of using an organic solvent as a
surface cleaning agent prior to fabricating,
surface coating, electroplating, or any other
process.
DRYCLEANING
A process by which an organic solvent is used
in the commercial cleaning of garments and
other fabric material.
PETROLEUM
DISTILLATE
Any finished and intermediate products which
are manufactured in crude petroleum processing
and finishing operations having a vapor pressure
of 1.5 p.s.i.a. or greater including gasoline
manufactured from any source or by using any
process.
SUBMERGED
FILL PIPE
Any gasoline or petroleum distillate tank fill
pipe the discharge of which is entirely submerged
when the liquid level is 6 inches above the
bottom of the tank. "Submerged fill pipe," when
applied to a tank which is loaded from the side,
is defined as any fill pipe the discharge opening
of which is entirely submerged when the liquid
level is 18 inches above the bottom of the tank.
E-94
-------
Adopted: November 27, 1973
Effective: May 1, 1974
REGULATION NO. 8
Regulation to Control the Emissions of
Chemical Substances and Physical Agents
I. Effective Areas and Dates of Regulation;
This regulation shall apply statewide. This regulation shall become
effective twenty (20) days following publication by mailing pursuant
to Section 3-16-2(11)(k) C.R.S. 1963, as amended, for new air contam-
ination sources and effective July 1, 1974 for existing sources.
II. Information Statement - New Sources:
No person shall construct a new, or modify an existing air contamination
source which may emit one or more chemical substances or physical
agents listed in Section IV of this Regulation No. 8 without first
submitting to the Division pursuant to Regulation No. 3 - Permit
System, acceptable information and preventive control measures,
where necessary, for said agents and substances as follows:
A. Types and quantities of substances and agents to be emitted;
B. allowable emission rates from openings as determined in
Section III of this regulation (show calculations);
C. frequency and duration of emissions;
D. potential contributions of agent and substance emissions to
localized and air basin air pollution problems unless deemed
unnecessary by the Division.
1. applicable climatic conditions and topographical
features affecting emission diffusion;
2. existing density, proximity and expected growth of
human and other habitation; and
3. the preventive steps to be taken, where necessary, to
control agent and substance emissions and, if applicable,
steps to prevent odor, photochemical reactivity, toxicity,
and damage to materials.
E-95
-------
III. Emission Limitations for Kew and Existing Sources:
A. No person shall cause or permit the emission of any chemical
substance or physical agent listed in Section IV of this
Regulation No. 8 as excerpted from the 1973 edition of
"Threshold Limit Values" (TLV) as published by the American
Conference of Governmental Industrial Hygienists (ACGIH) to
exceed the allowable emission rate as determined herein:
1. For substances and agents with a "C" prefix, the
allowable emission rate from any opening shall be
determined as follows:
Multiply the Threshold Limit Value
(mg/M3) from Section iv of this
regulation by the Factor "A" deter-
mined by using Table I.
2. For substances and agents without a "C" prefix the
allowable emission rate from any opening shall be
determined as follows:
First multiply the Threshold Limit Value
(mg/M3) from Section IV of this
regulation by the Factor "A" determined
by using Table I; then multiply by the
excursion factor as determined by using
Table II.
B. Application:
Only those substances and agents with numerical limit values
on the list shall be subject to this Regulation No. 8.
C. Exemptions:
1. Gasoline and diesel-powered engines shall not be subject
to this Regulation No. 8.
2. Carbon Dioxide
3. Oxides of Nitrogen from combustion processes under
500,000 BTU's/hr.
4. Sulfur Dioxide from this Regulation No. 8.
D. Relationship to Other Air Quality control Regulations:
Any person subject to this regulation must also conform to the
requirements of all other Commission regulations and meet the
most stringent requirements when inconsistency or other require-
ments exist.
E. -Sampling:
Sampling methods shall be subject to prior approval by the
Division as specified by the Division of Laboratory Services,
Colorado Department of Health.
E-96
-------
TABLE I
PROCEDURE AND NOMOGRAPH FOR DETERMINING FACTOR "A"
Normally, the allowable emission rate of this Regulation No. 8 will not
allow concentrations of substances and agents to exeed l/30th of the T.L.V.
at the ground level point of maximum concentration downwind from the emission
point. The following Table for finding plume rise is based upon the Moses-
Kraimer plume rise technique-'-. The nomograph simplifies an air pollution
predictive modeling technique based upon the Pasquill-Gifford diffusion
equation .
The following illustration identifies terms pertinent to determining
Factor "A". It also shows emissions from an opening as a stack, diffusing
with ambient air, until the emission-air mixture strikes ground level, the
point of critical concern.
Effective
Stack Height
(He)
Substances and Agents
Mix with Ambient Air
and Diffuse
Stij
ck
Height h
tance of emission point
above ground level)
•Point of Maximum Ground
Level Concentration
1/30 T.L.V.
Ground ///////////////////////////////////////////////////////////////////////////
level
1. "Moses-Kraimer Plume Rise Technique," journal of the Air Pollution
Control Association; Vol. 22, No. 8, August, 1972, pp 621-630
2. "Pasquill-Gifford Diffusion Equation," Workbook of Atmospheric
Diffusion Estimates, U.S.-H.E.W., PHS Pub. No. 99-AP 26, 1969
E-97
-------
Data Needed:
1. h (stack height) being the height in meters (M) of point
of emission into atmosphere above ground level.
2. Effluent flowrate being the flowrate in cubic meters
per second(M3/sec) of effluent gases, corrected to actual
conditions exiting from the opening.
3. Temperature of effluent in degrees centigrade (°C-Celsuis).
Calculations Procedure:
1. Determine heat emission rate (Q^) in kilocalories per
second (Kcal/sec) as follows:
Qfr = 0.25* x Temp.(°C) x Flowrate, (M3/sec)
Note: Use Q^ = flowrate in M3/sec if effluent
temperature equals or is less than 0°C.
2. Determine plume rise (Ah) as follows:
Qh (Kcal/sec) ( h (M)
0 to but not including 100 11 meters
100 to but not including 1,000 46 meters
1,000 to but not including 10,000 54 meters
10,000 and above 251 meters
3. Determine effective stack height (He) in meters as follows:
He = h + A h
4. Determine Factor "A" (103M3/sec) by entering Nomograph
(Table I-A) with effective stack height (He) and left-
hand side, then proceed horizontally to the right until
Line one is intersected, then proceed vertically upward
until Line two is intersected. Again proceed horizontally
to the right and read off Factor "A" (!03M3/sec) . if the
effective stack height (h) is below twelve (12) meters,
Factor "A" shall equal 0.034 (103M3/sec).
Units of the constant 0.25 are Real
E-98
-------
TABLE I-A
TLV FACTOR "A" NOMOGRAPH
NOTE: For effective stack heights
of less than 12 meters,
Factor "A" equals 0.034.
1000 _i
500
400
300 -i
.EFFECTIVE
STACK
HEIGHT, He
(meters)
200
100
so
40
30
20
E-99
-------
TABLE II
DETERMINATION OF EXCURSION FACTOR
Note: Excursion factors relate 7- or 8-hour exposures to
maximum allowable short-term concentrations. These
factors are not to be used with compounds having a
"C" prefix as shown in the A.C.G.I.H. list. Also,
excursion factors shall not be used if emission
durations exceed nine (9) consecutive hours in any
24-hour period.
TLV IN mg/M3 FROM SECTION IV EXCURSION
OF THIS REGULATION NO. 8 FACTOR
0 - THROUGH BUT NOT INCLUDING 1 mg/M3 3
1 - THROUGH BUT NOT INCLUDING 10 mg/M3 2
10 - THROUGH BUT NOT INCLUDING 100 mg/M3 1.5
100 - THROUGH BUT NOT INCLUDING 1,000 mg/M3 1.25
E-100
-------
ALLOWABLE EMISSION CALCULATION EXAMPLES
EXAMPLE ONE:
Given - Actual Stack Height (h) = 489 feet (149. meters*)
Stack Temperature = 160°C
Effluent Flowrate = 714.3 (M3/sec)
Find - Allowable Emission Rate for Hydrogen Bromide (HBr)
Solution - 1. Determine Effective Stack Height
a. From Procedure No. 1, page 4 of this
Regulation No. 8, heat emission rate becomes,
Qh = 0.25 x Temperature (°C) x effluent flowrate (m3/sec)
= 0.25 (160°C)(714.3 m3/sec)
= 28,572 Kilocalories/Second
b. From Procedure No. 2, page 4,
Qh = 28,572 (Kcal) is greater than 10,000,
( sec)
Therefore, Plumerise Ah = 251 meters.
c. From Procedure No. 3, page 4, effective
stack height becomes,
He = h + Ah
= 149(M) + 251 (M)
= 400 meters
Enter Table I-A as shown. Proceeding horizontally to
Line One then vertically to Line Two and again hori-
zontally to the scale where Factor "A" is determined
to be 2.4 x
2.
102 or 240 (103M3/sec).
3.
The TLV for HBr is 10 mg/M3 as found on page 11 of
this regulation. The excursion factor from Table II
is 1.5 for 9-hour workdays.
4. The product (TLV)x(Excursion Factor)x(Factor A) equals:
10(1.5)(240) = 3600 g/sec
providing emissions do not continue
beyond 9 hours in any 24-hour period.
EXAMPLE TWO;
Given
Find
Solution
Same conditions as Example One.
Allowable emission concentration of Formaldehyde.
1. Following a similar procedure, He, again equals 400 meters*
2. Again, this results in a Factor "A" of 240.
3. The TLV for Formaldehyde is 3 mg/M3.
4. Formaldehyde has a "C" prefix, therefore the allowable
emission rate equals:
(TLV) x (Factor "A") = (3)(240) ~ 720 g/sec
*1 meter equals 3.28 feet
E-101
-------
IV. Affected Chemical Substances and Physical Agents:
A. Special Compounds (Use instead of T.L.V. list)
The following compounds shall be considered in a manner
described in III.A.(2) of this Regulation No. 8. Values
listed herein shall be substituted for a T.L.V. value in
the prescribed calculation procedure. This compound shall
be treated as a "C" value without application of excursion
factors.
1. LEAD 0.04 mg/M3 (USE AS A "C" PREFIX LIMIT)
2. G.B. NERVE AGENT 0.0009 mg/M3 (USE AS A "C" PREFIX LIMIT)
3. MUSTARD 0.042 mg/M3 (USE AS A "C" PREFIX LIMIT)
B. in addition to the requirements of IV.A., the following shall
apply to G.B. Nerve Agent and Mustard Gas:
No person shall cause or permit emissions of the following
substances from any opening to exceed the limits listed below:
Maximum Relation to
Air Contaminants Concentration Time _ T.L.V.
G.B. Nerve Agent 0.003 mg/M3 2-hr No T.L.V.
(methylisopropoxyfluoro-
phosphine oxide)
Mustard 0.03 mg/M3 1-hr No T.L.V.
(dichlorodiethyl sulfide)
E-102
-------
ADOPTED AT THE 35TH ANNUAL MEETING OF THE AMERICAN CONFERENCE
OF GOVERNMENTAL INDUSTRIAL HYGIENISTS - BOSTON, MASSACHUSETTS,
MAY 21 - 25, 1973
Substance
ADOPTED VALUES (in Alphabetic Order)
na> mg/M3
PPm°
Abate
+ Acetaldehyde 100
Acetic acid 10
-f-C Acetic anhydride 5
Acetone 1,000
Acetonitrile 40
2-Acetylamino-
fluorene - Skin
Acetylene F
Acetylene dichloride,
see 1, 2-Dichloro-
ethylene
Acetylene tetrabromide 1
Acrolein 0.1
Acrylamide - Skin
Acrylonitrile - Skin 20
Aldrin - Skin
Allyl alcohol - Skin 2
Allyl chloride 1
*C Allyl glycidyl ether
(AGE) (10)
Allyl propyl disul- 2
fide
Alundum (Alo03)
4-Aminodiphenyl -
Skin
2-Aminoethanol, see
Ethanolamine
2-Aminopyridine
+ Ammonia
* Ammonium chloride,
fume
Ammonium sulfamate
(Ammate)
n-Amyl acetate 100
sec-Amyl acetate 125
0.5
25
a)
10
180
25
20
,400
70
A2
14
0.25
0.3
45
0.25
3
5
(45)
12
E
Ib
2
18
10
10
525
650
mg/M
19
0.5
0.5
0.3
0.5
0.2
Substance ppm'
Aniline - Skin 5
Anisidine(o, p-
isomers) - Skin
Antimony & compounds
(as Sb)
ANTU(alpha naphthyl
thiourea)
Argon F
Arsenic & com-
pounds (as As)
Arsine 0.05
Asphalt (petroleum)
fumes - 5
Azinphos methyl -
Skin - 0.2
Barium (soluble
compounds) - 0.5
C Benzene(benzol) -
Skin 25 80
Benzidine - Skin - A
p-Benzoquinone,see
Quinone
Benzoyl peroxide - 5
Benzyl chloride 1 5
Berylium - 0.002
4- Bismuth telluride - 10
-f Bismuth telluride(se-doped)~ 5
Biphenyl, see
Diphenyl
Boron oxide - 10
Boron tribromide 1 10
Z Boron trifluoride 1 3
Bromine 0.1 0.7
Bromine penta-
fluoride 0.1 0.7
3b)
E-103
-------
Substance
a) mg/M3b') Substance
ppm
a-)
mg/M-
Bromoform - Skin 0.5
Butadiene (1,3-
butadiene) 1,000
+ Butane. 500
Butanethiol, see
Butyl mercaptan
2-Butanone 200
2-Butoxy ethanol
(Butyl Cellosolve)
Skin 50
Butyl acetate (n-
butyl acetate) 150
sec-Butyl acetate 200
tert-Butyl acetate 200
Butyl alcohol 1 00
sec-Butyl alcohol 150
tert-Butyl alcohol 100
C Butylamine -Skin 5
C tert-Butyl chromate
(asCrC-3) - Skin
n-Butyl glycidyl
ether (BGE) 50
Butyl mercaptan 0.5
p-tert-Butyltoluene 10
Cadmium (Metal dust
and soluble salts)
C Cadmium oxide
fume (as Cd)
Calcium carbonate
Calcium arsenate
Calcium oxide
Camphor (Synthetic) 2
Carbaryl (SevinR)
Carbon black
'* Carbon dioxide 5,000
Carbon disulfide -
Skin 20
Carbon monixide 50
Carbon tetrachloride -
Skin 10
Cellulose (paper
fiber)
Chlordane - Skin
Chlorinated camphene -
Skin
Chlorinated diphenyl
oxide
Chlorine 1
Chlorine dioxide 0.1
CChlorine trifluoride 0.1
C Chloroacetaldehyde 1
2,200
1,200
590
240
710
950
950
300
450
300
15
0.1
270
1.5
60
0.2
0.1
E
1
5
12
5
3.5
9,000
60
55
65
0.5
0.5
0
.5
3
0.3
0.4
3
oc-Chloroaceto-
phenone(phen-
acylchloride) 0.05 0.3
Chlorobenzene
(monochloro-
benzene) 75 350
o-Chlorobenzyli-
dene malono-
nitrile (OCBM) -
Skin 0.05 0.4
Chlorobromome-
thane 200 1,050
2-Chloro-l,3-
butadiene, see
Chloroprene
Chlorodiphenyl
(42% Chlorine) -
Skin - I
Chlorodiphenyl
(54% Chlorine) -
Skin - 0.5
1-Chloro, 2,3-
epoxypropane, see
Epichloraydrin
2-Chloroethanol, see
Ethylene chlorohydrin
Chloroethylene, see
Vinyl chloride
C Chloroform
(trichloromethane) 25 120
1-Chloro-l-nitropro-
pane 20 100
Chloropicrin 0.1 0.7
Chloroprene (2-chloro-
1, 3-butadiene) -
Skin 25
Chromic acid and
chromates (as CrOo)
Chromium, sol. chromic,
chromous salts as Cr -
* Metal & insol. salts A
la
90
0.1
0.5
(1.0)
+ Coal dust (Bituminous)
(Respirable dust frac-
tion 5% quartz)(If
5% quartz use re-
spirable mass formulas
Coal tar pitch vola-
tiles (benzene sol-
uble fraction) an-
thracene, BaP, phen-
anthrene, acridine,
chrysene, pyrene)
Cobalt, metal fume
and dust
la
0.2
0.1
E-104
-------
Substance
ppm
**
C
C
**
Copper fume
Dusts and Mists
Corumdum (A^O^)
Cotton Dust
(raw)
Crag herbicide
Cresol(all isomers)
Skin 5
Crotonaldehyde 2
Cumene - Skin 50
Cyanide (as CN)-
Skin
Cyanogen 10
Cyclohexane 300
Cyclohexanol 50
Cyclohexanone 50
Cyclohexene 300
Cyclopentadiene 75
2,4-D
DDT
DDVP, see
Dichlorvos
Decaborane - Skin 0.05
Demetorr* - Skin
Diacetone alcohol
(4-hydroxy-4~
me thy1-2-penta-
:-.none) 50
1,2-Diaminoethane, see
Ethylenediamine
Diazinon - Skin
Diazomethane 0.2
Diborane 0.1
1,2-Dibromoethane
(ethylene dibromide)
-Skin 20
Dibrom
2-N Dibutylamino-
e.thanol - Skin 2
Dibutyl phosphate 1
Dibutylphthalate
Dichloracetylene 0.1
0-Dichlorobenzene 50
p-Dichlorobenzene 75
Dicholorbenzidine -
Skin
Dichlorodifluoro-
me thane 1,000
mgAr
0.1
1
E
(1)
10
22
6
245
,050
200
200
,015
200
10
1
0.3
0.1
240
0.1
0.4
0.1
145
3
14
5
5
0.4
300
450
A1
4,950
Substance
Ppm
mg/M
-*>
l,3-Dichloro-5,5-
dimethyl hydantoin - 0.2
4- 1,1-Dichloroethane 200, 820
1,2-Dichloroethane 50 200
l,2-Dichloroethylene200 790
+ Dichloroethyl ether
Skin 5 30
Dichloromethane,
see Methylene
chloride
Dichloromonofluoro-
methane 1,000 4,200
Cl,l-Dichloro-l-
nitroethane 10 60
1, 2-Dichloropro-
pane, see Propylene-
dichloride
Dichlorotetrafluo.ro-
ethane 1,000 7,000
Dichlorvos (DDVP)
Skin - 1
Dieldrin - Skin - 0.25
Diethylamine 25 75
Diethylamino
ethanol - Skin 10 50
* Diethylene triamine -
Skin 1 4
Diethylether, see
Ethyl ether
Difluorodibromo-
methane 100 860
C Diglycidyl ether
(DGE) 0.5 2.8
Dihydroxybenzene, see
Hydroquinone
+• Diisobutyl ketone 25 150
Diisopropylamine-
Skin 5 20
D ime thoxyme th ane,
see Methylal
Dimethyl aceta-
mide - Skin 10 35
Dimethylamine 10 18
4-Dimethylaminoazo-
benzene - A
Dimethylaminoben-
zene, see Xylidene
E-105
-------
Substance
ppm
a)
DimethyIaniline
(N-dimethylaniline)
Skin 5
Dimethylbenzene, see
Xylene
Dimethyl 1, 2-
dibromo-2-dichloro-
ethyl phosphate,
see DiBrom
Dimethylformamide -
Skin 10
2,6-Dimethylhep-
tanone, see Diiso-
butyl ketone
1,1-Dimethylhydrazine
-Skin 0.5
DimethyIphthalate
DimethyIsulfate-
** Skin (1)
Dinitrobenzene
(all isomers)-
Skin
Dinitro-o-cresol -
Skin
Dinitroltoluene -
Skin
** Dioxane (Diethylene
dioxide_ -Skin 100
Diphenyl 0.2
Diphenyl amino
DiphenyImethane
diisocyanate(see
Methylene bisphenyl
isocyanate (MDI)
Dipropylene glycol
methyl ether -
Skin 100
+ Diquat
Si-sec, octyl phthalate
(Di-2-ethylhexylph-
thalate)
Emery
Endosulfan (Thiodan )-•
Skin
Endrin - Skin
Epichlorhydrin-
Skin 5
EPN -Skin
1,2-Epoxypropane, see
Propyleneoxide
2 ,3-Epoxy-l-propanol,
see Glycidol
mg/M'
25
3b)
Substance
ppm
a)
mg/M
3b)
30
1
5
(5)
1
0.2
1.5
360
1
10
600
.05
5
E
0.1
0.1
19
0.5
Ethane F
Ethanethiol, see
EthyImereaptan
Ethanolamine 3
+ 2-Ethoxyethanol -
Skin 100
2-Ethoxyethylacetate
(Cellosolve ace-
tate - Skin 100
Ethyl acetate 400
Ethyl acrylate -
Skin 25
Ethyl alcohol
(ethanol) 1,000
Ethylamine 10
Ethyl sec-amyl
ketone (5-methy1-
3-heptanone) 25
Ethyl benzene 100
Ethyl bromide 200
Ethyl butyl ketone
(3-Heptanone)
Ethyl chloride
Ethyl ether
Ethyl formate
Ethyl mercaptan
Ethyl silicate
Ethylene
Ethylene chloro-
hydrin - Skin 5
Ethylenediamine 10
Ethylene dibromide,
see, 1,2-Dibromo-
ethane
Ethylene dichloride,
see, 1,2-Dichloro-
e thane
C Ethylene glycol dini-
trate and/or Nitro- ^\
glycerin- Skin 0.2
Ethylene glycol mono-
methyl ether ace-
tate (Methyl
cellosolve acetate)
-Skin 25
Ethylene imine -
Skin 0.5
Ethylene oxide 50
Ethylidine chloride,
see 1, 1-Dichloro-
ethane
N-EthyImorpholine-
Skin 20
6
370
540
1,400
100
1,900
18
130
435
890
50
000
400
100
0.5
100
F
230
2,600
1,200
300
1
850
-
16
25
120
1
90
94
E-106
-------
Substance
ppm
a)
mg/M
3b)
Substance
a)
ppm ' mg/M
000
2
5
5
(50)
5,600
3
9
20
(200i
B
0.6
E
E
Ferbam - 10
Ferrovana-
dium dust - 1
Fluoride (as F) - 2.5
+ Fluorine 1 2
Fluorotrichloro-
me thane
* C Formaldehyde
Formic acid
Furfural - Skin
Vurfuryl alcohol
Gasoline
-f Germanium tetra-
hydride(Germane) 0.2
Glass , fibrous
or dust
Glycerin mist
Glycidol (2,3 epoxy-
1-propanol) 50 150
Glycol monoethyl
ether, see 2-Etho-
xyethanol
Graphite, (Synthetic) - E
Guthion, see Azinphos-
methyl
Gypsum - E
Hafnium - 0.5
Helium F
Heptachlor -
Skin - 0.5
Heptane (n-heptane) 500 2,000
Hexachloroethane -
Skin 1 10
Hexachloronaphthalene
-Skin - 0.2
Hexafluoroacetone 0.1 0.7
Hexane (n-hexane 500 1,800
2-Hexanone 100 410
Hexone (Methyl
isobutyl ketone) 100 410
sec-Hexyl acetate 50 300
Hydrazine - Skin 1 1.3
Hydrogen F
Hydrogen bromide 3 10
C Hydrogen chloride 5 7
Hydrogen cyanide -
Skin ' 10 11
Hydrogen fluoride 3 2
Hydrogen peroxide 1 1.4
Hydrogen selenide 0.05 0.2
Hydrogen sulfide 10 15
Hydroquinone - 2
Indene 10 45
Indium and com-
pounds, as In - O.=l
C Iodine 0.1 1
** Iron oxide fume - 10
* Iron penta-
carbonyl 0.01 0.08
Iron salts,
soluble, as Fe - 1
Isoamyl acetate 100 525
Isoamyl alcohol 100 360
Isobutyl acetate 150 700
Isobutyl alcohol 100 300
** Isophorone
Isopropyl acetate 250 950
Isopropyl alcohol 400 980
Isopropylamine 5 12
+ Isopropylether 250 1,050
Isopropyl glycidyl
ether (IGE) 50 240
Kaolin _ £
Ketene 0.5 0.9
Lead - 0.15
Lead arsenate - 0.15
Limestone - E
Lindane - 0.5
Lithium hydride _ 0.025
L.P.G. (Liquified 1,800
petroleum gar.) 1,000 1,800
Magnesite - E
Magnesium oxide - 10
fume
Malathion -Skin - 10
Maleic anhydride 0.25 1
C Manganese and com-
pounds , as Mn - 5
Marble - E
Mercury (Alkyl com-
pounds - Skin - 0.01
Mercury (All forms
except alkyl) - 0.05
Mesityl oxide 25 100
Methane F
Methanethiol, see
Methyl mercaptan
Methoxychlor - 10
2-Methoxyethanol -
Skin (Methyl cello-
solve) 25 80
E-107
-------
Substance
ppm
Methyl acetate 200
Methyl acetylene 1,000
(propyne)
Methyl acetylene-
propadiene mixture
(MAPP) 1,000
Methyl acrylate -
Skin 10
Methylacrylonitrile-
Skin 1
Methylal (dimethoxy-
methane 1,000
Methyl alcohol (meth-
anol) 200
Methylamine 10
Methyl amyl alcohol,
see Methyl isobutyl
carbinol
Methyl 2-cyanoacry- 2
late
Methyl isoamyl 100
ketone (2-Heptanone)
Methyl bromide -
Skin
Methyl butyl ketone, see
2-Hexanone
Methyl cellosolve -
Skin
see 2-Methoxyethanol -
Methyl cellosolve
acetate - Skin
see Ethylene
glycol mono-
methyl ether
acetate
Methyl chloride 100
Methyl chloroform 350
Methylcyclohexane 500
MethyIcyclohexanol 50
o-Methylcyclo-
hexanone - Skin
Methylcyclopenta-
dienyl manganese
tricarbony 1(as
Mn) - Skin 0.1
Methyl derneton -
Skin
Methyl ethyl ketone
(MEK), see 2-
Butanone
Methyl formate 100
Methyl iodide -
Skin 5
mg/M
610
1,650
1,800
35
3
3,100
260
12
8
475
465
3b)
210
1,900
2,000
235
230
0.2
0.5
250
28
Substance ppm£
Methyl isobutyl
carbinol -
Skin 25 100
Methyl isobutyl
ketone, see
Hexone
Methyl isocyanate-
Skin 0.02 0.05
Methyl mercaptan 0.5 1
Methyl methacry-
late 100 410
Methyl parathion
Skin - 0.2
Methyl propyl
ketone, see 2-
Pentanone
C Methyl silicate 5 30
C x Methyl styrene 100 480
C Methylene bis-
phenyl isocya-
nate (MDI) 0.02 0.2
Methylene chloride
(dichloromethane) (500) (1,740)
Molybdenum
(soluble compounds) - 5
(insoluble com- - 10
pounds)
Monomethyl aniline
Skin 2 9
C Monomethyl hydra-
zine-Skin 0.2 0.35
Morpholine -
Skin 20 70
Naphtha (coal
tar) 100 400
Naphthalene 10 50
B-Naphthylamine
Neon
Nickel carbonyl
Nickel, metal and
soluble com-
pounds (as Ni) - 1
Nicotine - Skin - 0.5
Nitric acid 2 5
Nitirc oxide 25 30
p-Nitroaniline -
Skin 1 6
Nitrobenzene -
Skin 1 5
p-Nitrochloro-
benzene - Skin - 1
A
F
0.00^^0.007
Ib
E-108
-------
400
g)B2
0.05
0.1
30
Substance pprn3' mg/M
4-Nitrodipheny1 ~ A
Nitroethane 100 310
Nitrogen F
Nitrogen di-
oxide 5 9
Nitrogen tri-
fluoride 10 29
Nitroglycerin -
Skin 0.2 2
Nitromethane 100 250
1-Nitropropane 25 90
2-Nitropropane 25 90
N-Nitrosodi-
methylamine
(dimethylnitro-
soamine) - Skin - A^
Nitrotoluene -
Skin
Nitrotrichloro-
methane, see
Chloropicrin
Nitrous oxide
Octochloronaph-
thalene - Skin
Octane
Oil mist,
particulate
Oil mist, vapor
Osmium tetroxide
Oxalic acid
Oxygen difluoride
Ozone
Paraquat -
Skin
Parathion -
Skin
Perlite
Pentaborane
Pentachloro-
naphthalene -
Skin
Pentachloro-
phenol -Skin - 0.5.
Pentaerythritol - £
Pentane 500 1,500
2-Pentanone 200 700
Perchlorethy-
lene 100 670
Perchloromethyl
mercaptan 0.1 0.8
Perchoryl fluoride 3 14
3b)
a)
la
0.1
1,900
5f)
0.002
1
0.1
0.2
0.5
0.1
-mppcf 30
0.005 0.01
0.5
Substance pptn'
Petroleum dis-
tillates
(naphtha) g)fi2
Phenol - Skin 5
p-Phenylene
diamine -
Skin -
Phenyl ether
(vapor) 1
Phenyl ether-
Diphenyl
mixture
(vapor) 1
Phenylethylene ,
see Styrene
Phenyl glycidyl
ether (PGE) 10
Phenylhydra-
zine - Skin 5
Phenothiazine -
Skin -
Phosdrin (Mevin-
phos)R -
Skin -
Phosgene (car-
bonyl chloride) 0.1
Phosphine 0.3
Phosphoric acid -
Phosphorus
(yellow) -
Phosphorus penta-
chloride -
Phosphorus penta-
sulfide -
Phosphorus tri-
chloride 0.5
Phtalic anhydride 2
Picric acid -
Skin -
PivalR (2-Pivalyl-
1 ,3-indand ione) -
Plaster of Paris -
Platinum (Soluble
Salts) as Pt -
Polychlorobi-
phenyls , see
Chlorodiphenyls
Polytetraf luoro-
ethylene decom-
position products -
19
0.1
7
60
22
5
0.1
0.4
0.4
1
0.1
1
1
3
12
0.1
0.1
E
0.002
B
E-109
-------
Substance
Propane
B Propiolactone
Propargyl
alcohol - Skin
n-Propyl acetate
Propyl alcohol
n-Propyl nitrate
Propylene dichlo-
ride (1,2-Dichloro-
ppm"
mg/M
3b)
1
200
200
25
75
propane)
* Propylene glycol
monomethyl
ether 100
Propylene imine -
Skin 2
Propylene oxide 100
Propyne, see
Methylacety-
lene
Pyre thrum
Pyridine 5
Quinone 0.1
RDX - Skin
Rhodium, Metal
fume and
dusts (as Rh)
Soluble salts
Ronnel
* Rosin Core Solder,
Pryolysis products
(as formaldehyde)
Rotenone(commercial)
Rouge
Selenium com-
pounds (as Se)
Selenium hexafluo- 0.05
ride
+ Silicon
Silicon carbide
Silver, metal
and soluble com-
pounds
Sodium fluoro-
acetate (1080) -
Skin
** Sodium hydroxide
Starch
Stibine 0.1
Stoddard 'solvent 200
Strychnine
+C Subtillsins(Proteolytic
enzymes as 10070 pure
crystalline enzyme)
840
500
110
350
360
5
240
5
15
0.4
1.5
0.1
0.001
10
0.1
5
E
0.2
0.4
10
E
0.01
0.05
2
E
0.5
1,150
0.15
0.0003
Substance ppm3' mg/M"
Styrene (Monomer)
(Phenyl ethy- 100 420
lene)
Sucrose - E
Sulfur dioxide 5 13
Sulfur hexa-
fluoride 1,000 6,000
Sulfuric acid - 1
Sulfur mono- 1 6
chloride
Sulfur penta-
fluoride 0.025 0.25
+Sulfur tetrafluoride 0.1 0.4
""Sulfuryl fluo-
ride 5 20
Systox, see
Demeton
2,4,5T - 10
Tantalum - 5
TEDP - Skin - 0.2
Teflon^ decom-
position pro-
ducts - B-*-
Tellurium - 0.1
Tellurium hexa-
fluoride 0.02 0.2
TEPP - Skin - 0.05
C Terphenyls 1 9
1,1,1,2-Tetra-
chloro-2,
2-difluoro-
ethane 500 4,170
1,1,2,2-Tetra-
chloro-1, 2-
difluorethan 500 4,170
1,1,2,2-Tetra-
chloro-ethane
Skin 5 35
Tetrachloro-
ethyl.cne, see
Perchloroethy-
lene
Tetrachloro-
methane, see
Carbon tetra-
chloride
Tetrachloro-
naphthalene-
Skin - 2
E-110
-------
a\
Substance ppm '
Tetraethyl lead
(as Pb) -
Skin
Tetrahydrofuran 200
Tetramethyl
lead .(as Pb)
Skin
Tetramethyl succin-
onitrile - Skin 0.5
Tetranitromethane 1
Tetryl (2,4,6-
trinitrophenyl-
methylnitr-
mine) - Skin
Thallium (soluble
compounds) -
Skin (as Ti)
ThiramR
Tin (inorganic com-
pounds , except
SnH^ and SnC>2)
as Sn
Tin (organic
compounds) -
Skin (as Sn)
Tin oxide
Titanium dioxide
- Toluene 100
C Toluene- 2,4-
diisocyanate 0.02
o-Toluidine 5
Toxaphene, see
Chlorinated
camphene
Tributyl phos-
phate
1,1,1-Trichloro-
ethane , see
Methyl chloro-
form
1,1,2-Trichloro
ethane - Skin 10
Trichloroethylene 100
Trichlorome-
thane , see
Chloroform
Trichloronap-
th;1ane-
Skin
3b)
mg/M
o.iooh)
590
0.150h)
3
8
1.5
0.1
5
0.1
E
E
375
0.14
22
45
535
3) /
Substance ppm ' mg/M
1,2,3-Trichloro-
propane 50 300
1,1,2-Trichloro-
1,2,2-trifluoro-
ethane 1,000 7,600
Triethylamine 25 100
Trifluoromono-
bromomethane 1,000 6,100
Trimethyl ben-
zene 25 120
2,4,6-Trinitto-
phenol, see
Picric acid
2,4,6-Trinitro-
phenyl-methyl-
nitramine, see
Tetryl
Trinitrotoluene - - 1.5
Skin
Triorthocresyl
phosphate - 0.1
Triphenyl phos-
phate - 3
Tungsten and
compounds, as
W
Soluble - 1
Insoluble - 5
Turpentine 100 560
Uranium (natural)
soluble and
insoluble com-
pounds , as U - 0.2
Vanadium (V^Oc), as
V
Dust - 0.5
* C Fume - 0.05
Vinyl acetate 10 30
Vinyl benzene, see
Styrene
* Vinyl bromide 250 1,100
Vinyl chloride 200 770
Vinylcyanide, see
Acrylonitrile
Vinyl toluene 100 480
Warfarin - 0.1
Wood dust
(nonallergenic) - 5
3b>
E-lll
-------
g")
Substance ppm ' mg/M
Xylene(xylol) 100 435
Xylidine -
Skin 5 25
Yttrium - 1
Zinc chloride
fume - 1
Zinc oxide
fume - 5
Zirconium com- - 5
pounds (as Zr)
ppm Parts of vapor or gas per million parts of contaminated air by volume
at 25 C and 760 mm. Hg. pressure.
mg/M-* Approximate milligrams . •" substance per cubic meter of air.
NOTES
Capital letters refer to appendices
* 1972 Addition
** See notice of intended changes
+ 1973 Addition
a) Parts of vapor or gas per million parts of contaminated air by
volume at 25°C and 760 mm. Hg. pressure.
b) Approximate milligrams of substance per cubic meter of air.
a) An atmospheric concentration of not more than 0.02 ppm, or
personal protection may be necessary to avoid headache.
e) •< 5-7 um in diameter
f) As sampled by method that does not collect vapor.
g) According to analytically determined composition.
h) For control of general room air, biologic monitoring is essential
for personnel control.
E-112
-------
CHANGES IN ADOPTED VALUES - TENTATIVE LISTINGS
All changes that are recommended are based on documented evidence
which is available from the chairman.
Substance From To
o 3
Cadmium oxide fume 0.2 mg/m • C 0.05 mg/m
Carbon dioxide Documentation to permit TLV of
15,000 ppm provided certain stip-
ulated medical criteria are met.
bisChloroethyl ether C 15 ppm 5 ppm
Copper fume 0.1 mg/nr 0.2 mg/m
Iron Oxide fume 10 mg/nr 5 mg/iir
Paraffin wax fume 1 mg/m 2 mg/nr:
Sodium hydroxide 2 mg/m C 2 mg/m
NOTICE OF INTENDED CHANGES - MINERAL DUSTS
Substance TLV
Asbestos (All types) 5 fibers/ml -=*• 5 in
length n) Aia
-f-Silica flour Use respirable mass
formula for quartz
+Tripoli Use respirable mass
formula for quartz
n) As determined by the membrane filter method at 400-450 X magnification
(4 mm objective) phase contrast illumination. Concentrations 5 fibers/ml
but not to exceed 10, may be permitted for 15-minute periods each hour up
to five tiroes daily.
+1972 Revision or Addition
NOTICE OF INTENDED CHANGES
APPENDIX A
Carcinogens
The Committee lists below those substances in industrial use that have
proven carcinogenic in man or have induced cancer in animals under experimental
conditions. Present listing of those substances carcinogenic for man takes
two forms, those for which a TLV has been assigned (la), and those for x^hich
environmental conditions have not been sufficiently defined to assign at TLV
(Ib).
la. Human Carcinogens - Substances known to be occupational
carcinogens with an assigned TLV: Asbestos, 5 fibers/cc
^>" 5 Am in length; certain insoluble chromates, 0.1 mg/m-';
Coal tar pitch volatiles, 200 ppb; Nickel carbonyl, 1 ppb.
E-113
-------
Ib Human Carcinogens - Substances known to be occupational
carcinogens without an assigned TLV:
4-Aminodiphenyl
Benzidine & its salts
bis-Chloromethyl ether
Chloromethyl ether
beta-Naphthylamine
4-Nitrodiphenyl
For the substances in 1 b, no exposure or contact by any route,
respiratory, skin or oral, as detected by the most sensitive methods,
shall be permitted. "No exposure contact" means herrnitizing the
process or operation by the best practicable engineering methods, and
protecting the worker by proper equipment that will insure virtually
no contact or entry of the carcinogen by any route.
2. Experimental Carcinogens - Industrial substances found to be of high
potency in inducing tumors under experimental conditions in animals:
2-Acetylaminofluorene
3 ,3'-Dichlorobenzidine
4-Dimethylaminoazobenzene
Dimethyl sulfate
Ethylenimine
4,4'-Methylene bis(2-Chloroaniline)
N-Nitrosodimethylamine
beta-Propiolactone
For the above, worker exposure by all routes should be reduced
to a minimum in light of the warning of the potency of these substances
to induce tumors in animals. "Reduced to a minimum means extraordinary
care shall be taken both in manufacture and in handling so that worker
exposure by all routes is kept to an irreducible minimum.
APPENDIX B
1 •> y
B Polytetraf luoroethylene"' Decomposition products. Thermal decomposition
of the fluorocarbon chain in air leads to the formation of oxidized products
containing carbon, fluorine and oxygen. Because these products decompose in
part by hydrolysis in alkaline solution, they can be quantitatively determined
in air as fluoride to provide an index of exposure. No TLV is recommended
pending determination of the toxicity of the products, but air concentrations
should be minimal.
B Gasoline and/or Petroleum Distillates: The composition of these materials
varies greatly and thus a single TLV for all types of these materials is no
longer applicable. In general, the aromatic hydrocarbon content will determine
what TLV applies. Consequently the content of benzene, other aromatics and
additives should be determined to arrive at the appropriate TLV (Elkins, et al.
A.I.H.A.J. 24:99,1963).
wTrade Names: Algoflon, Fluon, Halon, Teflon, Tetran
E-114
-------
APPENDIX C
B.I THRESHOLD LIMIT VALUES FOR MIXTURES:
When two or more hazardous substances are present, their combined
effect, rather than that of either individually, should be given primary
consideration. In the absence of information to the contrary, the
effects of the different hazards should be considered as additive.
That is, if the sum of the following fractions
C^ + Cp + . . .Cn
exceeds unity, then the threshold limit of the mixture should be con-
sidered as being exceeded. C-^ indicates the observed atmospheric
concentration, and T-i the corresponding threshold limit (See Example
lA.a. and lA.c.) .
Exceptions to the above rule may be made when there is good reason
to believe that the chief effects of the different harmful substances
are not in fact additive, but independent as when purely local effects
on different organs of the body are produced by the various components
of the mixture. In such cases the threshold limit ordinarily is
exceeded only when at least one member of the series
( GI +C2 ^
( — + or — etc. )
( Tl T2 )
itself has a value exceeding unity (See Example 1 A.c.).
Antagonistic action or potentiation may occur with some combi-
nations of atmospheric contaminants. Such cases at present must be
determined individually. Potentiating or antagonistic agents are not
necessarily harmful by themselves. Potentiating effects of exposure
to such agents by routes other than that of inhalation is also possible,
e.g. imbibed alcohol and inhaled narcotic (trichloroethylene) .
Potentiation is characteristically exhibited at high concentrations,
less probably at low.
When a given operation or process characteristically emits a
number of harmful dusts, fumes, vapors or gases, it will frequently
be only feasible to attempt to evaluate the hazard by measurement of
a single substance. In such cases, the threshold limit used for this
substance should be reduced by a suitable factor, the magnitude of
which will depend on the number, toxicity and relative quantity of
the other contaminants ordinarily present.
Examples of processes which are typically associated with two or
more harmful atmospheric contaminants are welding, automobile repair,
blasting, painting, lacquering, certain foundry operations, diesel
exhausts, etc. (Example 2 in lA.a.).
E-115
-------
EXAMPLES
THRESHOLD LIMIT VALUES FOR MIXTURES
lA.a. General case, where air is analyzed for each component:
a. Additive effects. (Note: It is essential that the atmosphere
be analyzed both qualitatively and quantitatively for each
component present, in order to evaluate compliance or non-
compliance with this calculated TLV.)
+...=1
Example No. 1:
Example No. 2;
Air contains 5 ppm of carbon tetrachloride (TLV = 10 ppm)
20 ppm of ethylene dichloride (TLV = 50 ppm) and 10 ppm of
ethylene dibromide (TLV = 25 ppm)
Atmospheric concentration of mixture = 5 + 20 + 10 =
35 ppm of mixture
1 +
10
1° + 12 = 25 + 20 + 20 =1.3
50 25 50
Threshold Limit is exceeded. Furthermore, the TLV of
this mixture may be calculated by reducing the total
to 1.0; i.e.
35_
TLV of mixture =1.3 = 27 ppm
Air contains 200 ppm of hexane (TLV = 500 ppm)
100 ppm of methylene chloride (TLV = 500 ppm)
and 20 ppm of perchloroethylene(TLV = 100 ppm)
Atmospheric concentration of mixture = 200 +
100 + 20 = 320 ppm of mixture
200 100 20_ = 200 + 100 + 100 = 400 = 0 8
500 500 +100 500 500
Threshold Limit is not exceeded.
mixture = 320 ,__
„ = 400 ppm
U. o
The TLV of this
lA.b. Special case when the source of contaminant is a liquid mixture
and the atmospheric composition is assumed to be similar to that
of the original material; e.g. on a time weighted average
exposure basis, all of the liquid (solvent mixture)eventually
evaporates.
Additive effects (approximate solution)
1. The percent composition (by weight) of the liquid mixture
is known, the TLVs of the constituents must be listed
in mg/m^,
E-116
-------
TOTE: Though this regulation has
been adopted by the Commission,
it must still be approved by
the State Attorney General's
Office prior to official publi-
cation.
Adopted:
Effective:
July 25, 1974
REGULATION NO. 9
The Control of Automotive Air Pollution
through Motor vehicle Restraints and the Encouragement
of Public Transportation and Carpooling
I.
AREA OF APPLICATION:
II.
This Regulation No. 9 shall apply to the Metropolitan Denver Air
Quality Control Region, which includes the counties of Adams, Arapahoe,
Boulder, Denver, Douglas, and Jefferson.
PREFERENTIAL TREATMENT OF BUSES:
A. By September 1, 1974 (in cooperation with the Denver Regional
Council of Governments, the State Department of Highways and
each city and county government within the Metro Denver Air
Quality Control Region) the Regional Transportation District
(R.T.D.) shall develop and submit to the Commission a feasi-
bility study for demonstrating preferential treatment for
buses and carpools within the Metro Denver Air Quality Control
Region. By July 1, 1975, R.T.D. shall in the same manner develop
and submit to the Commission a regional plan for establishing
preferential treatment for buses and carpools within this region.
This plan shall include implementation steps, time schedules, and
costs for implementing this plan by January 1, 1976.
After the Commission holds a public hearing on and adopts the
plan, each party so identified in the plan as responsible for
a portion of it shall implement that portion.
In connection with the plan, R.T.D. shall demonstrate to the
Division that implementation of the preferential treatment of
buses will not increase the potential for additional motor
vehicle traffic within the affected area.
B. By October 1, 1974, in cooperation with the Denver Regional
Council of Governments, the State Department of Highways, and
major local business and employment center Associations, the
Regional Transportation District (R.T.D.) shall develop and
submit to the Commission a plan for automobile intercept park-
ing facilities and express bus service to employment and
business centers. Said plan shall include an implementation
time schedule and an evaluation of the effect of plan imple-
mentation upon reducing vehicle miles traveled (V.M.T.).
After the commission holds a public hearing and adopts the
plan, each party so identified in the plan as responsible
for a portion of it shall implement that portion.
E-117
-------
C. With respect to the requirements of Sections II.A. and II.B.
of this regulation, R.T.D. shall by October 1 of each year
submit plan revisions and additions for improving the effec-
tiveness of adopted plans.
III. EMPLOYER PLAN REQUIREMENTS FOR CARPOOLING AND MASS TRANSIT INCENTIVES;
A. By November 1, 1974, the Denver Regional Council of Governments
shall submit to the Commission a proposal to establish a uniform
carpooling locator service for the Denver metropolitan area.
B. By February 1, 1975, all public and private employers which employ
more than two hundred fifty (250) employees at one time in any one
plant or other business location shall submit an affidavit, or
plan, to the Division on forms provided by the Division. This
affidavit shall be signed by an authorized company employee. The
affidavit shall state that: 1) The locator service developed as
per Section III.A of this regulation will be provided by the
employer for use by all interested employees; or that: 21 another
carpooling locator service of equal or greater effectiveness will
be used, in the case of an alternative locator service, the
employer must submit for approval by the Division a plan describing
the system and effectiveness of it. The affidavit, or plan, shall
provide the following;
1. That the carpooling locator service must be fully
implemented by April 1, 1975.
2. That the carpooling locator service shall be for the
purpose of matching people to facilitate the trans-
porting of two (2) or more persons per vehicle.
3. A description of employee incentives to encourage the
, use of carpooling; such as -, free or reserved parking
adjustments in favor of carpooled vehicles where
employee parking is provided, imposition of parking
charges on non-carpooled vehicles, or other incentives.
4. A description of measures to encourage employees to use
bicycles and public transportation; such as, posting
information for employees as to the availability of
bicycle lanes and public transportation to and from
the place of employment; and providing incentives for
use of same (reimbursement of fares for use of public
transportation, provision of secure and convenient
parking for bicycles, and/or other similar fringe
benefits).
C. The Requirements of Section III.B shall apply to all public and
private employers which employ more than fifty (50) employees at
one time in any one plant or other business location exactly
six months later than the time requirements of Section III.B
(plan submittal by August 1, 1975 and carpooling locator service
implemented by October 1, 1975),
E-118
-------
D. All employers regulated by this Section m.D shall, on an annual
basis coinciding with the plan submittal date, submit on a form
provided by the Division a brief progress report as to the effec-
tiveness of implementing measures as required in this Section m.D.
IV. MOTOR VEHICLE PARKING;
By March 1, 1975, the Denver Regional Council of Governments (in
cooperation with the State Department of Highways and Regional Transportation
District (R.T.D.) shall provide written advice to the Commission as to the
relationship, if any, between restricting the construction of new parking
spaces in the Denver area and reducing vehicle miles traveled. It shall
also recommend to the Commission parking requirements that may stimulate
the use of public transportation and decrease single passenger vehicle miles
traveled.
E-119
-------
L''JiTr.D]":C'LST,. 'J1 DZnTjE^ fJKOljAL
'^Ss&f ^tfi* ^ i* U i/' ••» '-Si ^ - aw ;i '*i . ria ' 'v-c/ £ 'i tu
/***• /x:1* ^s wt-i "^ " /7-5*. n •*""', r "•• i ^M '"j, /^t / r"- '' r-"5^-,
[" ' * ' ' ; ' -' ' '' "* /•--'% , ' i' '4
V^ Vj U *. •', L, v '\ „' L.M ^ \, ,» ^ l. uJ" «^.l' ^ ^ ^, ,i M LtfX
Ci K B k«3iM ^^ U fc tai k Ltaa Njri^ h ^2$ **^*f tsyt \^«^* b* \A A ^ feiai-^
Colorado Air Poiiution Control Commission
Adopted : September 10, 3970
Effective Date: December 17, 1970
E-120
-------
SULFUR DIOXIDE
Areas of the State not included in Air Quality Control Areas
Achieve a Short Term Level of: A 24-hour maximum arithmetic mean of
15 micrograiTiG per cubic meter in any 24-hour period and must
not be exceeded more than once in a twelve-month period.
Air Quality Control Areas including the Metropolitan Denver Air Quality
Control Region:
On or before January 1, 1973, achieve a One Hour Level of: A 1-hour
maximum arithmetic mean of 800 micrograms per cubic meter of
air in any 24-hour period, and must not be exceeded more than
once in any 1-month period.
On or before January 1, 1973, achieve a Short Term Level of: A 24-hour
maximum arithmetic mean of 300 micrograms per cubic meter of
air in any 24-rhour period and must not be exceeded more than
once in a 12-month period.
On or before January 1, 1973, achieve a Long Term Level of: An annual
arithmetic mean of all 24-hour concentrations which must not
exceed 60 micrograms per cubic meter of air.
On or before January 1, 1976, achieve a One Hour Level of: A 1-hour
maximum arithmetic mean of 300 microyrams per cubic meter of
air in any 24-hour period, and must not be exceeded more than
once in any 1-month period.
On or ]'afore January 1, 1976, achieve a Short Term Level of: A 24-hour
maximum arithmetic mean of 150 micrograms per cubic meter of
air in any 24-hour period and must not be exceeded more than
once in a 12-rnonth period.
On or before January 1, 1976, achieve a Long Term Level of: An annual
arithmetic mean of all 24-hour concentrations which must not
exceed 25 micrograms per cubic meter of air.
On or before January 1, 1980, achieve a Short Term Level of: A 24-hour
maximum arithmetic mean of 55 micrograms per cubic meter of
air in £iny 24- hour period and must not be exceeded more than
once in a 12-month period.
On or before January 1, 1980, achieve a Long Term Level of: An annual
arithmetic mean of all 24-hour concentrations which must not
exceed 10 micrograms per cubic meter of air.
Method of Testing
The method used to measure sulfur dioxide is the West-Gaeke method. Other
methods may be used if they have been demonstrated to be equally or more specific,
sensitive, and reproducible. Results are expressed as micrograms of sulfur
dioxide per cubic meter of ambient air. These values may be converted to parts
per million by volume by dividing by 2H60. (1 ppm - 28^0 \ig/F>3 at 0°C and 760m>n
Ilg (Torr. ) ) .
ppm - parts per million
ug/m = micrograms per cubic meter of air
E-121
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AMBIENT AIR STANDARDS FOR
METROPOLITAN DENVER AIR QUALITY CONTROL REGION,
AIR QUALITY CONTROL AREAS, AND
THE STATE OF COLORADO
ADOPTED : September 10, 1970
EFFECTIVE: December 1.7, 1970
SUSPENDED PARTICIPATE MATTER;
Areas of the State not included in Air Quality Control Areas
Achieve a Snort Term Level of: A 24-hour maximum of 150 micrograms
per cubic meter of air in any 24-hour period and must not be
exceeded more than once in a twelve-month period.
Achieve a Long Term_ Level of: An annual arithmetic mean of all 24-
hour concentrations which must not exceed 45 micrograms
per cubic meter of air.
Air Quality Control Areas including the Metropolitan Denver Air Quality
Control Region:
On or before January 1, 1973, achieve a Short Term Level of: A 24-hour
maximum of 200 micrograms per cubic meter of air in any 24-
hour period and must not be exceeded more than once in a
twelve-month period.
On or before January 1, 1973, achieve a Lgng_Term Level of: An annual
arithmetic mean of all 24-hour concentrations which must not
exceed 70 microgrems per cubic meter of air.
On or before January 1, 1976, achieve a Short Term Level of: A 24-hour
maximum of 180 micrograras per cubic meter of air in any 24-
hour period and must not be exceeded more than once in a
twelve-month period.
On or before January 1, 1976, achieve a Long Term Level of: An annual
arithmetic mean of all 24-hour concentrations which must not
exceed 55 micrograms per cubic meter of air.
On or before January 1, 1980, achieve a Short Term Level of: A 24-hour
maximum of 150 micrograms per cubic meter of air in any 24-
hour period and must not be exceeded more than once in a
twelve-month period.
On or before January 1, 1980, achieve a Long Term Level of: An annual
arithmetic mean of all 24-hour concentrations which must not
exceed 45 micrograms per cubic meter of air.
Method of Testing
Suspended particulate matter is measured gravimetrically using the high-
volume sampler technique described by the National Air Pollution Control
Administration. Suspended particulate numerical levels are expressed in
micrograms per cubic meter of ambient air sampled.
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TABLE I
AMBIENT AIR STANDARDS FOR
METROPOLITAN DENVER AIR QUALITY CONTROL REGION,
AIR QimLITY CONTROL AREAS, AND
THE STATE OF COLORADO
SUSPENDED PARTICULATg NATTER AND SULFUR DIOXIDE
(Micrograms per cubic meter -
Pollutant
Suspended Particulate
Mattrr3
Short Termc ( -1 ^
Long Term
Sulfur Dioxtdeb
One hour Level
c(i-H
Short Term
Long Term
Won
Designated
Areas
150
45
15
(0.0050)f
Metro-Denver Air Quality Control
Region, and
Designated State Areas
1973
200
70
800
(0.28)f
300
(0.10)f
60
(0.020)f
1976
180
55
300
(0.10)f
150
(0.0f50)f
25
(0.0090)f
1980
150
45
55
(0.020)f
10
(0.0040)f
a. Measured at ambient conditions.
b. 0° Centigrade - 760 mm Hg (Torr.)
c. Short Tern Level
(i) A 24-hour maximum of any 24-hour period and must not be exceeded
more than once in a 12-month period.
(ii) A 24-hour maximum arithmetic mean of any 24-hour period, and must
not be exceeded more than once in a 12-month period.
d. Long Term Level - An annual arithmetic mean of all 24-hour concentrations.
e. One hour Level - A 1-hour maximum arithmetic mean in any 24-hour period,
and must not be exceeded more than once in any 1-month
period.
f• ( ) ~ Equivalent values in parts per million (1 ppm = 2860 ug/m3 at
0°C and 760 mm Hg (Torr)).
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"L I9"
i, j»,<». e> jf^ /*^ i.at
^tiio uy
"*•* vt »!.' : '-' !' i •. i>
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Colorado Air Pollution Control Commission
E-124
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STATEMENT OF POLICY
to
PART IV.A
CO* IKON PROVISIONS APPLICABLE TO BOTH
AUTHORITY TO CONSTRUCT AND PERMIT TO OPERATE
The Commission directs that the Division or Commission staff may
still require persons exempted by Part IV.A of Regulation No. 3
to supply any necessary information to the State for the completion
of emission inventories as may be required for planning purposes.
Adopted June 8, 1972
Colorado Air Pollution Control Commission
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STATEMENT OF POLICY
ON
AGRTCULTUTvAL OPEN BURNIl'TG
The following is hereby declared to be the present policy of the Colorado Air Pollution
Control Commission regarding Agricultural Open Burning and related matters:
1. A primary current need of the Commission is for the accumulation
of informsLion nnd data regarding agricultural burning and
emissions.
2. A voluntary report '.ng system appears to be of greater usefulness
to the Commission ii this regard than the use of a permit system
application form.
3. The implementation of the proposed agricultural burning permit
system under Regulation No. 1 shall be delayed until the
effectiveness of an agricultural open burning inventory system
is evaluated; and subject to further public hearing.
4. The report and recommendations dated November 10, 1972 of the
Agricultural Advisory Committee is adopted, and the Division
is directed to implement an Agricultural Open Burning inventory,
substantially by use of the Inventory Form attached to the
Advisory Committee1s report.
5. The Agricultural Advisory Committee has functions for the
mutual benefit of the /Air Pollution Control Commission and
the agricultural community. It shall be kept operational
through 1974 as requested in its report of November 10, 1972.
6. The permit system provisions of Regulation No. 1 regarding
agricultural open burning shall continue to be the basis (in
the sense of enabling authority) for local enforcement
(including permit systems) regarding agricultural burning.
The adoption of this Policy Statement by the Commission shall
not be deemed to restrict or affect independent local enforce-
ment in this area.
7. The Commission's endorsement of the voluntary, rather than
mandatory, compliance feature of the Agricultural Open Burning
Inventory concept is based in part, upon the apparent lack of
severity of the contribution of agricultural open burning to
the air pollution problems of the State as a whole; is limited
to the facts and circumstances of agricultural open burning;
and does not reflect a general policy of the Commission as to
mandatory vs voluntary compliance by individuals with the
Commission's air pollution controls.
Adopted November 10, 1972
Colorado Air Pollution Control Commission
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SECOND
AMENDED POLICY FOR
ACHIEVING AMBIENT AIR DUALITY STANDARDS ON SCHEDULE
WHEREAS compliance schedules submitted by owners or operators of air
contamination sources may be adequate to achieve the emission control
regulations of the Commission, but not be adequate to achieve Federal
Primary and Colorado State Ambient Air Quality Standards; and
WHEREAS the Commission has adopted (and so has the U.S. Environmental
Protection Agency) an Air Quality Control Implementation Plan for the
State of Colorado that is designed to achieve federal Ambient Air Quality
Standards for particulate matter and sulfur oxides by 1975;
THEREFORE, the Commission directs the Variance Board not to approve
compliance schedules for sources requesting variance unless the Division
does predict that the source, when controlled, will not result in exceeding
the Federal Primary and Colorado State Ambient Air Quality standards, and
that the compliance shcedule will not prevent meeting ambient air quality
standards on schedule.
ALSO, the Commission directs the Division of Air Pollution Control
to supply information to the Variance Board, upon request, to enable the
Variance Board to determine if compliance schedules are adequate to achieve
said ambient air quality standards on schedule.
/.'- '
Lane W. Kiirkpatrick
Technical Secretary
Air Pollution Control Commission
Ja/ic/s P. Lodge, Jr. , Ph. D .
CpaArman
At* Pollution Control Commission
Amended January 5, 1973
2d Amendment, April 26, 1973
Colorado Air Pollution Control Commission
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ADOPTED POLICY
AIR POLLUTION IMPACT - COMPLEX SOURCES
Colorado Air Pollution Control Commission
As a matter of policy, the Commission resolves:
1. That there be a postponement of the approval of the construction
of new freeways in the Denver area (and the enlargement of existing
freeways) until it has been demonstrated in environmental impact
statements for such freeways that such freeways will not adversely
affect air quality (both on a short and long term basis).
2. That any new construction of freeways and other "complex air
pollution sources"* in the Denver metropolitan area and in other
Colorado areas be allowed only when construction of said sources
is not likely to endanger the achievement or maintenance of ambient
air quality standards.
3. In order to meet Federal ambient air quality standards on schedule,
the Commission estimates that a significant decrease of projected
vehicle miles traveled will be necessary in the Denver area. The
Commission feels that automobile traffic should be discouraged while
at the same time less polluting alternate forms of transportation
should be encouraged.
4. That the Colorado Legislature recognize the importance of and pass
legislation mandating the joint use of Land Use and Transportation
planning as necessary tools for the attainment and maintenance of
publicly acceptable levels of air quality by granting sufficient
powers to appropriate agencies for this pvt
7
Wcw^VO
Lane KirKpatLick Ja/AfTs P. Lodge', Jr., Ph.D.
Technical Secretary Cnairman
Air Pollution Control Commission Ayr Pollution Control Commission
^Complex Air Pollution Source (Indirect Source)-
means facilities or activities, which perhaps though non-polluting
in themselves, generate air pollution as a result of adjunct or
secondary activities; for example, by the generation of motor vehicle
traffic.
Adopted April 26, 1973
Air Pollution Control Commission
State of Colorado
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COMMON PROVISIONS REGULATION
Definitions, Statement of Intent and General Provisions
applicable to all emission control regulations adopted by the
Colorado Air Pollution Control Commission
Colorado Air Pollution Control Commission
Adopted : December 9,1971
Effective Date: February 1, 1972
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PROPOSED REGULATIONS
NOTICE OF PUBLIC HEARINGS
before the
COLORADO AIR POLLUTION CONTROL COMMISSION
Pursuant to the provisions of Section 3-16-2 C.R.S. 1963 as amended
(1967-1969 Perm.Cum.Supps.) and 66-31-9 as amended (1971 Perm.Cum.Supps.)
pursuant to which public hearing procedures are herein and will be following,
and of 66-31-6, 66-31-7, 66-31-8 and 66-31-9, as amended, (1971 Perm.Cum.
Supps.) of the "Air Pollution Control Act of 1970", C.R.S. 1963, as amended,
which sections prescribe the legal authority for the Commission to adopt
such regulations or amendments, NOTICE is hereby given that the Colorado Air
Pollution Control Commission, after due and proper notice given pursuant to
said Section 66-31-9, will conduct a public hearing in accordance with the
provisions of Section 3-16-4, C.R.S. 1963, as amended (1969 Perm.Cum.Supps.),
to be held:
JUNE 24, 1974 (Monday)
9:30 a.m. to 5 p.m.
JUNE 25, 1974 (Tuesday)
9:30 a.m. to 5 p.m.
JUNE 27, 1974 (Thursday)
9:30 a.m. to 5 p.m.
BOULDER, COLORADO
National Center for Atmospheric Research
Main Seminar Room
1850 Table Mesa Drive
COLORADO SPRINGS, COLORADO
Colorado Springs Auditorium
Little Theatre
Kiowa and Weber Streets
(Use Weber Street Entrance)
GLENWOOD SPRINGS, COLORADO
County Court House
(District Court)
Corner of Colorado & 8th Avenue
for the purpose of considering and promulgating the following proposals to
amend the Colorado Air Pollution Control Commission's "Air Quality Control
Regulations and Ambient Air Quality standards" in particular amending the
following regulations, copies of which are hereto as proposed:
E-130
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June, 1974
Amend by Adding to:
COMMON PROVISIONS REGULATION - (pp. 1 and 2)
Section III.
Repeal and Reenact
"Smoking Gasoline-Powered Motor
Vehicle Control Region." A
description and map designating
the Denver Air Quality Control
Region as a "Smoking Gasoline-
Powered Motor Vehicle Control
Region" pursuant to Section
40-13-110(1)(a)(ii), Colorado
Revised Statutes, 1963, as
amended. (Counties of: Denver,
Adams, Jefferson, Arapahoe, Douglas,
Gilpin, Clear Creek and Boulder)
REGULATION NO. 3 - (pp. 3-34)
I. Air Contaminant Emission Notice
II. Permits for Direct Air Contaminant Sources
III. Permits for Indirect Air Contaminant Sources
IV. Portable Emission Sources
Note:
(Since a revised Regulation No. 3 had a
public hearing January 8, 1974 which
applied to the Denver Air Quality Control
Region only, the attached Regulation No.
3, Section III dealing with Indirect Air
Contaminant Emission Sources excludes
the Denver Region but applies to the
rest of the State).
REGULATION NO. 7 - (pp. 35 - 46)
Sections: A. Affected State Areas
B. Petroleum Distillate Storage
at Pipeline Termination and
Refineries
C. Petroleum Distillate Transfer
G. Organic Solvents
J. Drycleaning Solvents
L. Effective Date
The Commission will receive oral or written data, evidence, and testimony
and afford interested persons an opportunity to submit views and arguments and
otherwise to participate informally in conferences on the proposals under
consideration with regard to all of the rules, regulations, amendments, and
reenactments and additions proposed for its consideration leading to the
ultimate action by the Commission. Any interested person shall have an
opportunity to participate at said hearings in person or through counsel.
Amend
E-131
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June, 1974
Any person desiring to propose rules, regulations, or amendments in
lieu of those proposed by the Commission may file such other proposal with
Mr. Lane Kirkpatrick, Technical Secretary to the Commission on or before
5 p.m., June 4, 1974, and when so filed, shall be open for public inspec-
tion in Room 319 at the Colorado Department of Health, 4210 East llth
Avenue, Denver, Colorado 80220.
Witnesses at the hearing shall be subject to cross-examination by the
Commission, or by or on behalf of persons who have submitted proprosals
pursuant to the preceding paragraph.
Should all testimony be given to the Commission prior to 5 p.m. on the
date of the hearing, the Commission will close the hearing at such time, but
may hold the record open for further written amendment from those in attend-
ance or represented at said hearing which amended proposals shall be made
available to those requesting copies thereof, for consideration at the next
succeeding Commission meeting.
. The effective date of such amendments and additions to rules and regula-
tions as may be adopted by the Commission will be determined following receipt
of the Attorney General's opinion as to the legality and constitutionality
thereof and shall not be less than thirty (30) days after the same shall have
been published and filed in the office of the Secretary of State of Colorado.
There shall be made available to the public and delivered to anyone
requesting the same, a copy of any rule of the Commission now in effect, if
not otherwise contained among the attached material, or of any notice of
proposed rule-making proceeding in which action has not been completed which,
upon request, shall be certified. The Commission may make a reasonable charge
for supplying such material.
COLORADO AIR POLLUTION CONTROL COMMISSION
Jr., Ph.D., Chairman
u
DATED:
Attachments
Legal List on File with Legal Counsel
Colorado Department of Health
E-132
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PROPOSED AMENDMENT TO
COMMON PROVISIONS REGULATION
PROPOSED SMOKING VEHICLE AREA DESIGNATION
III.
PURSUANT TO SECTION 40-13-110(1)(a)(ii), C.R.S. 1963 AS AMENDED
(1.73, § 5, pp. 745,746) THE AIR POLLUTION CONTROL COMMISSION HEREBY
DESIGNATES THE FEDERAL AIR QUALITY CONTROL REGION WHICH INCLUDES THE
COUNTIES OF ADAMS, ARAPAHOE, BOULDER, CLEAR CREEK, DENVER, DOUGLAS, GILPIN
AND JEFFERSON AS A "SMOKING GASOLINE-POWERED MOTOR VEHICLE CONTROL REGION."
THIS DESIGNATION WILL ENABLE THE ENFORCEMENT OF SAID SECTION BY PEACE
OFFICERS TRAINED BY THE COMMISSION IN OPACITY DETERMINATION. THIS REGION
IS THE SAME REGION TO WHICH PORTIONS OF THE COLORADO STATE IMPLEMENTATION
PLAN APPLIES.
THE COMMISSION UPON REVIEW OF AMBIENT AIR QUALITY DATA HAS DETERMINED
THAT ON AT LEAST THIRTY-ONE (31) OCCASIONS, CARBON MONOXIDE LEVELS EXCEEDED
NINE (9) PARTS PER MILLION (ppm) AVERAGED OVER EIGHT (8)-HOUR NON-OVERLAPPING
PERIODS. THEREFORE THE COMMISSION FEELS REGIONAL DESIGNATION IS WARRANTED
UNDER THE PROVISIONS OF THIS SECTION.
E-133
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E-134
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DRAFT
March 28, 1974
Proposed for Public Hearing
REPEAL AND REENACTMENT OF
REGULATION NO. 3
Regulation Governing Authority to Construct
and
Permit to Operate
Page
' I. AIR CONTAMINANT EMISSION NOTICE 5
II. DIRECT AIR CONTAMINATION SOURCES 7
A. General 7
B. Application and Effective Date 7
C. Definitions and Exceptions 7
D. Preplanning Review 10
E. Authority to Construct 11
F. Impact Statement 17
III. INDIRECT AIR CONTAMINATION SOURCES
A. General 19
B. Application and Effective Date 19
C. Definitions and Exceptions 19
D. Preplanning Review 21
E. Authority to Construct 22
F. Impact Statement 27
IV. PORTABLE EMISSION SOURCES - 30
E-135
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REVISED
REGULATION NO. 3
Regulation Governing Authority to Construct
and
Permit to Operate
I. INSTRUCTIONS, PROCEDURAL GUIDELINES, AND SAMPLE FORMS FOR FILING AN
AIR CONTAMINANT EMISSION NOTICE: (REQUIRED AS PART OF THE IMPACT
STATEMENT FOR DIRECT AIR CONTAMINATION SOURCES).
The Act requires an "air contaminant emission notice" be filed
with the Department prior to the emission of an air contaminant from
any facility, process, or activity. The Commission has defined
insignificant sources exempted from filing a notice as listed in
ARTICLE II.C.2 of Regulation No. 3. Any facility, process, or activity
which is altered, RESULTING in A CHANGE in emission of air contaminants,
must also file an "air contaminant emission notice" with the Department
with respect to such proposed emission. A revised emission notice is
required and shall be filed whenever a significant change in emissions
shall have occurred. (See instructions)
Effective July 10, 1970, no person shall discharge, or cause to
be discharged, into the atmosphere any air contaminant if an "air
contaminant emission notice" has not been filed. Failure to comply
with this provision of the Act is punishable by a fine of not more
than one hundred dollars ($100).
The Air Contaminant Emission Notice may be obtained from the
Colorado Department of Health (see below) or from any local air
pollution control agency in Colorado.
The Air Contaminant Emission Notice is to be completed in tripli-
cate and all copies mailed to:
COLORADO DEPARTMENT OF HEALTH
AIR POLLUTION CONTROL DIVISION
4210 East llth Avenue
Denver, Colorado 80220
E-136
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AIR CONTAMINANT EMISSION NOTICE
INSTRUCTIONS
This form shall include information relating to a single stack or vent. The process, fuel, and control informa-
tion included shall relate to the emissions from this stack. Separate forms shall be filed for each stack or source
of emissions.
A. General Information:
Record the city and county where the equipment is located, number of employees, land area, operating.time, and
percent throughput. - •
B. Stack Information:
This information must be completed by the applicant. The stack height shall be the measured height from ground
level to the top of the stack or vent. Flow rate shall be given in actual cubic feet per minute at stack exit
temperature and pressure.
C. Fuel Information:
Type of Unit: This shall be the equipment that burns the fuel. Example: oil burner, coal burner, gas
burner, or any other unit that utilizes fuel or involves combustion.
Design Rate: Capacity of each fuel burning equipment (BTU/hr.).
Fuel Used: Name the fuel used and print in the space, in line with the equipment that uses the fuel.
Consumption: Print the amount of fuel used per year in units like tons/year, gallons/year, 10° SCF/year.
Heating Value: This shall be given in BTU/unit of fuel.
Percent Annual
Use: This information shall be given for each fuel used separately, to total 100* per year.
" D. Process Information:
Process
Equipment: List the major process equipment that causes or contributes to the emissions from this
stack or vent.
Raw Materials,
etc. List all materials used during each process.
Units/year: List amount of these materials used in proper units/year.
Design Rate: This shall be the design rate of usage of raw materials of the process equipment and shall
be given in proper units per hour.
Finished
Products: Name the finished products from these processes and print the units/year.
£. Control Equipment:
Primary and All air pollution control equipment used on the emissions released by this particular stack
Secondary or vent shall be reported. When two or more controls are used, the first type of control
Controls: equipment in line will be the primary collector, and the others will be secondary controls.
Collection
Efficiency: This shall include the total efficiency of 411 the above control equipment.
Estimated
Emissions: This figure shall be estimated at the exit end of the stack or vent in tons/year.
Method of
Estimation: (e.g., source test, emission factors, experience with similar sources, or guesswork)
This subnuttal should include a simple block fiaure flow duaram showina all process equipment, flow of
materials, and all emission points with emission estimates. Include manufacturers' brochures, if available.
Mail this information to: Air Pollution Control Division
Colorado Department of Health
4210 East llth Avenue
Denver, Colorado 80220
APC-200A (11-72-20)
E-137
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Notice No.
-------
II. DIRECT AIR CONTAMINATION SOURCES
A. GENERAL -
No person shall construct or modify any new DIRECT air contamination
source mentioned in Paragraph C without receiving written authorization
from the Division. SOURCES WHICH MEET THE DEFINITION OF BOTH DIRECT
AND INDIRECT AIR CONTAMINATION SOURCES- SHALL BE SUBJECT TO DUAL
CONTROLS AND PERMIT REQUIREMENTS UNDER THIS REGULATION.
B. APPLICATION AND EFFECTIVE DATE -
THIS ARTICLE II SHALL APPLY STATEWIDE AND SHALL BECOME EFFECTIVE
THIRTY (30) DAYS AFTER ADOPTION.
C. DEFINITIONS AND EXCEPTIONS -
1. THE TERM "DIRECT AIR CONTAMINATION SOURCE" SHALL INCLUDE THE
FOLLOWING:
Classes of machines, equipment, articles, FACILITIES,
STRUCTURES and contrivances.
a. Basic equipment -
This class includes any machine, equipment, article
or other contrivance associated with operations
except as exempted in Paragraph C.2, the use of
which may cause the emission of air contaminants.
b. Air pollution control equipment -
This class includes any machine, equipment, article
or other contrivance associated with operations or
processes except as exempted in Paragraph C.2, the
use of which may eliminate or reduce or control the
emission of air contaminants.
E-139
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2. THE FOLLOWING DIRECT AIR CONTAMINATION SOURCES ARE EXEMPT
FROM THE REQUIREMENTS OF THIS ARTICLE II:
a. Structures used solely as residential dwellings
and which do not exceed seven family units;
b. EXISTING, AS OF EFFECTIVE DATE OF THIS REGULATION,
retail and wholesale establishments where no
processing or incineration occurs and where solid
or liquid fuel is not burned;
c. Air conditioning or ventilating systems not
designed to remove air contaminants generated
by or released from equipment;
d. Fuel-burning equipment, other than smokehouse
generators, which use gas as a fuel having a
BTU input of not more than 500,000 BTU per hour;
e. Fireplaces used for inside or outside recreational
purposes;
f. Fires used for non-commercial cooking of food for
human beings;
g. The installation or alteration of an air contaminant
detector, or air contaminant recorder;
h. Laboratory equipment used exclusively for chemical
or physical analyses;
i. Flares used to indicate some danger to the public;
j. Normal agricultural cultivation operations;
k. Internal combustion engines are exempt except that
emission notices and permit to operate are required
for engines of greater than 1,000 horsepoweri
1. Natural gas-fired indirect heat exchangers used as
separators and known as heater treaters when used
in oil and gas field operations when sweet gas is
burned.
3. THE FOLLOWING ADMINISTRATIVE PROCEDURES AND STATEMENTS CONSTITUTE
THE MECHANICS OF THE PERMIT SYSTEM UNDER THIS ARTICLE:
a. PREPLANNING REVIEW
b. AUTHORITY TO CONSTRUCT
C. IMPACT STATEMENT
E-140
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4. THE PHRASE "TO COMMENCE CONSTRUCTION" MEANS TO ENGAGE IN A
CONTINUOUS PROGRAM OF CONSTRUCTION INCLUDING SITE CLEARANCE,
GRADING, DREDGING, OR LAND FILLING SPECIFICALLY DESIGNED FOR
A DIRECT SOURCE IN PREPARATION FOR THE FABRICATION, ERECTION,
OR INSTALLATION OF THE BUILDING COMPONENTS OF THE DIRECT
SOURCE. INTERRUPTIONS RESULTING FROM ACTS OF GOD, STRIKES,
LITIGATION, OR OTHER MATTERS BEYOND THE CONTROL OF THE OWNER
. SHALL BE DISREGARDED IN DETERMINING WHETHER A CONSTRUCTION OR
MODIFICATION PROGRAM IS CONTINUOUS.
5. THE PHRASE "TO COMMENCE MODIFICATIONS" MEANS TO ENGAGE IN A
CONTINUOUS PROGRAM OF MODIFICATION, INCLUDING SITE CLEARANCE,
GRADING, DREDGING, OR LAND FILLING IN PREPARATION FOR A
SPECIFIC MODIFICATION OF THE DIRECT SOURCE.
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D. PREPLANNING REVIEW -
1. GENERAL REQUIREMENT:
a. PRIOR TO SUBMITTING AN APPLICATION FOR AUTHORITY TO
CONSTRUCT, THE APPLICANT SHALL MAKE A REQUEST TO THE
DIVISION FOR A PREPLANNING REVIEW.
b. THIS PREPLANNING REVIEW, AT THE DISCRETION OF THE
' DIVISION, MAY BE A TELEPHONE DISCUSSION, A MEETING,
A SITE INSPECTION, OR COMBINATION THEREOF, FOR THE
PURPOSE OF EXCHANGING CONTROL REQUIREMENT INFORMATION,
AIR MONITORING AND AIR POLLUTION PREDICTIVE MODELING
REQUIREMENTS, AND DISCUSSING OTHER REQUIREMENTS AS
OUTLINED IN PARAGRAPH E (AUTHORITY TO CONSTRUCT) AND
PARAGRAPH F (IMPACT STATEMENT). SUCH REVIEW IS
ADVISABLE PRIOR TO LARGE SCALE PLANNING AND DESIGN
EXPENDITURES ON BEHALF OF THE APPLICANT TO DISCUSS
WITH THE DIVISION IN CONCEPTUAL TERMS THE NATURE AND
SCOPE OF THE PROPOSED PROJECT AS RELATING TO AIR
POLLUTION CONTROL REQUIREMENTS. THE DIVISION SHALL
ADVISE THE APPLICANT IN WRITING THAT ITS CONCLUSIONS
ARE ADVISORY IN NATURE TO THE APPLICANT FOR ASSISTING
IN THE REVIEW OF DETAILED FORMAL APPLICATION FOR AUTHORITY
TO CONSTRUCT.
C. AT THE PREPLANNING CONFERENCE, THE APPLICANT SHALL
DISCUSS WITH THE DIVISION THE AVAILABILITY AND NEED FOR
DATA ON PRESENT AIR QUALITY, TOPOGRAPHY, METEOROLOGY AND
EMISSIONS FROM OTHER SOURCES IN THE AFFECTED AREA. SUCH
DATA WHICH THE DIVISION HAS OBTAINED FROM EMISSION
INVENTORIES, PREVIOUS SAMPLING PROGRAMS OR OTHER MEANS
E-142
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SHALL BE MADE AVAILABLE TO THE APPLICANT IN CONJUNCTION
WITH THE PREPLANNING REVIEW AS AN AID TO THE APPLICANT
IN PREPARING THE IMPACT STATEMENT.
d. THE DIVISION MAY REQUIRE AMBIENT AIR MONITORING FOR A
PERIOD OF NOT MORE THAN TWELVE (12) MONTHS BY APPLICANT
PRIOR TO FILING OF APPLICATION FOR AUTHORITY TO CONSTRUCT
BUT SHALL SPECIFY THE MINIMUM PERIOD AND TIME OF YEAR FOR
AIR MONITORING SUFFICIENT TO ESTIMATE BACKGROUND LEVELS
OF MAJOR AIR POLLUTANTS.
E. AUTHORITY TO CONSTRUCT -
1. GENERAL. REQUIREMENT:
a. ,NO PERSON SHALL CONSTRUCT OR MODIFY A DIRECT AIR CON-
TAMINANT EMISSION SOURCE WITHOUT FILING AN APPLICATION
FOR AUTHORITY TO CONSTRUCT AND RECEIVING WRITTEN
AUTHORIZATION FROM THE DIVISION EXCEPT AS EXEMPTED
PER PARAGRAPH C.2.
b. TOGETHER WITH THE APPLICATION, THE APPLICANT SHALL
SUBMIT A DETAILED STATEMENT OF AIR POLLUTION IMPACT
(IMPACT STATEMENT) OF THE PROPOSED ACTION AS DESCRIBED
IN PARAGRAPH F.
C. APPLICATIONS SHALL BE SIGNED BY THE INDIVIDUAL LEGALLY
RESPONSIBLE AND AUTHORIZED TO DO SO, AND HE THEREBY
COVENANTS THAT THE APPLICANT WILL EITHER CONSTRUCT OR
MODIFY THE AIR CONTAMINATION SOURCE IN ACCORDANCE WITH
THE REQUIREMENTS FOR GRANTIN3 APPLICATIONS AS OUTLINED
IN THIS REGULATION.
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2. STANDARDS FOR GRANTING OR DENYING APPLICATIONS:
a. NO AUTHORITY TO CONSTRUCT SHALL BE GRANTED TO THE
APPLICANT UNLESS THE DIVISION DETERMINES TO ITS
SATISFACTION THAT:
a-1. THE NEW DIRECT AIR CONTAMINATION EMISSION
SOURCE IS DESIGNED, BUILT, AND EQUIPPED IN
ACCORDANCE WITH THE BEST AVAILABLE TECHNOLOGY
AND OTHER ALTERNATIVES TO REDUCE, PREVENT, AND
CONTROL AIR POLLUTION.
a-2, THE NEW DIRECT AIR CONTAMINATION EMISSION SOURCE
IS SO DESIGNED AND WILL BE CONSTRUCTED OR MODIFIED
*
TO OPERATE WITHOUT CAUSING A VIOLATION OF THE
EMISSION CONTROL REGULATIONS OF THE COMMISSION,
AND ANY APPLICABLE NATIONAL OR LOCAL AIR POLLUTION
EMISSION CONTROL ORDINANCES AND REGULATIONS.
a-3. THE AIR CONTAMINATION EMISSION SOURCE, AS DESIGNED
OR MODIFIED, DOES NOT SIGNIFICANTLY ENDANGER MAINT-
TENANCE OR ATTAINMENT OF ANY AMBIENT AIR QUALITY
STANDARDS OF THE COMMISSION, AND ANY MORE STRINGENT
NATIONAL OR LOCAL AMBIENT AIR QUALITY STANDARDS.
a-4. THE APPLICATION SHALL CONTAIN ACCEPTABLE HALT OR
CURTAILMENT PROCEDURES WHICH CONFORM WITH THE
REQUIREMENTS OF SECTION 66-31-11 OF THE ACT. SUCH
PROCEDURES SHALL STATE THE TIMES IN WHICH THE
APPLICANT SHALL HALT OR CURTAIL ACTIVITIES UPON
BEING NOTIFIED OF THE DECLARATION OF AN AIR
POLLUTION EMERGENCY.
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a-5. IF THE CONDITIONS OF a-2 AND a-3 OF THIS SUBSECTION
CANNOT BE MET, YET THE APPLICANT UTILIZES THE BEST
AVAILABLE TECHNOLOGY AND OTHER ALTERNATIVES, WHICH
WOULD SIGNIFICANTLY REDUCE OR MINIMIZE POLLUTION,
THE DIVISION SHALL CONSULT WITH THE COMMISSION AND
THEREAFTER THE DIVISION, WITH THE CONCURRENCE OF
THE COMMISSION OR THE COMMISSION ALONE, MAY GRANT
THE PERMIT.
b. CONDITIONAL APPROVAL OF APPLICATIONS;
b-1. AN AUTHORITY TO CONSTRUCT OR MODIFY MAY BE ISSUED
TO AN APPLICANT OWNING OR OPERATING ANY AIR CON-
TAMINANT EMISSION SOURCE SUBJECT TO CONDITIONS
WHICH WILL MAKE THE EQUIPMENT OR FACILITY OPERATE
WITHIN THE EMISSION CONTROL REGULATIONS AND AMBIENT
AIR QUALITY STANDARDS OF THE COMMISSION OR APPLICABLE
NATIONAL OR LOCAL AIR POLLUTION CONTROL ORDINANCES AND
REGULATIONS, AND AMBIENT AIR QUALITY STANDARDS, IN
WHICH CASE THE CONDITIONS WILL BE SPECIFIED IN WRITING.
COMMENCING WORK UNDER SUCH AN AUTHORITY TO CONSTRUCT
SHALL BE DEEMED ACCEPTANCE BY THE APPLICANT OF ALL
CONDITIONS SPECIFIED'.
b-2. THE DIVISION MAY IMPOSE CONDITIONS UPON THE APPLICANT
IN THE AUTHORITY TO CONSTRUCT OR MODIFY WHICH REQUIRE
OWNERS OR OPERATORS OF AIR CONTAMINATION EMISSION
SOURCES TO INSTALL, MAINTAIN, AND USE INSTRUMENTATION
TO MONITOR AND RECORD EMISSION AND AMBIENT AIR DATA
' AS A BASIS FOR PERIODIC REPORTS TO THE DIVISION.
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C. DENIAL OF AN APPLICATION:
C-l. IN THE EVENT OF A DENIAL OF AN APPLICATION THE
DIVISION SHALL NOT ACCEPT A FURTHER APPLICATION
UNLESS THE APPLICANT HAS COMPLIED WITH THE
OBJECTIONS SPECIFIED AS REASONS FOR DENIAL.
C-2 PRIOR TO THE APPLICANT BEING NOTIFIED, IN WRITING,
OF DENIAL, A CONFERENCE BETWEEN THE DIVISION AND
THE APPLICANT MAY BE HELD TO DISCUSS THE REASONS
-FOR DENIAL.
3. REQUIREMENTS FOR REVIEWING APPLICATIONS:
a. THE DIVISION SHALL PREPARE ITS PRELIMINARY ANALYSIS OF
THE EFFECT UPON THE AMBIENT AIR QUALITY AND THE EXTENT
OF EMISSION CONTROL WITHIN TWENTY (20) DAYS AFTER DATE
ON WHICH AN APPLICATION IS FILED (66-31-12(4)(c).
b. FOR THOSE TYPES OF PROJECTS OR ACTIVITIES DEFINED OR
DESIGNATED BY THE COMMISSION AS WARRANTING PUBLIC COMMENT
WITH RESPECT THERETO, AS STATED IN PARAGRAPH b-1
OF THIS SUBSECTION (b), THE DIVISION SHALL, WITHIN FIFTEEN
(15) DAYS AFTER IT HAS PREPARED ITS PRELIMINARY ANALYSIS,
GIVE PUBLIC NOTICE OF THE PROPOSED PROJECT OR ACTIVITY BY
AT LEAST ONE PUBLICATION IN THE NEWSPAPER OF GENERAL CIRCU-
LATION IN THE COUNTY IN WHICH THE PROPOSED PROJECT OR
ACTIVITY, OR A PART THEREOF, IS TO BE LOCATED. IF NO
QUALIFIED NEWSPAPER IS PUBLISHED WITHIN SUCH COUNTY, THEN
THE PUBLICATION SHALL BE MADE IN A NEWSPAPER PUBLISHED IN
AN ADJOINING OR NEARBY COUNTY. THE DIVISION SHALL ALSO
WITHIN SUCH PERIOD OF TIME MAINTAIN IN THE OFFICE OF THE
COUNTY CLERK AND RECORDER OF THE COUNTY IN WHICH THE
PROPOSED PROJECT OR ACTIVITY, OR A PART THEREOF, IS LOCATED
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A COPY OF ITS PRELIMINARY ANALYSIS AND A COPY OF THE
APPLICATION WITH ALL ACCOMPANYING DATA FOR PUBLIC INSPECTION.
THE DIVISION SHALL RECEIVE AND CONSIDER PUBLIC COMMENT
THEREON FOR A PERIOD OF THIRTY (30) DAYS THEREAFTER.
(66-31-12(4)(d).
b-1. NEW AIR CONTAMINATION "SOURCES SUBJECT TO PUBLIC
COMMENT SHALL BE LIMITED TO THOSE WHOSE ANNUAL
EMISSION EXCEEDS TWENTY-FIVE (25) TONS OF ANY
ONE POLLUTANT FOR WHICH THE COMMISSION HAS
ADOPTED EMISSION REGULATIONS.
C. WITHIN THIRTY (30) DAYS FOLLOWING THE PERIOD FOR 5UBLIC
COMMENT, OR WITHIN FIFTEEN (15) DAYS AFTER THE PREPARATION
OF ITS PRELIMINARY ANALYSIS WHERE NO DELAY FOR PUBLIC COMMENT
IS REQUIRED, THE DIVE ION SHALL GRANT OR DENY THE PERMIT BASED
UPON THE STANDARDS SET FORTH IN PARAGRAPH E.2 OF THIS REGULA-
TION. ANY PERMIT ISSUED BY THE DIVISION MAY CONTAIN SUCH TERMS
AND CONDITIONS AS IT DEEMS NECESSARY FOR THE PROPOSED PROJECT
OR ACTIVITY TO QUALIFY FOR A PERMIT. IF ANY OF SUCH TERMS OR
CONDITIONS OF THE PERMIT ARE VIOLATED, THE DIVISION MAY REVOKE
THE PERMIT. IF THE DIVISION FAILS TO ACT UPON THE APPLICATION
WITHIN THE PRESCRIBED TIME THE PERMIT SHALL BE DEEMED TO HAVE
BEEN GRANTED. (66-31-12(4)(e).
d. IF THE DIVISION DENIES OR REVOKES A PERMIT, THE APPLICANT MAY
REQUEST A CONFERENCE WITH THE COMMISSION OR A HEARING BEFORE
THE COMMISSION IN ACCORDANCE WITH THE PROVISIONS OF SECTION
66-31-16. THIS APPEAL SHALL BE ADMINISTERED AS STATED BY THE
COMMISSION'S POLICY STATEMENT IN APPENDIX TO THESE REGULATIONS.
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e. WITHIN THIRTY (30) DAYS AFTER SUCH CONFERENCE OR HEARING, THE
COMMISSION OR VARIANCE BOARD SHALL ISSUE AN ORDER EITHER
AFFIRMING OR REVERSING THE DECISION OF THE DIVISION. IF THE
DECISION OR REVOCATION OF THE DIVISION IS REVERSED, THE
COMMISSION OR VARIANCE BOARD SHALL ORDER THE ISSUANCE OR
REINSTATEMENT OF THE PERMIT WHICH ORDER MAY CONTAIN SUCH
TERMS AND CONDITIONS AS SHALL BE NECESSARY AND REASONABLE.
IF A CONFERENCE IS REQUESTED IN LIEU OF A HEARING, THE
APPLICANT MAY REQUEST A HEARING THEREAFTER IF THE APPLICANT
IS NOT SATISFIED WITH THE RESULTS OF SUCH CONFERENCE.
(66-31-12(4)(h).
4. EXPIRATION OF AUTHORITY TO CONSTRUCT;
THE DIVISION MAY CANCEL AN AUTHORITY TO CONSTRUCT OR MODIFY IF
THE CONSTRUCTION OR MODIFICATION IS NOT BEGUN WITHIN SIX (6)
MONTHS FROM THE DATE CONSTRUCTION IS TO BE STARTED AS STATED
IN THE APPLICATION OR IF THE WORK INVOLVED IN THE CONSTRUCTION
OR MODIFICATION IS SUSPENDED FOR SIX (6) MONTHS OR MORE. AN
APPLICANT MAY SECURE AN EXTENSION OF THE EXPIRATION DATE BY
WRITTEN REQUEST TO THE DIVISION STATING THE REASONS FOR THE
REQUEST. EXTENSIONS MAY BE GRANTED FOR A PERIOD OF NOT MORE
THAN SIX (6) MONTHS.
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5. COMMENCEMENT V OPERATION:
"No perse:) shall commence the operation of any project or the
condv^1'. of any activity for which a permit has been issued
wlihout giving at least thirty days prior notice to the
division of the date on which such commencement is to take
place. During such thirty-day period and again within
thirty days after commencement, the division shall inspect
the project or activity to determine whether or not the
terms and conditions of the permit have been properly
satisfied. If the division finds that the terms or con-
ditions of the permit have been violated it may revoke the
permit, or it may grant a period of not more than six months
in which the terms or conditions may be satisfied. If the
division determines that the terms and conditions of the
permit have not been satisfied within such period of time,
the division shall revoke the permit, if the division
determines that the terms and conditions of the permit have
been satisfied, the division shall grant its final approval
of the permit whereupon all requirements of this subsection
. (4) shall have been fulfilled by the applicant."
(Section 66-31-12(4)(i) of the State Act).
F. IMPACT STATEMENT -
1. FOR ALL DIRECT AIR POLLUTION SOURCES EXCEPT THOSE EXEMPT BY
PARAGRAPH C.2 AN IMPACT STATEMENT SHALL BE SUBMITTED TO THE
DIVISION WITH THE APPLICATION FOR AUTHORITY TO CONSTRUCT
WHICH INCLUDES AN AIR CONTAMINANT EMISSION NOTICE AS SHOWN
IN ARTICLE I OF THIS REGULATION NO. 3. ADDITIONALLY THE
FOLLOWING INFORMATION SHALL BE REQUIRED IF SPECIFIED BY
THE DIVISION AT THE TIME OF THE PREPLANNING REVIEW.
a. INFORMATION ON THE IMPACT OF THE NEW OR MODIFIED
SOURCE UPON AIR QUALITY IN POLITICAL SUBDIVISIONS
ADJACENT TO THAT IN WHICH THE SOURCE IS TO BE
LOCATED AS SPECIFIED BY THE DIVISION AT THE
PREPLANNING REVIEW.
b. DATA ON PRESENT AIR QUALITY, TOPOGRAPHY, METEOROLOGY
AND EMISSIONS FROM OTHER SOURCES IN THE AFFECTED AREA
AS SPECIFIED BY THE DIVISION AT THE PREPLANNING REVIEW.
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C. THE APPLICANT SHALL USE MODELING TECHNIQUES FOR
APPROXIMATING THE EFFECTS OF THE ACTIVITY UPON AIR
QUALITY IF SPECIFIED BY THE DIVISION AT THE
PREPLANNING REVIEW. FOR THE PURPOSES OF UNIFORMITY
THE DIVISION SHALL SPECIFY MODELING TECHNIQUES AND
PROCEDURES TO BE USED.
d. TWO COPIES OF THE COMPLETE DATA, SITING (LOCATION)
INFORMATION, PLANS, DESCRIPTIONS, SPECIFICATIONS AND
DRAWINGS SUFFICIENT IN SCOPE TO ALLOW AN ENGINEERING
EVALUATION TO BE MADE TO DETERMINE WHETHER APPROPRIATE
AIR POLLUTION CONTROL REGULATIONS, AND ORDINANCES AND
' AMBIENT AIR QUALITY CONTROL STANDARDS WILL BE MET.
FOR CERTAIN CLASSES OF EQUIPMENT, SPECIAL INSTRUCTION
FORMS ARE AVAILABLE WHICH DETAIL THE INFORMATION
REQUIRED. THESE FORMS CAN BE IDENTIFIED AS THE FORM 200A
SERIES.
e. SUCH PERFORMANCE TESTS RESULTS, INFORMATION AND RECORDS
AS MAY BE REQUIRED BY THE DIVISION TO DETERMINE WHETHER
THE REQUIREMENTS OF THIS REGULATION ARE MET. SUCH
INFORMATION MAY ALSO BE REQUIRED BY THE DIVISION AT ANY
TIME WHEN THE SOURCE IS BEING OPERATED TO DETERMINE
COMPLIANCE WITH APPLICABLE EMISSION CONTROL REGULATIONS
AND AMBIENT AIR QUALITY STANDARDS.
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PROPOSED REVISIONS TO REGULATION NO. 3
III. INDIRECT AIR CONTAMINATION SOURCES
A. GENERAL.
SUBJECT TO THE FOLLOWING PROVISIONS, THIS REGULATION NO. 3 SHALL APPLY
TO INDIRECT AIR CONTAMINATION SOURCES. SOURCES WHICH MEET THE DEFINITION
OF BOTH DIRECT AND INDIRECT AIR CONTAMINATION SOURCES SHALL BE SUBJECT
TO DUAL CONTROLS AND PERMIT REQUIREMENTS UNDER THIS REGULATION.
B. APPLICATION AND EFFECTIVE DATE
THIS ARTICLE III SHALL APPLY STATEWIDE WITH THE EXCEPTION OF THE'
COUNTIES OF ADAMS, ARAPAHOE, BOULDER, CLEAR CREEK, DENVER, DOUGLAS,
GILPIN AND JEFFERSON, WHICH COUNTIES ARE THE SUBJECT OF A SEPARATE
ARTICLE UNDER THIS REGULATION NO. 3. THE PROVISIONS OF THIS ARTICLE
III SHALL BE EFFECTIVE JANUARY 1, 1975.
C. DEFINITIONS AND EXCEPTIONS
1. THE TERM "INDIRECT AIR CONTAMINATION SOURCE" SHALL INCLUDE
REGARDLESS OF SIZE OR NUMBER OF UNITS, COMMERCIAL FACILITIES,
PUBLIC AND PRIVATE OFFICE BUILDIN3S, SPORTS COMPLEXES, AIRPORTS,
RESTAURANTS, MEDICAL CARE FACILITIES, APARTMENT OR CONDOMINIUM
COMPLEXES, SUBDIVISIONS OF SINGLE OR MULTIPLE-FAMILY DWELLING
UNITS, PARKING LOTS, ROADWAYS, OR OTHER STRUCTURES WHOSE
PATRONAGE RELIES WHOLLY OR IN PART, ON THE USE OF MOTOR VEHICLES.
2. THE FOLLOWING INDIRECT AIR CONTAMINATION SOURCES ARE EXEMPT
FROM THE REQUIREMENTS OF THIS ARTICLE III IF THEIR SOLE SOURCE
OF AIR CONTAMINANTS IS A RESULT OF MOTOR VEHICLE TRAFFIC
GENERATED BY THE SOURCE.
a. NEW PARKING FACILITIES TO ACCOMMODATE 1,000 AUTOMOBILES
OR LESS AT ANY ONE TIME OR EXISTING FACILITIES TO BE
MODIFIED TO INCREASE PARKING CAPACITY BY 500 AUTOMOBILES
OR LESS.
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d. Parking facilities used exclusively for public or private
mass transportation.
C. NEW MOTOR VEHICLE ROADWAYS WITH AN ANTICIPATED ANNUAL
AVERAGE DAILY TRAFFIC VOLUME OF 20,000 OR LESS VEHICLES
PER DAY WITHIN 10 YEARS OF CONSTRUCTION OR A SIMILAR ESTIMATED
INCREASE OF 10,000 ADDITIONAL VEHICLES PER DAY IN THE CASE
OF A ROADWAY MODIFICATION.
d. LOCATION OR RELOCATION OF ANY MAJOR DEVELOPMENT, PRIVATE
OR PUBLIC ENTERPRISE EMPLOYING LESS THAN 500 PERSONS AT
ANY ONE TIME.
6. RESIDENTIAL DEVELOPMENTS OF LESS THAN 250 SINGLE-FAMILY
DWELLING UNITS.
f. AIRPORTS, OR ENLARGEMENTS TO ANY AIRPORT, WHOSE TOTAL
OPERATION AMOUNTS TO LESS THAN 50,000 TAKEOFFS AND
LANDINGS PER YEAR OR USED BY 1,600,000 OR LESS PASSENGERS
PER YEAR.
3. WHERE AN INDIRECT SOURCE IS CONSTRUCTED OR MODIFIED IN INCREMENTS
WHICH INDIVIDUALLY ARE NOT SUBJECT TO REVIEW UNDER THIS ARTICLE,
ALL SUCH INCREMENTS OCCURRING SINCE THE EFFECTIVE DATE OF THIS
REGULATION, OR SINCE THE LATEST APPROVAL HEREUNDER, WHICHEVER
DATE IS MOST RECENT, SHALL BE ADDED TOGETHER FOR DETERMINING THE
APPLICABILITY OF THIS ARTICLE.
4. THE PHRASE "TO COMMENCE CONSTRUCTION" MEANS TO ENGAGE IN A
CONTINUOUS PROGRAM OF CONSTRUCTION INCLUDING SITE CLEARANCE,
GRADING, DREDGING, OR LAND FILLING SPECIFICALLY DESIGNED FOR
AN INDIRECT SOURCE IN PREPARATION FOR THE FABRICATION, ERECTION,
OR INSTALLATION OF THE BUILDING COMPONENTS OF THE INDIRECT
SOURCE. INTERRUPTIONS RESULTING F.ROM ACTS OF GOD, STRIKES,
LITIGATION, OR OTHER MATTERS BEYOND THE CONTROL OF THE OWNER
SHALL BE DISREGARDED IN DETERMINING WHETHER A CONSTRUCTION OR
MODIFICATION PROGRAM IS CONTINUOUS.
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5. THE PHRASE "TO COMMENCE MODIFICATION" MEANS TO ENGAGE IN A
CONTINUOUS PROGRAM OF MODIFICATION, INCLUDING SITE CLEARANCE,
GRADING, DREDGING, OR LAND FILLING IN PREPARATION FOR A
SPECIFIC MODIFICATION OF THE INDIRECT SOURCE.
6. THE FOLLOWING ADMINISTRATIVE PROCEDURES AND STATEMENTS
CONSTITUTE THE MECHANICS OF THE PERMIT SYSTEM UNDER THIS
ARTICLE:
a. PREPLANNING REVIEW
b. AUTHORITY TO CONSTRUCT
C. IMPACT STATEMENT
D. PREPLANNING REVIEW
1. PRIOR TO SUBMITTING AN APPLICATION FOR AUTHORITY TO CONSTRUCT,
THE APPLICANT SHALL MAKE A REQUEST TO THE DIVISION FOR A
PREPLANNING REVIEW.
2. THIS PREPLANNING REVIEW, AT THE DISCRETION OF THE DIVISION,
MAY BE A TELEPHONE DISCUSSION, A MEETING, A SITE INSPECTION,
OR COMBINATION THEREOF, FOR THE PURPOSE OF EXCHANGING CONTROL
REQUIREMENT INFORMATION, AIR MONITORING AND AIR POLLUTION
PREDICTIVE MODELING REQUIREMENTS, AND DISCUSSING OTHER
REQUIREMENTS AS OUTLINED IN PARAGRAPH E (AUTHORITY TO CONTRUCT).
SUCH REVIEW IS ADVISABLE PRIOR TO LARGE SCALE PLANNING AND
DESIGN EXPENDITURES ON BEHALF OF THE APPLICANT TO DISCUSS WITH
THE DIVISION IN CONCEPTUAL TERMS THE NATURE AND SCOPE OF THE
PROPOSED PROJECT AS RELATING TO AIR POLLUTION CONTROL REQUIREMENTS.
THE DIVISION SHALL ADVISE THE APPLICANT IN WRITING THAT ITS
CONCLUSIONS ARE ADVISORY IN NATURE TO THE APPLICANT FOR
ASSISTING LATER REVIEW OF THE FORMAL APPLICATION FOR AUTHORITY
TO CONSTRUCT.
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3. BEFORE A FORMAL APPLICATION FOR A PERMIT TO CONSTRUCT WILL BE
ISSUED, DATA ON PRESENT AIR QUALITY, TOPOGRAPHY, METEOROLOGY
AND EMISSIONS FROM OTHER SOURCES IN THE AFFECTED AREA MUST BE
SUBMITTED TO THE DIVISION IN AN IMPACT STATEMENT PER PARAGRAPH
F. ANY DATA ON PRESENT AIR QUALITY, METEOROLOGY AND EMISSIONS
FROM THE OTHER SOURCES IN THE AREA WHICH THE DIVISION HAS
OBTAINED FROM EMISSION INVENTORIES, PREVIOUS SAMPLING PROGRAMS
OR OTHER MEANS SHALL BE MADE AVAILABLE TO THE APPLICANT IN
CONJUNCTION WITH THE PREPLANNING REVIEW AS AN AID IN PREPARING
THE IMPACT STATEMENT.
4. THE DIVISION MAY REQUIRE AMBIENT AIR MONITORING FOR A PERIOD OF
UP TO TWELVE (12) MONTHS BY APPLICANT PRIOR TO FILING OF
APPLICATION FOR AUTHORITY TO CONSTRUCT, BUT SHALL SPECIFY THE
MINIMUM PERIOD AND TIME OF YEAR FOR AIR MONITORING SUFFICIENT
TO ESTIMATE BACKGROUND LEVELS OF MAJOR AIR CONTAMINANTS.
E. AUTHORITY TO CONSTRUCT
1. GENERAL REQUIREMENT
a. NO PERSON SHALL CONSTRUCT OR MODIFY ANY INDIRECT AIR
CONTAMINANT EMISSION SOURCE WITHOUT FILING AN APPLICATION
FOR AUTHORITY TO CONSTRUCT AND RECEIVING WRITTEN AUTHORI-
ZATION FROM THE DIVISION EXCEPT AS EXEMPTED PER PARAGRAPH C.2.
b. TOGETHER WITH THE APPLICATION, THE APPLICANT SHALL SUBMIT A
DETAILED STATEMENT OF AIR POLLUTION IMPACT (IMPACT STATEMENT)
OF THE PROPOSED ACTION AS DESCRIBED IN PARAGRAPH F.
C. APPLICATIONS SHALL BE SIGNED BY THE INDIVIDUAL LEGALLY
RESPONSIBLE AND AUTHORIZED TO DO SO, AND HE THEREBY COVENANTS
THAT THE APPLICANT WILL EITHER CONSTRUCT OR MODIFY THE AIR
'CONTAMINATION SOURCE IN ACCORDANCE WITH THE REQUIREMENTS FOR
* •
GRANTING APPLICANTS AS OUTLINED IN THIS.REGULATION.
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2. STANDARDS FOR GRANTING OR DENYING APPLICATIONS
a. NO AUTHORITY TO CONSTRUCT SHALL BE GRANTED TO THE APPLICANT
UNLESS THE DIVISION DETERMINES TO ITS SATISFACTION THAT:
(i) THE NEW INDIRECT AIR CONTAMINATION SOURCE IS
DESIGNED, BUILT, AND EQUIPPED IN ACCORDANCE
WITH THE BEST AVAILABLE TECHNOLOGY AND OTHER
ALTERNATIVES TO REDUCE, PREVENT, AND CONTROL
AIR POLLUTION.
(ii) THE INDIRECT AIR CONTAMINATION SOURCE, AS DESIGNED
OR MODIFIED, DOES NOT SIGNIFICANTLY ENDANGER
MAINTENANCE OR ATTAINMENT OF ANY AMBIENT AIR
QUALITY STANDARDS OF THE COMMISSION, AND ANY
MORE STRINGENT NATIONAL OR LOCAL AMBIENT AIR
QUALITY STANDARDS.
(iii) IF THE CONDITIONS OF (i) and (ii) OF THIS SECTION
CANNOT BE MET, YET THE APPLICANT UTILIZES THE BEST
AVAILABLE TECHNOLOGY AND OTHER ALTERNATIVES, WHICH
WOULD SIGNIFICANTLY REDUCE OR MINIMIZE POLLUTION,
THE DIVISION SHALL CONSULT WITH THE COMMISSION AND
THEREAFTER THE DIVISION, WITH THE CONCURRENCE OF THE
COMMISSION OR THE COMMISSION ALONE, MAY GRANT THE PERMIT.
(iv) APPROVAL OF A PERMIT APPLICATION SHALL NOT EXEMPT
APPLICANT FROM THE RESPONSIBILITY TO COMPLY WITH
APPLICABLE PORTIONS OF THE CONTROL STRATEGY INCLUDED
IN COLORADO STATE IMPLEMENTATION PLANS.
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b. CONDITIONAL APPROVAL OF APPLICATIONS
(i) AN AUTHORITY TO CONSTRUCT OR MODIFY MAY BE ISSUED
TO AN APPLICANT OWNING OR OPERATING ANY INDIRECT
AIR CONTAMINATION SOURCE SUBJECT TO CONDITIONS WHICH .
WILL MAKE THE SOURCE OPERATE WITHIN THE EMISSION
CONTROL REGULATIONS AND AMBIENT AIR QUALITY STANDARDS
OF THE COMMISSION OR APPLICABLE NATIONAL OR LOCAL
AIR POLLUTION CONTROL ORDINANCES AND REGULATIONS,
AND AMBIENT AIR QUALITY STANDARDS, IN WHICH CASE
THE CONDITIONS WILL BE SPECIFIED IN WRITING.
COMMENCING WORK UNDER SUCH AN AUTHORITY TO CONSTRUCT
SHALL BE DEEMED ACCEPTANCE BY THE APPLICANT OF ALL
CONDITIONS SPECIFIED.
(ii) THE DIVISION MAY IMPOSE CONDITIONS UPON THE APPLICANT
IN THE AUTHORITY TO CONSTRUCT OR MODIFY WHICH REQUIRE
OWNERS OR OPERATORS OF INDIRECT AIR CONTAMINATION
SOURCES TO INSTALL, MAINTAIN, AND USE INSTRUMENTATION
TO MONITOR AND RECORD EMISSION, AMBIENT AIR AND/OR
VEHICLE TRAFFIC DATA AS A BASIS FOR PERIODIC REPORTS
TO THE DIVISION.
C. DENIAL OF AN APPLICATION
(i) IN THE EVENT OF A DENIAL OF AN APPLICATION THE DIVISION
SHALL NOT ACCEPT A FURTHER APPLICATION UNLESS THE
APPLICANT HAS COMPLIED WITH THE OBJECTIONS SPECIFIED
AS REASONS FOR DENIAL.
PRIOR TO THE APPLICANT BEING NOTIFIED, IN WRITING, OF
DENIAL, A CONFERENCE BETWEEN THE DIVISION AND THE
APPLICANT MAY BE HELD TO DISCUSS THE REASONS FOR DENIAL.
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3. REQUIREMENTS FOR REVIEWING APPLICATIONS
a. THE DIVISION SHALL PREPARE ITS PRELIMINARY ANALYSIS -OF
THE EFFECT UPON THE AMBIENT AIR QUALITY AND THE EXTENT OF
EMISSION CONTROL WITHIN TWENTY (20) DAYS AFTER DATE ON
WHICH AN APPLICATION IS FILED. (66-31-12(4)(c).
b. FOR THOSE TYPES OF PROJECTS OR ACTIVITIES DEFINED OR
DESIGNATED BY THE COMMISSION AS WARRANTING PUBLIC COMMENT
WITH RESPECT THERETO, AS STATED IN PARAGRAPH b-1 OF
THIS SUBSECTION (b), THE DIVISION SHALL, WITHIN FIFTEEN (15)
DAYS AFTER IT HAS PREPARED ITS PRELIMINARY ANALYSIS, GIVE
PUBLIC NOTICE OF THE PROPOSED PROJECT OR ACTIVITY BY AT
LEAST ONE PUBLICATION IN THE NEWSPAPER OF GENERAL CIRCULATION
IN THE COUNTY IN WHICH THE PROPOSED PROJECT OR ACTIVITY, OR
A PART THEREOF, IS TO BE LOCATED. IF NO QUALIFIED NEWSPAPER
IS PUBLISHED WITHIN SUCH COUNTY, THEN THE PUBLICATION SHALL
V
BE MADE IN A NEWSPAPER PUBLISHED IN AN ADJOINING OR NEARBY
COUNTY. THE DIVISION SHALL ALSO WITHIN SUCH PERIOD OF TIME
MAINTAIN IN THE OFFICE OF THE COUNTY CLERK AND RECORDER OF
THE COUNTY IN WHICH THE PROPOSED PROJECT OR ACTIVITY, OR A
PART THEREOF, IS LOCATED A COPY OF ITS PRELIMINARY ANALYSIS
AND A COPY OF THE APPLICATION WITH ALL ACCOMPANYING DATA FOR
PUBLIC INSPECTION. THE DIVISION SHALL RECEIVE AND CONSIDER
PUBLIC COMMENT THEREON FOR A PERIOD OF THIRTY (30) DAYS
THEREAFTER. (66-31-12(4)(d).
INDIRECT AIR CONTAMINATION SOURCES SUBJECT TO PUBLIC
COMMENT SHALL INCLUDE THOSE COVERED BY THIS ARTICLE III.
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C. WITHIN THIRTY (30) DAYS FOLLOWING THE PERIOD FOR PUBLIC
COMMENT, OR WITHIN FIFTEEN (15) DAYS AFTER THE PREPARATION
OF ITS PRELIMINARY ANALYSIS WHERE NO DELAY FOR PUBLIC COMMENT
IS REQUIRED, THE DIVISION SHALL GRANT OR DENY THE PERMIT BASED
UPON THE STANDARDS SET FORTH IN PARAGRAPH E.2 OF THIS REGULATION.
ANY PERMIT ISSUED BY THE DIVISION MAY CONTAIN SUCH TERMS AND
CONDITIONS AS IT DEEMS NECESSARY FOR THE PROPOSED PROJECT OR
ACTIVITY TO QUALIFY FOR A PERMIT. IF ANY OF SUCH TERMS OR
CONDITIONS OF THE PERMIT ARE VIOLATED, THE DIVISION MAY REVOKE
THE PERMIT. IF THE DIVISION FAILS TO ACT UPON THE APPLICATION
WITHIN THE PRESCRIBED TIME, THE PERMIT SHALL BE DEEMED TO HAVE
BEEN GRANTED. (66-31-12(4)(e).
d. IF THE DIVISION DENIES OR REVOKES A PERMIT, THE APPLICANT MAY
REQUEST A CONFERENCE WITH THE DIVISION OR A HEARING BEFORE THE
COMMISSION IN ACCORDANCE WITH THE PROVISIONS OF SECTION 66-31-16.
THIS APPEAL SHALL BE ADMINISTERED AS STATED BY THE COMMISSION'S
POLICY STATEMENT V IN THE APPENDIX OF THESE REGULATIONS.
e. WITHIN THIRTY (30) DAYS AFTER SUCH CONFERENCE OR HEARING, THE
COMMISSION OR VARIANCE BOARD SHALL ISSUE AN ORDER EITHER
AFFIRMING OR REVERSING THE DECISION OF THE DIVISION. IF THE
DECISIONS OR REVOCATION OF THE DIVISION IS REVERSED, THE
COMMISSION OR VARIANCE BOARD SHALL ORDER THE ISSUANCE OR
REINSTATEMENT OF THE PERMIT WHICH ORDER MAY CONTAIN SUCH TERMS
AND CONDITIONS AS SHALL BE NECESSARY AND REASONABLE. IF A
CONFERENCE IS REQUESTED IN LIEU OF A HEARING, THE APPLICANT
MAY REQUEST A HEARING THEREAFTER IF THE APPLICANT IS NOT
SATISFIED WITH THE RESULTS OF SUCH CONFERENCE. (66-31-12(4)(h).
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4. EXPIRATION OF AUTHORITY TO CONSTRUCT
THE DIVISION MAY CANCEL AN AUTHORITY TO CONSTRUCT OR MODIFY IF THE
CONSTRUCTION OR MODIFICATION IS NOT BEGUN WITHIN SIX (6) MONTHS
FROM THE DATE CONSTRUCTION IS TO BE STARTED AS STATED IN THE
APPLICATION OR IF THE WORK INVOLVED IN THE CONSTRUCTION OR
MODIFICATION IS SUSPENDED FOR SIX (6) MONTHS OR MORE. AN APPLICANT
MAY SECURE AN EXTENSION OF THE EXPIRATION DATE BY WRITTEN REQUEST
TO THE DIVISION STATING THE REASONS FOR THE REQUEST. EXTENSIONS
MAY BE GRANTED FOR A PERIOD OF NOT MORE THAN SIX (6) MONTHS.
5. COMMENCEMENT OF OPERATION
"No person shall commence the operation of any project or the
conduct of any activity for which a permit has been issued without
giving at least thirty days prior notice to the division of the
date on which such commencement is to take place. During such
thirty-day period and again within thirty days after commencement
the division shall inspect the project or activity to determine
whether or not the terms and conditions of the permit have been
properly satisfied. If the division finds that the terns or
conditions of the permit have been violated it may revoke the
permit, or it may grant a period of not more than six months in
which the terms or conditions may be satisfied. If the division
determines that the terms and conditions of the permit have not
been satisfied within such period of time, the division shall
revoke the permit. If the division determines that the terms and
conditions of the permit have been satisfied, the division shall
grant its final approval of the permit whereupon all requirements
of this subsection (4) shall have been fulfilled by the applicant.
(Section 66-31-12(4)(i) of State Act).
F. IMPACT STATEMENT
1. FOR ALL INDIRECT AIR POLLUTION SOURCES EXCEPT THOSE EXEMPT BY
PARAGRAPH C.2, AN IMPACT STATEMENT COVERING THE FOLLOWING SHALL
BE SUBMITTED WITH THE APPLICATION FOR AUTHORITY TO CONSTRUCT:
a. INFORMATION ON THE IMPACT OF THE NEW OR MODIFIED
SOURCE UPON AIR QUALITY IN POLITICAL SUBDIVISIONS
ADJACENT TO THAT IN WHICH THE SOURCE IS TO BE LOCATED.
E-159
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b. DATA ON PRESENT AIR QUALITY, TOPOGRAPHY, METEOROLOGY AND
EMISSIONS FROM OTHER SOURCES IN THE AFFECTED AREA.
C. INFORMATION ON THE SIZE OF THE SOURCE AND TIMES OF OPERATION
WHEN DEEMED ADVISABLE BY THE DIVISION, THE APPLICANT SHALL
USE MODELING TECHNIQUES FOR APPROXIMATING THE EFFECTS OF
THE ACTIVITY UPON AIR QUALITY. FOR PURPOSES OF UNIFORMITY
THE DIVISION SHALL SPECIFY MODELING TECHNIQUES AND PROCEDURES
TO BE USED.
2. IN ADDITION, THE FOLLOWING INFORMATION MUST BE INCLUDED IN THE
STATEMENT SUBMITTED:
a. ANTICIPATED NUMBER OF EMPLOYEES AND PATRONS, EXPECTED
TRANSPORTATION ROUTES, MODES, AND TRANSPORTATION HABITS
OF EMPLOYEES AND PATRONS, AND NUMBER OF HOUSING UNITS
AND ESTIMATED NUMBER OF RESIDENTS.
b. ESTIMATION OF THE EFFECT OF THE PROPOSED ACTIVITY UPON
CHANGES IN THE VEHICLE MILES TRAVELED (V.M.T.) PATTERN IN
THE GENERAL AREA; THE EFFECT UPON GENERATING SECONDARY
BUSINESS, COMMERCIAL AND RESIDENTIAL ACTIVITY IN THE GENERAL
AREA; AND CONSIDERATION TO THE SPATIAL DISTRIBUTION OF
MOTOR VEHICLE MOVEMENT; HEIGHT OF EMISSIONS AND ANY FACILITY
CONFIGURATION WHICH WOULD CONSTRAIN DISPERSION OF POLLUTANTS
(SUCH AS A PARKING DECK).
• C. EFFECTIVE JULY 1, 1975, UNLESS EXEMPTED BY THE DIVISION ALL
INDIRECT SOURCES SHALL USE TRANSPORTATION MODELING TECHNIQUES
AS DEVELOPED BY THE DIVISION FOR APPROXIMATING THE EFFECTS
UPON AIR QUALITY OF FACILITIES WITH ASSOCIATED MOBILE SOURCE
ACTIVITY.
E-160
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d. APPLICANT SHALL DEMONSTRATE TO THE DIVISION THAT MOTOR VEHICLE
TRAFFIC HAS BEEN OR WILL BE MINIMIZED BY THE FOLLOWING, WHEN
APPLICABLE:
(i) MAXIMUM UTILIZATION OF PUBLIC AND PRIVATE MASS
TRANSPORTATION SYSTEMS AND PROVISIONS RELATING TO
REGULATIONS FOR EXPRESS BUS SERVICE AND EXCLUSIVE
BUS LANES.
(ii) CONSIDERATION OF ALTERNATE BUILDING SITES AND
ACTIVITY LOCATIONS (FOR EXAMPLE, CONSTRUCTING NEXT
TO PUBLIC TRANSPORTATION ROUTES AS OPPOSED TO
RELIANCE UPON MOTOR VEHICLE ROADWAYS).
(iii) USE OF TRAFFIC SIGNALIZATION AND CONTROL TECHNIQUES TO
REDUCE VEHICLE TRAFFIC OR TO IMPROVE VEHICLE FLOW.
(iv) LIMITING THE USE OF MOTOR VEHICLE PARKING SPACES AND
ADJUSTING PARKING FEES SO AS TO ENCOURAGE CAR POOLING
AND TO DISCOURAGE SINGLE OCCUPANCY COMMUTER VEHICLES.
(v) DEVELOPMENT AND USE OF A CAR POOLING SERVICE.
(vi) USE OF AUTOMOBILE-FREE ZONES.
-------
PROPOSED ADDITIONS
TO
REGULATION NO. 3
(Permit System)
IV. PORTABLE EMISSION SOURCES:
1. FOR PURPOSES OF THIS SECTION PORTABLE EMISSION
SOURCES MAY INCLUDE BUT SHALL NOT BE LIMITED TO
ASPHALT AND ROCK CRUSHING PLANTS, CONCRETE BATCH
PLANTS, QUARRY WAGON DRILLS AND ROOFING ASPHALT
KETTLES.
2. ALL EXISTING SOURCES INCLUDED IN PARAGRAPH 1 OF
THIS SECTION SHALL BE TREATED AS NEW SOURCE INSOFAR
AS ANY PERSON OWNING SAID SOURCES SHALL BY SEPTEMBER
1, 1974, OBTAIN A PERMIT FOR EXISTING EQUIPMENT FROM
THE DIVISION PURSUANT TO THIS SECTION. NEW SOURCES
SHALL ALSO APPLY IN ACCORDANCE WITH THE PROCEDURES
OF THIS SECTION.
a. THE PERMIT MAY BE GRANTED AND RENEWED FOR ANY
PERIOD OF TIME AS DEEMED APPROPRIATE BY THE
DIVISION.
E-162
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b. THE PERMIT MAY BE GRANTED TO ANY SINGLE
APPLICANT FOR ANY SINGLE PROJECT OR COMBI-
NATION OF PROJECTS AS DEEMED APPROPRIATE
BY THE DIVISION.
b-1. WITH RESPECT TO ROOFING ASPHALT
KETTLES AND QUARRY WAGON DRILLS,
A SINGLE PERMIT ISSUED PURSUANT TO
THIS SECTION IV. 2 MAY BE ISSUED FOR
MORE THAN ONE UNIT BELONGING TO A
SINGLE APPLICANT PROVIDING ALL UNITS
ADHERE TO THE PROVISIONS OF I.A.I OF
THIS REGULATION NO. 1.
C. SOURCE RELOCATIONS -
EXCEPT FOR QUARRY WAGON DRILLS AND ROOFING
ASPHALT KETTLES, ANY PERSON HAVING BEEN
GRANTED A PERMIT, SHALL NOTIFY THE DIVISION
THIRTY (30) DAYS IN ADVANCE OF EACH SOURCE
RELOCATION. SAID NOTIFICATION SHALL INCLUDE
THE FOLLOWING INFORMATION:
C-l LOCATION AND EXPECTED DURATION
AT RELOCATION SITE,
C-2 FUEL CHANGE IF ANY,
C-3 TYPE, MATERIAL SIZE RANGE AND MOISTURE
CONTENT OF MATERIAL TO BE PROCESSED AS
RELATED TO AIR POLLUTION POTENTIAL,
C-4 AFTER REVIEW OF THE NOTICE BY THE DIVISION
ADDITIONAL CONTROL MEASURES IF DEEMED
NECESSARY BY THE DIVISION.
E-163
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APPENDIX F
THE COLORADO PLAN FOR
FEDERAL SECONDARY AMBIENT AIR QUALITY STANDARDS
(PARTICIPATE MATTER AND SULFUR OXIDES)
Adopted February 28, 1974
F-l
-------
PARTICULATE MATTER
Plan Summary and Implementation Schedule;
The Colorado Air Pollution Control Commission adopted for public hearing
proposals of the "Colorado Fugitive Dust investigation" report as the Colorado
plan for the Federal secondary ambient air quality standard for particulate
matter. This report was prepared by PEDCo-ENVlRONMENTAL of Cincinnati, Ohio,
under contract to the Environmental Protection Agency. The Commission considers
the three regions studies in this report as typical of the problem statewide.
The Commission agreed with the consultant's recommendations on the practical
controls available and adopted all recommendations formally outlined in the
report as regulation on March , 1974. However the Commission remains
uncertain of the means by which fugitive dust emissions can be further reduced
from snow sanding by 25% as a result of quicker sand pickup by machine sweeping
after snow melt. To this end, the Commission has solicited information on the
sand pickup problem from the State Highway Department and local governments
within the Denver Metropolitan area and has dec-msd immediate controls '..indefinable
on the basis of the public hearing record and oilier information received at this
tiine. The Conraission recuests twelve (12) additional months to study this
matter in more depth and to submit a control regulation if the Environmental
Protection Agency and the Commission concludes control measures are available
and reasonable considering the public safety problem.
Following is an outline of the Commission's plan for the Federal Secondary
Standard for Particulate Matter;
November 27, 1973 -
Commission adopted for purposes of public hearing, Secondary Standards
Plan. Legal notice sent to 600 organization and news release.
January 7, 1974 -
Commission held public hearing on the proposed plan according to the
attached Notice of Hearing.
February 28, 1974 -
Commission adopted plan and submitted it, through the Governor, to the
Regional Administrator of E.P.A. for approval. As part of that plan,
the Commission adopted a fugitive dust control regulation pursuant to
public hearings on July 10, 18, 19, 1973 and January 7, 1974 and after
receipt of the PEDCo Report recommendations.
August 1, 1974;
Commission to submit additional control plans to E.P.A. regarding the
control of fugitive dust from snow-sanding if feasible control measures
are identified. The Commission will annually investigate additional
particulate matter control measures that may be workable. Additionally,
the Commission is amiable to suggestions from the Environmental Protection
Agency and any other organization or person as to additional practical
control measures, and recommends meetings with E.P.A. officials on such
suggestions so plan revisions can be made on mutually agreeable measures.
F-2
-------
W ^ (. -J « 5f i ^ .- 1
COLORADO DEPARTMENT OF HEALTH 4210 EAST 11TH AVENUE • DENVER, COLORADO 80220
NOTICE OF PUBLIC HEARING BEFORE
THE COLORADO AIR POLLUTION CONTROL COMMISSION
ON THE
PROPOSED PLAN TO MEET THE
FEDERAL SECONDARY STANDARDS FOR PARTICULATE MATTER Aid SULFUR OXIDES
Pursuant to the provisions of Colorado Revised Statutes 1963, Section 3-16-2, as
amended (1967-1969 Perm.Guru.Supps.) and Section 66-31-5 as amended (1971 Perm.Cum.Supps.}
of the "Air Pollution Control Act of 1970, and pursuant to 37 Code of Federal Regulations
(CFR) 10855 as amended in 40 CFR Part 52, NOTICE is hereby given that the Colorado Air
Pollution Control Commission will hold a public hearing on January 7, 1974 at 9:30 a.m.
in the Colorado Division of Highways Auditorium, 4201 East Arkansas, City and County of
Denver, Colorado, to consider and act upon the adoption of a proposed plan to meet the
Federal Secondary Standards for particulate matter and sulfur oxides in the Federal
designated Denver, San Isabel and Pawnee Air Quality Control Regions (consisting of
the Front Range and eastern portion of Colorado).
The entire plan is available for public inspection at the office of the Technical
Secretary, Colorado Department of Health. A summary of the proposed plan and rules and
regulations is attached and also available at the air quality control region offices of
the state as follows:
Fort Collins, Colorado
Larimer County Health Department
200 West Oak Street
Denver, Colorado
Colorado Department of Health
4210 East llth Avenue
La Junta, Colorado
Otero County Health Department
County Court House
Colorado Springs, Colorado
City-County Health Department
501 North Foote Street
Alamosa, Colorado
Alamosa County Clerk
County Court House
Durango, Colorado
San Juan Basin Health Unit
1905 East Third Avenue
F-3
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Notice of Hearing - January 7, 1974
Colorado Air Pollution Control Commission
page 2
Grand Junction, Colorado
Mesa County Health Department
515 Patterson Avenue
Steamboat Springs, Colorado
Routt County Clerk
Routt County Court House
Any interested person shall have an opportunity to participate at said public hearing
by submitting written data, views, or arguments or submitting them orally at said public
hearing or through legal counsel. It is expected that all speakers will summarize their
remarks where proper, and will provide lengthy supportive information in written form-for
review by the Commission.
Any person desiring to propose amendments to the proposed plan shall file such other
proposal with Mr. Lane Kirkpatrick, Technical Secretary to the Commission on or before
5 p.m., January 1, 1974 at the above letterhead address, when on file these proposals
shall be open for public inspection.
Witnesses at the hearing shall be subject to cross-examination by or on behalf of
the Commission, or by or on behalf of persons who have proposed amendments to the plan and
rules and regulations as herein provided.
At such time as no persons are present to offer testimony, the hearing shall be closed
and in no event later than 4 p.m.
COLOK/iDO AIR POLLUTION CONTROL COMMISSION
Dated December 4, 1973
Jan&s P. Lodg^> Cn: . , Ph.D., Chairman
;olorado Department of Health
4210 East llth Avenue
Denver, Colorado 80220
Distribution List in
Legal Counsel's Office
Colorado Department of Health
F-4
-------
COLORADO
.
[ ^^ _ » (!
. ,—J ^--^ U
Wslcllflr .utcit, ^4d
t u • ' t
SAN ISABEL
COUNTY SEATS
Location of Metro-Denver, Pawnee, and
San Isabel AQCR's.
F-5
-------
PEDCo REPORT SUMMARY
The entire PEDCo report is available for inspection at the office
of the Technical Secretary of the Commission, 4210 East llth Avenue,
Denver, Colorado. Telephone 303-388-6111, Extension 286. The
following highlights that report:
Introduction
Prior to submittal in January of 1972 of its initial implementation plan
for attainment of particulate nir quality standards, the State of Colorado
requested and E.P.A. granted an 18-month extension for development of a plan
to achieve the secondary standard of 60 micrograms per cubic meter (ug/m )
annual geometric mean. The particulate control regulations submitted in the
initial implementation plan showed that the primary standard would barely be
achieved in some areas.
in searching for particulate emission sources where additional emission
reductions could be demonstrated as part of the plan to achieve the secondary
standard, the Colorado Air Pollution Control Commission identified fugitive
dust from unpaved roads and other sources as contributors to particulate
pollution which were amenable to control. The agency next drafted regulations
designed to provide the best control feasible for the fugitive dust sources
that thoy had identified. However, due to lack of available data on (1)
emission rates from these sources and (2) tie effectiveness of the proposed
regulations in reducing particulate emissions, the Commission was unable to
quantitatively demonstrate that the fugitive dust controls would result in
the necessary reduction in emissions.
To compound this problem of presentation, measured particulate levels at
some sampling sites vrere increasing with time, rather than decreasing according
to the projections of the initial implementation plan. This divergence of
actual measurements from projections indicated that the emission inventory on
which the control strategy was based did not account for all emission sources
impacting on the samplers.
The present study was thus undertaken to quantify the reduction in
fugitive dust emissions that can be expected from enforcement of the proposed
regulations and to estimate the resulting air quality in three Colorado Air
Quality control Regions with these regulations in addition to existing control
regulations.
The procedure employed to accomplish these objectives was first to prepare
a detailed inventory of fugitive dust emissions by county for the three AQCR's;
Metro-Denver, Pawnee and San Isabel. Concurrently, the inventory of conven-
tional particulate emissions that was submitted in the implementation plan was
updated. Next, the approximate control efficiency of the proposed fugitive dust
regulations in reducing emissions from each source category was determined.
Using the combined particulate inventory and estimated emission reductions, the
expected air quality in the three AQCR's was then determined by the proportional
modeling, or "rollback" method on a county basis. Finally, conclusions were
drawn on the adequacy of the proposed and existing regulations and recommendations
were made on particulate source categories in need of further control.
The fugitive dust emission inventory methodology is described in this
report, and the updated and combined particulate inventory is presented. Also
discussed are procedures for estimating control efficiencies of the proposed
fugitive dust regulations. The rollback calculations are performed and
summarized and recommendations for futher emission reductions are made.
F-6
-------
Fugitive Dust Emission in the Three Air Quality Control Regions:
The list used in reporting fugitive dust emissions in this study was
based upon reevaluation of the fugitive dust source categories as the inventory
progressed. As a result of this review, three changes were made in the classi-
fications :
1. a category was added — dust from traffic on paved streets
after the streets have been sanded for snow control;
2. unpaved parking lots were deleted from the inventory when
preliminary data indicated that regional emissions would
be negligible; and
3. the construction category was divided into two separate
categories with different emission factors and data sources —
highway construction and residential, industrial, and
commercial construction. .
The revised listing at source categories, used in reporting fugitive
dust emissions in this study is:
- unpaved roads
sand on paved roads
agriculture
land development
residential, industrial, and commercial construction
highway construction
quarrying, mining, and tailings
aggregate storage
cattle feedlots
The summary of emission estimating parameters and emission factors appear
in Table 2.1 on the following page.
F-7
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F-15
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Predicted Particulate Air Quality by county;
The procedure used to estimate ambient air quality was the proportional
model, or "rollback," in the following form:
A2 - B E2
= ' where
AI - B Ex
A-j_ = Existing air quality at location in county having
highest measured concentration
A2 - projected air quality
B = background concentration
E, = existing particulate emissions in county
E~ = projected particulate emissions in county after
implementation of regulations
To determine the reduction needed to reach the air quality standard, the
appropriate value for the standard was substituted for A2.
The proportional modeling was performed separately for each county rather
than for entire AQCR's since this procedure; (1) provided some definition of
the distribution of particulate air quality throughout the relatively large
AQCR's and (2) permitted a better evaluation of the sources which need additional
control in the "hot spots."
Air quality data and summaries for 1972 for every hi-vol site in Colorado
were obtained from the National Aerometric Data Bank through Region VIII of the
Environmental Protection Agency. The data were analyzed to find the maximum
annual geometric mean arid maximum 24-hour reading recorded in each county. The
annual mean and maximum 24-hour reading did not necessarily come from the same
sampling station in the county.
These two values for each county are presented by AQCR in Tables 5.1, 5.2,
and 5.3. Using the proportional model and the annual geometric means, the
percent reductions in emissions in each county that are needed to meet the
primary and secondary air quality standards were calculated and are recorded
in the same tables. The annual mean has been used in the rollback calculations
in every case, even though a higher reduction was sometimes shown to be necessary
when the maximum single reading was used, for the following reasons:
F-16
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1. the validity of the single high readings is much more
questionable than long-term averages and thus they
provide a much weaker base for the development of
control strategies;
2. the 24-hour air quality standard could be interpreted
to be for the second highest reading during the year
—"maximum 24-hour concentration not to be exceeded
more than once per year";
3. most high values could be systematically disqualified
due to the presence of high winds, episode conditions,
nonrecurring emissions near the site, or other reasons;
and
4. the variation in maximum recorded values is much greater
from year to year, and therefore they are not a good
indicator of overall air quality at a site.
Readings at the sites in different topographic areas of the state with the
lowest annual geometric means were used to estimate the particulate background
concentrations for the proportional model. Values of 35 micrograms per cubic
meter on the plains, 15 micrograms per cubic meter in the mountains, and 30
micrograms per cubic meter in the sandhills at the northeastern corner of the
Stcite were selected.
The predicted particulate air qualities in all counties with existing air
quality data are shown in Tables 5.1 through 5.3. The emission totals utilised
in calculating ths ambient levels are also presented. The results indicate that
the primary standards will be exceeded by significant amounts in all three
AQCR's, even after implementation of the proposed fugitive dust regulations.
In general, the inadequate reductions in emissions can be attributed to
the low control efficiencies of fugitive dust control regulations and their
large share of total particulate emissions. For example, county-wide emission
reductions by county range from 19 to 45 percent in the Metropolitan Denver
AQCR and from only 2 to 15 percent in the Pawnee AQCR.
The presence of extremely high particulate levels currently in Denver County
makes achievement of air quality standards by 1975 a very remote possibility.
While the projected air quality levels in all parts of the three regions are
much higher when fugitive dust is considered, they appear to correspond much
better when fugitive dust is considered, they appear to correspond much better
with actual particulate air quality trends than the control strategy evaluations
of the initial implementation plan, which did not consider fugitive dust.
F-17
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Summary and Recommendations:
The initial purpose of this study x^as to quantitatively evaluate the
adequacy of proposed fugitive dust control regulations in achieving second-
ary particulate air quality standards for three AQCR's in Colorado. However,
the analyses that were performed, including an emission inventory that con-
sidered fugitive dust emissions, indicated that attainment of the secondary
s tandard for particulate matter in semiarid regions may be impossible to
achieve because of the combination of sparse vegetation, low rainfall and
wind.
The emission inventory showed that unp-nvcd road? were the largest
source of particulate, with ar.riculture being the second largest. In the
three AQCR's combined, these two sources accounted for 36 and 34 percent,
respectively, of the particulate emissions inventoried. The other seven
fugitive dust categories -- sanded paved roadc (for snow control), land
development, building construction, highway construction, quarrying/mining,
aggregate storage, and cattle feedlots -- also contributed significant
emissions on a regional basis, so that fugitive dust was responsible for
70 percent of particulate emissions in the Metro-Denver AQCR, 97 percent
in Pawnee AQCR, and 78 percent in San Isabel AQCR.
Several available control methods were identified, either in the
proposed regulations or in published reports on fugitive dust control,
for each source c.ategoi-y except agriculture. Average control efficiencies
of 25 to 85 percent were assigned to these methods for purposes of estimat-
ing the effect of the proposed regulations in reducing emissions and im-
proving air Duality.
The effect of the emission reductions on particulate air quality was
determined by use of the proportional model for each county where high
volumn air sampler data was available. These calculations indicated that
Denver Ccur>1~y would scill have a minimum particulate level of 130 ug/n~:3
amiunl geometric mean ^~Ltec inpleir.eritction of the proposed regulations,
and that the counties surronding Deliver would generally have maxiinum levels
near the primary standard of 75 113/111 . In the Pawnee AQCR, with its ex-
tensive farming areas, all counties with hi^vol ;Uita ware o/nowri to have
projected air qualities at or above 75 ug/m , with 88 ug/ra"' .in Weld County
being the highest projected concentration. In the San Isabel AQCR.> both
Pueblo and El Paso (Colorado Springs area) counties had~projected air
qualities above the primary standard, at 77 and 91 ug/m , respectively,
Existing Colorado control regulations for particulate emissions from
fuel combustion, processes, and other sources were reviewed to determine
•whether additional emission reductions could be obtained from these sources.
Generally, it was concluded that these regulations represent the best avail-
able technology, and no significant improvements could be expected over these
allowable emission rates.
Three recommendations were made in an effort to increase the emission
reductions attributable to the proposed fugitive dust regulations:
F-18
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1. control plans should be required for all road
seqments with traffic densities greater than
20 vehicles/hour, instead of the proposed 30
vehicles/hour on road segments greater than
one-half mile long;
2. the requirements for submitting a control plan
should be modified to insure that all land de-
velopments with unpaved roads must submit a
plan, and
3,, a program should be instituted for the more
rapid and more complete removal of sand from
streets and highways following its application
for snow control.
However, even with these additional provisions, it is still doubtful
that the secondary standards will be achieved in the three AQCR's. The
major problems in achieving the standards are the large contribution of
fugitive dust to total particulate emissions in the regions and the low
control efficiencies attainable for most fugitive dust sources.
(End of PEDCo Report Summary)
F-19
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Adopted: March 14, 1974
Effective: August 1, 1974
Repeal and Reenactment
of Section II.D-
Regulation No. 1
Emission Control Regulations for
Particulates, Smokes, and Sulfur Oxides
for the State of Colorado
II. PARTICULATE EMISSION REGULATIONS -
D. Fugitive Dust:
1. Effective Date and Affected Areas.
a. The existing Section II.D. of Regulation No. 1 controlling
fugitive dust shall be repealed effective July 31, 1974 and
the new Section n.D as follows shall become effective
August 1, 1974 . This delayed effective date for the new
Section II.D allows time for voluntary compliance with
the new provisions.
b. Sections II.D.3, 4 and 5 shall apply only to Commission
designated air pollution control areas as shown on page
1.13 of this Regulation No. 1.
c. Sections II.D.2, 6, 7, 8, and 9 shall apply statewide.
2. Opacity Regulations for Fugitive Dust Emissions Emanating from
Unenclosed Operations .
a. No person shall emit or cause to be emitted from any
source of fugitive dust whatsoever, any particulate
matter which,
(i) at or from the source of said emission, is of
such a shade or density on the property of emission
origination so as to obscure an observer's vision
to a degree in excess of 20% opacity, or
(ii) is visibly transported off the property of emission
origination and remains visible to an observer
positioned off said property when sighting along
a line which does not cross, the property of emission
origination.
F-20
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b. Exceptions from Opacity Regulation Section U.D.2(a).
(i) All unpaved roads and unpaved parking lots
(covered by Section il.D.3).
(ii) Earth and construction-material moving and
excavating activities except for crushing,
grinding, milling, conveying, and bagging
processes. (covered by Section il.D.4).
(iii) Demolition, wrecking, and moving of structures
and explosives detonation activities. (covered
by Section li.D.5).
(iv) Open mining activities. (covered by Section
II.D.6).
(v) Agricultural cultivation activities (regulated
in part by Section II.D.7).
(vi) Sources of fugitive dust which exceed opacity
regulations for a period or periods aggregating
, less than three (3) minutes in any sixty (60)
consecutive minutes.
(vii) Sources of fugitive dust from which dust emissions
exceed opacity regulations when wind velocities
exceed 30 m.p.h. as determined by one or more of
the following practices as approved by the Divisions
By a one-hour average at the nearest official station
of the U.S. Weather Service; by interpretation of
surface weather maps by a qualified meteorologist;
or by use of one or more anemometers at the site.
(viii) any other sources as specified by the Commission.
3. Unpaved Roads and Unpaved Parking Areas .
a. All new unpaved roads and unpaved parking areas:
a-1 No person shall construct or operate a new
unpaved road, or new unpaved parking area
unless a permit therefore has been granted
by the Division pursuant to Section II.D.8.
-------
a-2 Exceptions:
(i) Any new road or parking area which,
after demonstration to the Division,
will not exceed an average daily
traffic count of 165 vehicles averaged
over any consecutive 3-day period.
(ii) Any new road or parking area associated
solely with housing or apartment projects
of seven family dwelling units or less.
(iii) Any new road or parking area to be hard
surfaced (concrete or bituminous binder
and rock) within six (6) months of start
of construction, except that the person
constructing or contracting to construct
said road or parking area shall notify
the Division in advance of commencing
construction of the nature, size, and
location of the hard surfacing project
and the dates on which the road or parking
area construction project is to start and
is to be completed. The person shall use
abatement and preventive measures as out-
lined in II.D.9 during construction.
a-3 The Division may require the person owning or maintain-
ing any new or existing unpaved road to supply traffic
count information on a regular basis to the Division
as necessary to determine if additional abatement and
preventive measures or changes in the implementation
time schedule are required of the person by the Division.
b. Existing Privately Owned or Maintained unpaved Roads and Unpaved
Parking Areas.
b-1 Any person owning any unpaved road or unpaved parking area
or having a right-of-way easement or possessory right to
use the same, found by the Division to exceed a maximum
allowable traffic count of 165 vehicles per day averaged
over any consecutive 3-day period, shall discontinue and
prevent use of that road or parking area, unless the
Division has approved a fugitive dust control plan which
includes preventive measures as outlined in II.D.9 and
unless the conditions of the approved plan are met
continually.
F-22
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c. Existing Publicly Owned or Maintained Unpaved Roads and
Unpaved Parking Areas.
c-1 By July 1 of each year the Division shall submit
to the political subdivision owning or maintaining
unpaved roads or unpaved parking areas and to the
Commission, a report on the nature and degree of
the emissions from existing unpaved roads and
unpaved parking areas within said political sub-
divisions which exceed 165 vehicles per day
averaged over any 3-day period based upon traffic
.count information as collected by the Division
or the political subdivision.
c-2 Said political subdivisions shall submit a plan
and progress report to the Division by October 1
of each year which includes a specified time
schedule for the control of fugitive dust emissions
on unpaved roads and unpaved parking areas as
reported by the Division pursuant to Section II.D.
3(c-1). Said plans shall be based upon:
(i) availability of existing and new funds
for paving or fugitive dust suppression;
(ii) use of preventive measures applicable to
unpaved roads and unpaved parking areas
as outlined in Section II.D.9.
4. Earth and Construction-Material Moving and Excavating except for
Crushing, Grinding, Milling, Conveying and Bagging Processes.
No land developer of a new, or owner of an existing
construction or land development project shall throughout
the duration of the project, disturb or contract to disturb
by grading, excavating or depositing on more total surface
area than five (5) acres of land (in the aggregate) unless
abatement and preventive measures as outlined in section
II.D.9 are being met continually. New sources regulated
in this paragraph 4 must be granted a permit from the
Division pursuant to Section II.D.8 prior to breaking
ground.
5. Demolition, wrecking and Moving of Structures and Explosives
Detonation Activities.
a. No person shall conduct demolition, wrecking, or
moving of structures or explosives detonation
activities unless a permit therefore has been
granted by the Division pursuant to Section II.D.8
and unless the provisions of Section II.D.9 are
being met continually.
F-23
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6. Open Mining Activities:
No developer of a new or owner of an existing open
mining activity shall throughout the duration of the
operation, disturb or contract to disturb by grading,
excavating, or depositing on more total surface area
than one (1) acre of land (in the aggregate) unless
the provisions of Section II.D.9 are being met con-
tinually. New open mining activities must be granted
a permit from the Division pursuant to Section II.D.8
prior to operation. Open mining shall be as defined
in the Colorado Open Mining Land Reclamation Act of
1973 meaning the mining of natural mineral deposits of
limestone used for construction purposes, coal, sand,
gravel, and quarry aggregate, by removing the overburden
lying above such deposits and mining directly from the
deposits thereby exposed. The term includes, but is
not limited to, such-practices as open cut mining, open
pit mining, strip mining, quarrying, and dredging.
7. Complaint Section:
When a complaint of dust or fugitive dust is
registered with the Division by a single complainant
or multiple complainants who allege that any dust or
fugitive dust obstructs or*interferes with the
reasonable and comfortable use of his or their property,
the Division shall investigate and if the Division finds
that such conditions exist, the Division shall issue a
citation to the person or persons from whose land or
activity the objectionable emission emanates and shall
require a fugitive dust control plan containing reasonable
control measures where appropriate according to the
abatement and preventive measures as outlined in Section
II.D.p.
8. New Source Permit Requirements:
a. No permit shall be granted to an applicant unless
the Division determines to its satisfaction that
a plan has been submitted on forms provided by
the Division which includes the following infor-
mation:
F-24
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a-1
a-2
A description of the nature and scope
of the activity and of the existing or
new sources of fugitive dust including
but not limited to the following:
excavating
land leveling
repair or alteration
sand blasting
vehicle movement
screening
drying
waste disposal
detonation of explosives
earth moving
construction
demolition
handling
transporting
mining activities
crushing
site preparation
feed lots
campgrounds
fairgrounds
processing of sand,
gravel and rock
cleaning
mixing
miscellaneous uses of land
storage
quarrying
unpaved roads
unpaved parking areas
Fugitive dust abatement and preventive measures
as outlined in Section II.D.9.
a-3 A time schedule for fugitive dust abatement and
prevention.
a-4 A description of any monitoring or sampling
methods used for recording and reporting
data to the Division.
b. The permit may be granted and renewed for any period of
time as deemed appropriate by the Division.
c. The permit may be granted to any single applicant for
any single project or combination of projects as deemed
appropriate by the Division.
d. In the granting of a permit, the Division may impose
any permit condition it deems necessary to attain and
maintain compliance with the provisions of this
Section II.D.
e. The Division may suspend, revoke, modify, or refuse to
renew or grant a permit under the following conditions:
(i) the requirements of this Section II.D. have
not been met;
(ii) the approved compliance or prevention plan
has not been followed as determined by the
Division, or
(iii) the permit conditions are not met.
Any appeal by an applicant of a denial or revocation of
a permit shall be conducted in accordance with the
-provisions of Sections 66-31-12(4)(f), (g), and (h) of
the Act.
F-25
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9. List of Abatement and Preventive Measures.
a. Unpaved Roads and Unpaved Parking Areas.
a-1 Abatement and preventive measures shall be
approved by the Division and may include but
shall not be limited to frequent watering,
addition of dust palliatives, detouring,
paving, closure, speed control, or other
means such as surface treatment with
penetration chemicals (ligninsulfonates,
oil, water, cutbacks, etc.) or methods of
equal or greater effectiveness in reducing
the air contamination produced.
b. Demolition, Wrecking and Explosive Detonation Activities;
Earth and Construction Material Moving, Mining and
Excavation Activities.
b-1 Abatement and preventive fugitive dust control
measures shall be approved by the Division and
may include, but shall not be limited to:
wetting down, including pre-watering;
landscaping and replanting with native
vegetation;
covering, shielding or enclosing the area;
paving, temporary or permanent;
treating, the use of dust palliatives and
chemical stabilization;
detouring;
restriction of the speed of vehicles on sites;
prevention of the deposit of dirt and mud on
improved streets and roads and other such
effective means of dust control as the
Division may deem necessary;
disturbing less topsoil and reclaiming as
soon as possible.
b-2 Sequential blasting shall be employed whenever or
wherever feasible to reduce the amounts of unconfined
particulate matter;
b-3 Such dust control strategies as ro-vegetation, delay
of surface opening until demanded, or surface
compaction and sealing, shall be applied.
b-4 Haulage equipment shall be washed or wetted down,
treated, or covered when necessary to minimize the
amount of dust emitted in transit and in loading.
b-5 These measures shall also be enforced during periods
when actual construction work is not being conducted,
such as on weekends and holidays.
F-26
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NOTE: THE FOLLOWING DEFINITIONS ARE TO BE ADDED TO THE COMMON PROVISIONS
REGULATIONS, SECTION I, ENTITLED, "DEFINITIONS."
Adopted : March 14, 1974
Effective Date: August 1, 1974
AMENDMENT
TO
COMMON PROVISIONS REGULATIONS
I. DEFINITIONS:
FUGITIVE DUST - Solid airborne particulate matter emitted from
any source other than/an opening which channels
the flow'or air contaminants and then exhausts
the contaminants directly into the atmosphereT1,
Fugitive dust also includes solid particles ~"
released into the atmosphere by natural forces
or. by mechanical processes such as crushing,
grinding, milling, drilling, demolishing,
shoveling, conveying, covering, bagging,
sweeping, etc.
LAND DEVELOPER - Any person, firm, corporation or governmental
entity who initiates any change in the state of
existing land use. The person, firm, corporation
or governmental entity who contracts with others
for construction services for said change in
land use will be deemed to be the land developer.
(DELETE FROM COMMON PROVISIONS REGULATION - DEFINITION OF DUST)
ADD TO PAGE 12 OF REGULATION NO. 1:
I.A. Stationary Air Contamination Sources
2. Exceptions:
(e) THE PROVISIONS OF I.A.I. SHALL
NOT APPLY TO FUGITIVE DUST.
F-27
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Impractical Constraints in Meeting Federal Secondary Ambient Air Quality
Standards for Particulate Matter:
The Commission agrees with the E.P.A. Consultant, PEDCo, on the
impracticality of meeting secondary standards as a result of the unique
semiarid conditions of much of Colorado and the Southwesto In fact,
O
the Federal secondary particulate standard of 150 ug/m is exceeded
on almost completely virgin (undeveloped) areas. For example, at the Sand
Dunes National Monument, 208 ug/m for a 24-hour average was recorded
March 26, 1973 and 628 for Alamosa, Colorado on the University grounds.
Loren Crow, a professional meteorologist, has testified before the Commission,
that based upon data collected by him, this undeveloped area particulate
problem exists for much of the Front Range area. He cited documented
readings of over 300 ug/m for 24-hour periods on windy days east of
Pueblo, Colorado on agricultural lands unaffected by other sources.
It seems that high winds in these semiarid areas take advantage of
the sparse vegetation and the ground literally becomes airborne - a condition
beyond human control and one not adequately recognized by Federal air pollu-
tion control laws. Therefore, we recommend to E.P.A. that when wind
speeds exceed 30 m.p.h. those situations be exempt from meeting the second-
ary particulate matter standard. We concur with the use of annual geo-
metric mean data as a more reasonable basis for a control plan; but never-
theless, feel meeting the Federal Secondary Standard will have a devastat-
ing effect upon the State.
PEDCo stated before the Commission it has reviewed most of the fugitive
dust control regulations in the U.S., and that those proposed by our Commission
are the most restrictive. Surely this must indicate the intent of our
Commission to do everything possible to control particulate matter emissions
as long as a balance is maintained with other needs of our society.
With respect to any significant air pollution source, the Commission
has regulations prohibiting new construction unless the Division determines
to its satisfaction that:
a. The new air contamination source is so designed
and will be constructed or modified to operate
without causing a violation of the emission
control regulations of the Commission, and any
applicable national or local air pollution emis-
sion control ordinances and regulations.
b. The new air contamination source is designed,
built, and equipped in accordance with the best
available practical methods to reduce, prevent
and control air pollution.
c. The new air contamination source, as designed or
modified does not significantly endanger mainten-
ance or attainment as determined by criteria set
forth in IV. C.2 of any ambient air quality standards
of the Commission, and any more stringent national
or local ambient air quality standards.
F-28
-------
With these regulatory measures, significant sources of particulate
matter air pollution are not allowed to construct in Colorado. Existing
sources perhaps face the most stringent fugitive dust control measures
anywhere.
PEDCo has suggested that attaining the secondary standard is not pos-
sible in much of Colorado without closing down many existing activities.
The Commission believes that in order to meet the secondary standard, a
drastic measure as closing down much of Colorado's economy would be necessary.
The Commission thinks such a measure is not realistic, especially when
considering that the secondary standard is not based upon protecting
human health.
Beyond the provisions of this plan an additional 21% or 5,000 tons/yr.
of particulate matter control would be needed to meet the secondary standard
for the Denver AQCR. For the Pawnee AQCR the figures are 20% or 24,500
tons/yr. and for the San Isabel AQCR, 14% or 9,500 tons/yr. Following is
a statement of the social, economic and other problems associated with
achieving the standards, which the Commission feels outweigh the air pollu-
tion benefits that would otherwise accrue.
Unpaved Roads:
Unpaved roads are not a problem in Denver City- County, but for all
problem areas the Commission has adopted the following measures:
1. dust control of all roads in new developments
and all new parking lots of over 165 vehicles
per day traffic.
2. paving of existing roads under a plan and
time schedule prepared by County and City
authorities with maximum available funds for
that purpose, the plans to be approved by
our Division, and
3. maximum traffic counts to serve as a guide
in determing paving priorities.
Road paving is expensive, amounting to about $20,000 a mile for
minimum width two-lane roads. Much testimony has been collected by the
Commission on the limitation of highway user funds and other revenues to
pave the thousands of miles of roads in Colorado air basins. The Commission's
plan calls for maximum possible paving with available funds. The Commission
also recognizes increasing difficulty to acquire asphalt for paving with
the increasing energy crisis.
Sand on Paved Roads:
The Commission seriously doubts the PEDCo recommendation that a 25%
reduction of emissions is possible by picking up sand sooner. The -State
Department of Highways and Denver County Department of Highways have in-
formed our Division that, in their opinion:
F-29
-------
1. The sands used are 1/4 inch diameter material on
down in size, to very fine material,
2. the sands are mostly comprised of river-run
material and decomposed granite and that,
3. road crews are removing sand off the streets as
soon as possible now without endangering the
flow of traffic.
Assuming this information to be correct, eliminating or significantly
reducing street sanding would appear to risk human injury and cause property
damage problems, out of proportion to the air pollution benefits.
Agriculture:
Commission regulations require good conservation practices which save
soil and prevent air pollution. Information has not been submitted to the
Commission as to any practical controls available. Agriculture is a pri-
mary industry of Colorado. Though serious food shortages have not been
felt by this country, surplus is declining. Agricultural and forest lands
are decreasing in this nation at the rate of over one million acres per
year, while our population continues to grow. Some critics warn that agri-
cultural technology may not be keeping pace. We need food and clean air,
and the Commission maintains it is doing everything reasonably possible to
control agricultural air pollution sources.
Land Development and Construction Activities:
The regulations of the Commission require, on a case-by-case basis,
review of all development plans of over 5 acres in the critical air pollu-
tion areas. Additionally, the Commission will consider smaller increments
of road cutting, and requirements for road surfacing, and revegetation and
surface treatment. Watering for dust suppression will be required where
water is avilable. Inherently, earth-moving activities are dusty; especially
where subsurface moisture content is low as in much of the Southwest United
States. Control beyond that adopted by the Commission would most likely
severely inhibit land development and construction activities, an alternative
having serious economic implications. It is our intent to deny permits
only to those development and construction plans which fail to employ all
available practical air pollution controls as provided from time to time in
Commission regulations and policy.
Quarrying Mining, Tailings and Aggregate Storage:
Going beyond the Commission and PEDCo recommendations, with possible
minor exceptions, involves prohibiting the activity or causing severe econo-
mic hardship. Blasting cannot be totally controlled; nor can airborne particu-
late matter be controlled due to high winds. The Commission requires serial
blasting under controlled conditions, wind barriers such as the use of berms
and wind fences, and periodic watering as reasonable measures.
F-30
-------
SULFUR OXIDES
Plan Requirements and Summary of Air Quality Data:
The Federal Register, Vol. 38, No. 178 - September 14, 1973, sets
forth the revised secondary ambient air standard for sulfur dioxide. The
amendments revoke the annual National Secondary Ambient Air Quality
Standard for sulfur dioxide which is 60 micrograms per cubic meter (0.02 ppm).
In addition, the amendments delete the maximum 24-hour concentration of 260
micrograms per cubic meter (0.1 ppm). The secondary 3-hour standard, a
maximum concentration of.1300 micrograms per cubic meter (0.5 ppm) not to
be exceeded more than once per year, remains in effect.
In the Denver Air Quality Control Region, sulfur dioxide as measured at
the CAMP station since January, 1969, has not exceeded 0.30 ppm in any 3-hour
average - well below the secondary 3-hour standard.
The only other region with any potential for sulfur dioxide concentra-
tions is the Four Corners Region. Estimations for concentrations reaching
Colorado from the power plants in New Mexico (23 miles from the Colorado
border) were made for the State Implementation Plan using a point source
model - a procedure permitted for use in Priority 1-A regions. The max9
imum 1-hour concentration computed out as 279 micrograms per cubic meter
(0.11 ppm). Thus the maximum 3-hour value would be less than 0.11 ppm and
well below the secondary 3-hour standard of 0.5 ppm.
In short, a plan for meeting the secondary standard for sulfur oxides
is not needed because the standards are not exceeded in Colorado. The Com-
mission's existing regulations are deemed adequate to maintain the standards
over the foreseeable future.
F-31
-------
APPENDIX G
PROJECTION OF POINT SOURCE PARTICULATE EMISSIONS
The majority of particulate emissions from point sources in the Denver
AQMSA occur within the Joint Regional Planning Program (JRPP) designated
super districts. Therefore, most careful attention is paid to the pro-
jection of particulate emissions within this area while more rural re-
gions are projected only after considering the results of the more ex-
tensive analysis of the super districts.
Due to the fact that different source sectors produce varying amounts of
particulates in the various super districts and that these source sec-
tors are assumed to grow at different rates within each super district,
it is necessary to provide a weighting to each super district within
each county. The point source sectors chosen for consideration are
commercial-institutional (C-I) and industrial. The allocation scheme
for each super district is then based on the amount of C-I employment
and industrial employment within each super district. For the purpose
of this study, the distribution of these parameters is considered not
to have changed significantly between 1970, the last census presented
in the Denver Regional Council of Governments (DRCOG) data; and 1972,
the year of the National Emissions Data System (NEDS) emissions inven-
tory. The 1970-based employment figures for each super district (SD)
are given in Table G-l. The C-I employment is the "total employment"
minus the "mfg., trnsp., commn., util. (mtcu)" which was considered to
be the employment by industry.
G-l
-------
Table G-l. EMPLOYMENT IN THE SUPER DISTRICTS (1970)'
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
C-I Total
30,306
12,340
47,750
12,050
32,030
24,900
12,600
17,420
7,400
34,530 231,326
8,630
7,060
21,530
16,231
5,940 59,391
23,290
300
2,705
6,660
7,830
302 41,087
9,370
4,000
21,000
4,020 38,390
95
1,950
17,900
110
2,660
2,040
2,680
6,830
600
55 34,825
Industrial
9,623
4,523
19,175
13,149
620
5,417
1,489
2,265
1,484
18,376
8,454
1,454
1,983
1,111
1,534
8,551
417
429
3,819
1,147
1
2,477
1,454
5,812
702
0
980
1,797
3,931
2,557
248
152
1,705
173
0
Total
76,121
14,536
14,364
10,445
11,543
Data from the Denver Regional Council of Governments.
G-2
-------
It is assumed that the ratios of emissions from each source sector
among the super districts are equal to the ratios of the characteris-
tic parameter for each source sector. To provide a weighted alloca-
tion of particulate emissions to each district, the percentage of em-
ployment in each super district, as compared to the total in each
county provided by the super district, is calculated (Table G-2) and
then multiplied by the emissions from the corresponding point source
sectors as given in Table G-3. (Particulates from the generation of
electrical energy are not considered in the projections as there are
no new power plants due for construction by 1985 and no announced ex-
pansion plans. Additional electrical requirements are expected to be
absorbed by the new nuclear plant at Fort St. Vrain.) This provides
an allocation of particulate point emissions to the super districts
which is tabulated in Table G-4. (Allocation and projections for
Douglas County are not made as only one super district is given.)
To project these emissions to 1975, 1980, and 1985, growth rates for
the C-I employment and industrial employment are calculated from DRCOG
data. The growth rates for 1975 and 1985 are interpolated by assuming
that the employment grows at a rate such that half of the increase
between 1970 and 1980 and 1980 and 1990 has occurred by 1975 and 1985,
respectively. These growth rates are adjusted to the NEDS baseline
year of 1972 and are presented in Table G-5.
The growth rates for C-I employment and industrial employment are then
applied to the allocated C-I and industrial particulate emissions,
respectively (Table G-4), for each super district. This provides esti-
mates of the emissions for each point source sector and the total with-
in each super district for the years 1975, 1980, 1985, and 1990, and
these are given in Tables G-6, G-7, G-8, and G-9, respectively.
These total emission estimates are then used to calculate a general
point source particulate emission growth rate for each super district.
G-3
-------
Table G-2. PERCENTAGE OF EMPLOYMENT IN EACH SUPER DISTRICT (1970)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
C-I
13.1
5.3
20.6
5.2
13.9
10.8
5.5
7.5
3.2
14.9
14.5
11.9
36.3
27.3
10.0
56.7
0.7
6.6
16.2
19.1
0.7
24.4
10.4
54.7
10.5
100.0
5.6
51.4
0.3
7.6
5.9
7.7
19.6
1.7
0.2
Industrial
12.7
5.9
25.2
17.3
0.8
7.1
2.0
3.0
2.0
24.2
58.3
10.0
13.7
7.7
10.6
59.5
2.9
3.0
26.5
8.0
0.0
23.7
13.9
55.6
6.7
100.0
8.5
15.6
34.2
22.2
2.2
1.3
14.8
1.5
0.0
G-4
-------
Table G-3. PARTICULATE POINT SOURCE EMISSIONS IN JRPP COUNTIES
(1972 NEDS DATA - tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
C-I
131
646
13
0
0
0
Industrial
1,920
7,271
2,719
154
379
2,351
Electrical
401
0
749
0
0
7,586
Total
2,451
7,917
3,481
154
379
9,937
G-5
-------
Table G-4. ALLOCATION OF PARTICULATE POINT EMISSIONS TO
THE SUPER DISTRICTS - 1972 (tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
C-I
17
7
27
7
18
14
7
10
4
20
94
77
234
177
65
7
0
1
2
2
0
0
0
0
0
--
453
4,156
26
617
474
622
1,586
139
13
Industrial
243
114
484
332
16
137
38
57
37
464
4,238
727
995
557
769
1,618
8
52
721
217
0
36
25
84
10
--
200
368
804
523
51
31
349
35
0
Total
260
121
511
339
34
151
45
67
41
484
4,332
804
1,229
734
834
1,625
8
53
723
219
0
36
25
84
10
653
4,524
830
1,140
525
653
1,935
174
13
G-6
-------
Table G-5. GROWTH RATES OF EMPLOYMENT IN THE SUPER DISTRICTS
(BASEYEAR 1972)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
C-I
1975
1.12
1.13
1.08
1.11
1.14
1.15
1.26
1.16
1.22
1.11
1.20
1.19
1.23
1.33
0.99
1.23
6.10
1.38
0.96
1.25
3.20
1.40
2.48
1.20
1.17
--
1.14
1.17
3.08
1.26
1.30
1.33
1.26
2.79
--
1980
1.25
1.26
1.15
1.25
1.27
1.28
1.50
1.33
1.52
1.22
1.40
2.00
1.47
1.67
0.99
1.46
10.80
1.74
0.91
1.49
5.00
1.80
3.95
1.39
1.33
__
1.28
1.33
5.28
1.52
1.59
1.66
1.52
4.58
--
1985
1.35
1.39
1.21
1.34
1.37
1.33
1.76
1.49
1.75
1.31
1.55
1.57
1.73
1.99
0.89
1.67
19.10
1.85
0.87
1.85
5.30
2.29
4.74
1.58
1.53
--
1.43
1.50
5.20
1.63
1.88
1.75
1.72
5.41
—
1990
1.46
1.52
1.26
1.44
1.48
1.48
2.02
1.65
2.02
1.39
1.71
1.74
2.00
2.32
0.79
1.87
27.40
1.97
0.83
2.20
5.60
2.77
5.53
1.78
1.72
—
1.57
1.67
5.13
1.73
2.18
1.77
1.93
6.24
—
Industrial
1975
0.99
1.08
1.10
1.15
1.15
0.99
1.04
1.06
1.16
1.11
1.26
1.18
0.95
1.41
2.38
1.16
1.28
2.25
1.28
1.20
--
1.31
2.17
1.10
1.28
--
1.40
1.03
1.16
1.20
1.15
2.94
1.09
2.63
— —
1980
0.98
1.16
1.20
1.30
1.32
0.98
1.08
1.13
1.31
1.22
1.52
1.37
0.89
1.82
3.75
1.32
1.55
3.11
1.57
1.38
--
1.76
3.33
1.19
1.56
--
1.80
1.06
1.33
1.40
1.28
4.85
1.19
4.28
--
1985
0.90
1.16
1.27
1.45
1.77
0.97
1.09
1.16
1.44
1.29
1.82
1.55
0.86
2.24
5.05
1.46
1.51
3.42
1.87
1.47
--
1.87
3.87
1.25
1.88
--
2.28
1.07
1.47
1.49
1.64
5.10
1.29
5.10
--
1990
0.80
1.25
1.35
1.60
2.23
0.97
1.10
1.19
1.57
1.37
2.11
1.74
0.82
2.65
6.34
1.61
1.46
3.74
2.18
1.56
--
2.11
4.41
1.31
2.20
--
2.77
1.08
1.61
1.58
1.98
5.35
1.40
5.92
--
G-7
-------
Table G-6. PROJECTED PARTICULATE POINT EMISSIONS IN
THE SUPER DISTRICTS - 1975a (tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SB26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
C-I
19.4
7.9
29.0
7.8
20.5
16.0
8.8
11.6
5.3
21.9
111.6
93.2
290.6
236.7
64.8
9.1
—
1.1
2.0
3.1
--
_ _
-_
—
--
--
519.8
4840.1
91.0
780.0
611.9
831.8
1993.6
389.5
Industrial
239.7
123.2
532.7
381.9
18.3
134.9
39.1
60.9
43.1
514.3
5342.0
862.0
939.3
785.1
1821.2
1875.2
10.1
113.9
925.4
257.6
45.9
46.8
54.6
91.7
13.0
--
279.5
378.2
934.0
626.4
57.5
89.4
381.9
95.0
Total
259.1
131.1
561.7
389.7
38.8
150.9
47.9
72.5
48.6
536.2
5453.6
955.2
1229.9
1021.8
1886.0
1884.3
10.1
115.0
927.4
260.7
45.9
46.8
54.6
91.7
13.0
799.3
5218.3
1025.0
1406.4
679.4
921.2
2375.5
384.5
to control case.
G-8
-------
Table G-7. PROJECTED PARTICULATE POINT SOURCE EMISSIONS
IN THE SUPER DISTRICTS - 1980a (tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDll
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
C-I
21.7
8.9
31.0
8.7
22.8
17.9
10.5
13.4
6.6
24.1
130.0
109.5
347.0
297.0
65.0
10.8
0.1
1.4
1.9
3.7
0.3
--
--
--
--
--
586.4
5524.0
156.0
942.7
750.3
1014.3
2401.0
640.0
Industrial
236.8
132.6
581.0
432.0
20.9
133.6
40.7
64.6
48.8
564.9
6445 . 6
997.0
883.9
1013.2
2873.1
2132.6
12.4
157.6
1129.7
298.5
91.5
57.9
84.0
99.8
15.9
--
358.7
388.9
1064.5
731.6
64.1
147.9
415.2
154.7
Total
258.5
141.5
612.0
440.7
43.7
151.5
51.2
78.0
55.4
589.0
6575.6
1106.5
1230.9
1310.2
2938.1
2143.4
12.5
159.0
1131.6
302.2
91.8
57.9
84.0
99.8
15.9
--
945.1
5912.9
1220.5
1674.3
814.4
1189.2
2816.2
794.7
No control case.
G-9
-------
Table G-8. PROJECTED PARTICULATE POINT SOURCE EMISSIONS
IN THE SUPER DISTRICTS - 1985a (tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
C-I
23.5
9.8
32.6
9.4
24.7
18.6
12.3
15.0
7.6
25.8
144.2
122.8
409.2
345.6
58.3
12.3
0.1
1.5
1.8
4.6
0.4
__
--
--
--
--
652.0
6238.5
426.4
1006.3
888.1
1097.8
2728.6
755.8
Industrial
215.9
132.6
616.8
480.8
28.1
133.3
41.1
66.4
53.7
600.4
7704.7
1132.2
849.8
1242.1
3865.8
2368.8
12.1
173.4
1351.0
316.8
96.2
66.7
97.6
104.9
19.2
--
455.7
392.6
1180.7
777.4
81.8
155.4
451.1
184.2
Total
239.4
142.4
649.4
490.2
52.8
151.9
53.4
81.4
61.3
626.2
7848.9
1255.0
1259.0
1587.7
3924.1
2381.1
12.2
174.9
1352.8
321.4
96.6
66.7
97.6
104.9
19.2
--
1107.7
6531.1
1606.1
1783.7
969.9
1253.2
3179.7
940.0
No control case.
G-10
-------
Table G-9. PROJECTED PARTICULATE POINT SOURCE EMISSIONS
IN THE SUPER DISTRICTS - 1990a (tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
C-I
25.3
10.7
34.1
10.0
26.5
20.9
14.5
16.6
8.8
27.4
158.8
132.6
471.6
412.2
51.6
13.8
0.2
1.6
1.7
5.4
0.4
_ _
--
--
—
--
719.6
6953.8
151.4
1069.3
1026.1
1154.3
3056.1
871.7
Industrial
194.8
142.4
652.6
529.9
35.3
133.0
41.5
68.2
58.6
635.7
8963.8
1267.5
815.7
1470.9
4858.5
2604.8
11.7
189.3
1572.1
335.1
100.8
75.5
111.1
110.0
22.4
--
552.7
396.3
1296.7
823.2
99.6
163.0
487.2
213.6
Total
220.1
153.1
686.7
539.9
61.8
153.9
56.0
84.8
67.4
663.1
9122.6
1403.7
1287.3
1883.1
4910.1
2618.6
11.9
190.9
1573.8
340.5
101.2
75.5
III. I
110.0
22.4
--
1272.3
7350.1
1348.1
1892.5
1125.7
1317.3
3543.3
1085.3
No control case.
G-ll
-------
As many of the point sources given in the NEDS are coming under con-
trols promulgated by the State of Colorado, substantial reductions in
point source emissions are due to occur by 1975. Therefore, projec-
tions should not be based on the 1972 data but on the controlled 1975
projected emission levels. The growth rates derived, and presented
in the main text of this document (Section III), are then the ratios
of 1980, 1985, or 1990 emission estimates to the projected 1975 emis-
sions (uncontrolled case).
To provide the base year (1975) projections, all point sources produc-
ing more than 100 tons/year of particulate matter were investigated to
see whether they were in compliance with state regulations. For all
such point sources not in compliance, the process regulations given in
the regulations are applied to provide an allowable emission level.
Because the regulations are only applied to the sources of over 100
tons/year particulates and this presumes the maximum allowable emis-
sions for these sources, it is assumed that this is a liberal (i.e.,
greater than expected) estimate of the level of emissions which can
then be assumed to serve as the 1975 base year emissions. The total
county point source particulate emissions before and after the state
regulations are applied are given in Table G-10.
As can be seen from Table G-10, the state regulations have a signifi-
cant impact on the expected emissions of particulates from point sources,
This would produce a corresponding improvement in the air quality if
point sources are major contributions to its degradation; however, as
shown in Section IV, this is not the case.
G-12
-------
Table G-10. POINT SOURCE EMISSION REDUCTIONS
DUE TO PROMULGATED REGULATIONS -
BY COUNTY
County
Adams
Arapahoe
Boulder
Denver
Jefferson
Larimer
Weld
Tons /year
emissions
1972
2840
2468
8411
2802
7797
2372
6945
1975a
1603
308
1134
1141
928
384
1746
Percent
reduction
44
88
87
59
88
84
75
by application of promulgated point source
regulations to all point sources over 100
tons/year particulates
G-13
-------
APPENDIX H
PROJECTION OF AREA SOURCE PARTICULATE EMISSIONS
The majority of particulate emissions from traditional (non-fugitive)
area sources in the Denver AQMSA occur within the Joint Regional Plan-
ning Program (JRPP) designated super districts. Therefore, most care-
ful attention is paid to the projection of particulate emissions within
this area while more rural regions are projected only after considering
the results of the more extensive analysis of the super districts.
Due to the fact that different source sectors produce varying amounts
of particulates in the various super districts and that these source
sectors are assumed to grow at different rates with each super district,
it is necessary to provide a weighting to each source sector and each
super district within each county. The area source sectors chosen for
consideration are residential, commercial-institutional (C-I), and in-
dustrial. The allocation scheme for each super district is then to con-
sider the amount of population, C-I employment, and industrial employ-
ment within each super district. For the purpose of this study, the
distribution of these parameters is considered not to have changed
significantly between 1970, the last census presented in the Denver
Regional Council of Governments (DRCOG) data; and 1972, the year of the
National Emissions Data System (NEDS) emission inventory. The 1970-
based population and employment figures for each super district (SD)
are given in Table H-l. The population figures are the "total popula-
tion" given in the DRCOG data. The C-I employment is the "total em-
ployment" minus the "mfg., trnsp., commn., util (mtcu)" which was
considered to be the employment by industry.
H-l
-------
Table H-l. POPULATION AND EMPLOYMENT IN THE
SUPER DISTRICTS (1970)a
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDll
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
Popu-
, I. Total
lation
2,697
64,778
61,914
40,867
51,849
62 , 640
42,998
63,213
52,909
74,538 518,405
26,234
50,814
74,101
60,787
8,399 220,335
112,506
1,270
11,141
28,344
29,954
768 182,983
49,050
20,411
67,597
19,427 156,485
315
8,439
36,687
1,137
6,585
17,784
18,573
25,654
9,410
473 124,742
C-I Total
30,306
12,340
47,750
12,050
32,030
24,900
12,600
17,420
7,400
34,530 231,326
8,630
2,060
21,530
16,231
5,940 59,391
23,290
300
2,705
6,660
7,830
302 41,087
9,370
4,000
21,000
4,020 38,320
95
1,951
17,900
110
2,660
2,040
2,680
6,830
600
55 34,825
Indus-
trial
9,623
4,523
19,175
13,149
620
5,417
1,489
2,265
1,484
18,376
8,454
1,454
9,983
1,111
1,534
8,551
417
429
3,819
1,147
1
2,477
1,454
5,812
702
0
980
1,797
3,931
2,557
248
152
1,705
173
0
Total
76,121
14,536
14,364
10,445
11,543
Data from the Denver Regional Council of Governments
H-2
-------
It is assumed that the ratios of emissions from each source sector
among the super districts are equal to the ratios of the characteristic
parameter for each source sector. To provide a weighted allocation of
particulate emissions to each district, the percentage of population
and employment in each super district, as compared to the total in each
county provided by the super districts, is calculated (Table H-2) and
then multiplied by the emissions from the corresponding area source
sectors as given in Table H-3. (Particulates from the transportation
sector are not considered at this time but are projected separately and
averaged in later.) This provides an allocation of particulate area
emissions to the super districts which is tabulated in Table H-4. (Al-
location and projections are not made for Douglas County as only one
super district is given.)
To project these emissions to 1975, 1980, and 1985, growth rates for
the total population, C-I employment, and industrial employment, are
calculated from the DRCOG data. The growth rates for 1975 and 1985
are interpolated by assuming that the population and employment grows
at a rate such that half of the increase between 1970 and 1980 and 1980
and 1990 has occurred by 1975 and 1985, respectively. These growth
rates are adjusted to the NEDS baseline year of 1972 and are presented
in Tables H-5, H-6, H-7, and H-8.
These growth rates for population, C-I employment, and industrial em-
ployment are then applied to the allocated residential, C-I, and in-
dustrial particulate emissions, respectively (Table H-4), for each
super district. This provides estimates of the emissions for each
area source sector and the total within each super district for the
years 1975, 1980, 1985, and 1990 and these are given in Tables H-9,
H-10, H-ll, and H-12, respectively.
These estimates of total area emissions from the residential, C-I, and
industrial sectors are used to calculate a general stationary area source
particulate emission growth rate for each super district. As these
H-3
-------
Table H-2. PERCENTAGE OF POPULATION AND EMPLOYMENT
IN THE SUPER DISTRICTS (1970)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
Population
0.5
12.5
11.9
7.9
10.0
12.1
8.3
12.2
10.2
14.4
11.9
23.1
33.6
27.6
3.8
61.5
0.7
6.1
15.5
15.8
0.4
31.3
13.0
43.2
12.5
100.0
6.8
29.4
0.9
5.3
14.3
14.9
20.6
7.6
0.4
C-I
13.1
5.3
20.6
5.2
13.9
10.8
5.5
7.5
3.2
14.9
14.5
11.9
36.3
27.3
10.0
56.7
0.7
6.6
16.2
19.1
0.7
24.4
10.4
54.7
10.5
100.0
5.6
51.4
0.3
7.6
5.9
7.7
19.6
1.7
0.2
Industrial
12.7
5.9
25.2
17.3
0.8
7.1
2.0
3.0
2.0
24.2
58.3
10.0
13.7
7.7
10.6
59.5
2.9
3.0
26.5
8.0
0.0
23.7
13.9
55.6
6.7
100.0
8.5
15.6
34.2
22.2
2.2
1.3
14.8
1.5
0.0
H-4
-------
Table H-3. PARTICUIATE AREA EMISSIONS IN JRPP COUNTIES
(1972 NEDS DATA - tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Residential
359
164
128
106
9
110
C-I
393
167
173
116
20
186
Industrial
4,011
1,348
581
635
20
849
Transportation
2,422
527
384
366
24
312
Total
7,186
2,205
1,265
1,224
72
1,457
H-5
-------
Table H-4. ALLOCATION OF PARTICULATE AREA EMISSIONS
TO THE SUPER DISTRICTS - 1972 (tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDll
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
Residential
2
45
43
28
36
43
30
44
37
52
20
38
55
45
6
79
1
8
20
20
1
33
14
45
13
--
8
32
1
6
16
16
23
8
1
C-I
52
21
81
21
54
42
21
30
13
59
24
20
61
46
17
98
1
11
28
33
1
28
12
63
12
--
62
564
4
84
64
85
215
19
2
Industrial
507
238
1,011
693
33
286
79
120
78
969
786
135
184
103
142
346
17
17
154
46
0
147
104
345
42
--
72
133
290
189
18
11
126
13
0
Total
561
304
1,135
742
123
371
130
193
128
1,080
830
193
300
194
165
523
19
36
202
99
2
208
130
453
67
--
142
729
295
279
98
112
364
40
3
H-6
-------
Table H-5. GROWTH RATES OF POPULATION AND EMPLOYMENT
IN THE SUPER DISTRICTS - 1972 TO 1975
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SD11
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
Residential
1.00
0.90
0.95
1.04
1.17
1.10
1.18
1.09
1.09
0.96
1.41
1.28
1.13
1.36
2.27
1.20
2.90
1.14
1.01
0.89
1.00
1.41
1.75
1.09
1.18
--
1.39
1.11
2.70
1.51
1.11
1.18
1.17
1.65
--
C-I
1.12
1.13
1.08
1.11
1.14
1.15
1.26
1.16
1.22
1.11
1.20
1.19
1.23
1.33
0.99
1.23
6.10
1.38
0.96
1.25
3.20
1.40
2.48
1.20
1.17
--
1.14
1.17
3.08
1.26
1.30
1.33
1.26
2.79
--
Industrial
0.99
1.08
1.10
1.15
1.15
0.99
1.04
1.06
1.16
1.11
1.26
1.18
0.95
1.41
2.38
1.16
1.28
2.25
1.28
1.20
--
1.31
2.17
1.10
1.28
--
1.40
1.03
1.16
1.20
1.15
2.94
1.09
2.63
--
H-7
-------
Table H-6. GROWTH RATES OF POPULATION AND EMPLOYMENT
IN THE SUPER DISTRICTS - 1972 TO 1980
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SDl
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDll
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
Residential
1.10
0.79
0.90
1.08
1.34
1.19
1.37
1.18
1.19
0.93
1.84
1.57
1.26
1.71
3.50
1.40
4.90
1.30
1.02
1.27
1.40
1.79
2.52
1.30
1.34
--
1.84
1.20
4.50
2.20
1.24
1.33
1.37
2.26
--
C-I
1.25
1.26
1.15
1.25
1.27
1.28
1.50
1.33
1.52
1.22
1.40
2.00
1.47
1.67
0.99
1.46
10.80
1.74
0.91
1.49
5.00
1.80
3.95
1.39
1.33
--
1.28
1.33
5.28
1.52
1.59
1.66
1.52
4.58
--
Industrial
0.98
1.16
1.20
1.30
1.32
0.98
1.08
1.13
1.31
1.22
1.52
1.37
0.89
1.82
3.75
1.32
1.55
3.11
1.57
1.38
--
1.76
3.33
1.19
1.56
__
1.80
1.06
1.33
1,40
1.28
4.85
1.19
4.28
—
H-8
-------
Table H-7. GROWTH RATIO OF POPULATION AND EMPLOYMENT
IN THE SUPER DISTRICTS - 1972 TO 1985
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SD11
SD12
SD13
SDH
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
Residential
1.15
1.20
0.98
1.68
1.46
1.27
1.48
1.24
1.16
0.94
2.11
1.59
1.32
1.84
7.97
1.45
9.30
1.31
1.00
1.59
1.50
2.11
3.33
1.40
1.33
--
2.14
1.18
5.00
2.28
1.25
1.36
1.44
2.55
--
C-I
1.35
1.39
1.21
1.34
1.37
1.33
1.76
1.49
1.75
1.31
1.55
1.57
1.73
1.99
0.89
1.67
19.10
1.85
0.87
1.85
5.30
2.29
4.74
1.58
1.53
--
1.43
1.50
5.20
1.63
1.88
1.75
1.72
5.41
--
Industrial
0.90
1.16
1.27
1.45
1.77
0.97
1.09
1.16
1.44
1.29
1.82
1.55
0.86
2.24
5.05
1.46
1.51
3.42
1.87
1.47
--
1.87
3.87
1.25
1.88
--
2.28
1.07
1.47
1.49
1.64
5.10
1.29
5.10
--
H-9
-------
Table H-8. GROWTH RATIO OF POPULATION AND EMPLOYMENT
IN THE SUPER DISTRICTS - 1972 TO 1990
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
Residential
1.20
0.78
1.06
1.26
1.58
1.35
1.60
1.30
1.13
0.94
2.37
1.61
1.39
1.98
12.40
1.50
13.70
1.34
0.98
1.91
1.50
2.42
4.14
1.50
1.32
--
2.44
1.16
5.50
2.35
1.24
1.38
1.51
2.85
--
C-I
1.46
1.52
1.26
1.44
1.48
1.48
2.02
1.65
2.02
1.39
1.71
1.74
2.00
2.32
0.79
1.87
27.40
1.97
0.83
2.20
5.60
2.77
5.53
1.78
1.72
—
1.57
1.67
5.13
1.73
2.18
1.77
1.93
6.24
--
Industrial
0.80
1.25
1.35
1.60
2.23
0.97
1.10
1.19
1.57
1.37
2.11
1.74
0.82
2.65
6.34
1.61
1.46
3.74
2.18
1.56
--
2.11
4.41
1.31
2.20
--
2.77
1.08
1.61
1.58
1.98
5.35
1.40
5.92
--
H-10
-------
Table H-9. PROJECTED PARTICULATE AREA SOURCE EMISSIONS
IN THE SUPER DISTRICTS - 1975 (tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
Residential
2.0
40.2
40.8
29.2
42.1
47.3
35.4
47.9
40.3
50.0
28.1
48.7
62.3
61.0
13.6
94.5
2.9
9.1
20.1
17.8
1.0
46.6
24.5
49.1
15.3
--
11.1
35.4
2.7
9.5
17.8
18.8
27.0
13.2
1.0
C-I
58.1
23.7
87.2
23.4
61.5
48.1
26.4
34.8
15.9
65.5
28.8
23.8
75.1
61.2
16.8
120.6
6.1
15.2
26.8
41.2
3.2
39.3
29.7
75.4
14.0
--
70.5
657.1
12.3
105.9
83.1
113.0
270.6
53.0
2.0
Industrial
500.8
257.6
1112.8
797.8
38.0
281.9
81.8
127.2
90.1
1074.5
990.6
158.8
174.1
145.6
337.6
400.7
21.8
38.2
197.8
55.0
15.3
192.6
225.3
378.1
53.7
--
100.9
136.6
337.2
227.0
20.7
32.3
136.9
34.2
--
Total
560.9
321.5
1240.8
850.4
141.6
377.3
143.6
209.9
146.3
1190.0
1047.5
232.3
311.5
267.8
368.0
615.8
30.8
62.5
244.7
114.0
19.5
278.5
279.5
502.6
83.0
--
182.5
829.1
352.2
342.4
121.6
164.1
434.5
100.4
3.0
H-ll
-------
Table H-10. PROJECTED PARTICIPATE AREA SOURCE EMISSIONS
IN THE SUPER DISTRICTS - 1980 (tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SD11
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
Residential
2.2
35.6
38.9
30.1
48.3
51.1
41.0
52.0
43.9
48.3
36.8
59.6
69.3
76.8
21.0
110.3
4.9
10.4
20.4
25.3
1.4
59.1
35.3
58.6
17.4
--
14.7
38.3
4.5
13.2
19.9
21.2
31.5
18.1
C-I
64.8
26.5
93.2
26.2
68.5
53.8
31.5
40.0
19.7
72.2
33.5
29.9
89.6
76.7
16.8
143.2
10.8
19.1
25.6
49.3
5.0
50.5
47.4
87.5
16.0
--
79.6
749.9
21.1
127.9
101.9
141.4
325.9
87.0
Industrial
494.7
277.1
1213.9
902.4
43.6
279.0
85.0
135.0
102.1
1180.3
1195.3
184.9
163.8
187.9
532.6
455.7
26.3
52.8
241.4
63.8
30.5
258.3
346.5
411.2
65.6
--
129.5
140.4
384.5
264.6
23.1
53.4
150.0
55.6
Total
561.7
339.2
1346.0
958.7
160.4
383.9
157.5
227.0
165.7
1300.8
1265.6
272.4
322.7
341.4
570.4
709.2
42.0
82.3
287.4
138.4
36.9
367.9
429.2
557.3
99.0
--
223.8
928.6
410.1
405.7
144.9
216.0
507.4
160.7
H-12
-------
Table H-ll. PROJECTED PARTICULATE AREA SOURCE EMISSIONS
IN THE SUPER DISTRICTS - 1985 (tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SD11
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
Residential
2.3
54.1
42.3
32.7
52.5
54.5
44.5
54.6
42.9
48.7
42.1
60.3
72.8
82.7
47.8
114.3
9.3
10.5
20.0
31.7
1.5
69.5
46.6
63.1
17.3
--
17.1
37.7
5.0
13.7
20.0
21.7
33.2
20.4
C-I
70.3
29.2
97.8
28.2
74.1
55.8
36.9
44.7
22.7
77.2
37.2
31.3
105.7
91.6
15.1
163.3
19.1
20.4
24.4
60.9
5.3
64.0
56.9
99.7
18.3
--
88.6
847.0
20.8
136.6
120.6
149.1
370.4
102.8
Industrial
451.1
277.1
1288.6
1004.3
58.5
278.5
86.0
138.7
112.3
1254.2
1428.8
209.9
157.5
230.4
716.6
506.2
25.6
58.2
288.7
67.7
32.0
274.5
402.5
432.3
79.1
--
164.5
141.8
426.1
281.2
29.5
56.1
162.9
66.3
Total
523.7
360.4
1428.7
1065.2
185.1
388.8
167.4
238.0
177.9
1380.1
1508.1
301.5
336.0
404.7
779.5
786.8
54.0
89.1
331.1
160.3
38.8
408.0
506.0
595.1
114.7
--
270.2
1026.5
451.9
431.5
170.1
226.9
566.5
189.5
H-13
-------
Table H-12. PROJECTED PARTICIPATE AREA SOURCE EMISSIONS
IN THE SUPER DISTRICTS - 1990 (tons/year)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDll
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
Residential
2.4
35.0
45.7
35.3
56.7
57.9
48.0
57.1
41.9
49.1
47.4
61.0
76.3
88.9
74.6
118.3
13.7
10.7
19.5
38.2
1.5
79.9
58.0
67.5
17.2
--
19.5
37.0
5.5
14.1
19.9
22.1
34.8
22.8
C-I
75.8
31.9
102.4
30.2
79.8
62.1
42.4
49.5
26.3
82.1
41.0
34.7
121.8
106.5
13.4
183.4
27.4
21.7
23.1
72.5
5.6
77.5
66.3
111.9
20.6
--
97.6
944.1
20.5
145.2
139.3
150.8
414.8
118.5
Industrial
407.0
297.6
1363.4
1106.9
73.5
277.9
86.8
142.5
122.5
1328.1
1662.3
235.0
151.2
272.8
900.6
556.6
24.9
63.5
336.0
71.6
33.6
310.7
458.4
453.4
92.6
--
199.5
143.1
468.3
297.8
35.9
58.9
175.9
76.9
Total
485.2
346.5
1511.5
1172.4
210.0
397.9
177.2
249.1
190.7
1459.3
1750.7
330.7
349.3
468.2
988.6
858.3
66.0
95.9
378.6
182.3
40.7
468.1
582.7
632.8
130.4
--
316.6
1124.2
494.3
457.1
195.1
231.8
625.5
218.2
H-14
-------
stationary area sources are not presumed to come under any controls ,
the base year emissions can be assumed to be those of the 1972 NEDS
emission inventory. The growth rates derived for stationary area
sources are then the rates of the 1975, 1980, 1985, or 1990 emissions
estimates to the allocated 1972 emissions inventory (Table H-4).
These stationary area source growth rates, base year 1972, are pre-
sented in Table H-13.
Since the transportation sector provides a substantial contribution to
the total area source particulates (more than one-third in Denver
County), it is necessary to also project any increased particulates
from this source sector. Functional-system annual travel data by urban
and rural areas is available from the Colorado Highway Department for
the years of 1968 and 1990. This data is presented in Table H-14 along
with the growth rate. Assuming a constant growth over the years, growth
rates for 1975, 1980, 1985, and 1990 can be generated for the base year
of 1972.
These growth rates do not represent the actual growth of particulates,
due to the installation of catalytic mufflers which will have some effect
in reducing the particulate emissions. Based on the fact that 61.7 per-
cent, 94.2 percent, and 100 percent of cars (from Table L-3) are expected
to be so equipped by 1980, 1985, and 1990, respectively, and that such
cars will produce around 60 percent less particulates in their exhaust (or
a total of 39 percent less since 37 percent of motor vehicle emissions are
a result of tires), the actual growth rates of motor vehicle related par-
ticulate emissions can be calculated.
Using these growth rates and the proportionality of the contribution of
particulates due to transportation sources (from Table H-3) it is pos-
sible to provide a rate of the growth of particulates due to all area
sources. These weighted rates are presented in the text of the report
(Section III).
H-15
-------
Table H-13. STATIONARY AREA SOURCE GROWTH RATES
BY SUPER DISTRICTS (BASEYEAR 1972)
County
Denver
Jefferson
Adams
Arapahoe
Douglas
Boulder
Area
SD1
SD2
SD3
SD4
SD5
SD6
SD7
SD8
SD9
SD10
SDH
SD12
SD13
SD14
SD15
SD16
SD17
SD18
SD19
SD20
SD29
SD21
SD22
SD23
SD24
SD25
SD26
SD33
SD34
SD35
SD36
SD37
SD38
SD39
SD40
1975
1.00
1.06
1.09
1.15
1.15
1.02
1.10
1.09
1.14
1.10
1.26
1.20
1.04
1.38
2.23
1.18
1.62
1.74
1.21
1.15
9.75
1.34
2.15
1.11
1.24
--
1.29
1.14
1.19
1.23
1.24
1.47
1.19
2.51
--
1980
1.00
1.12
1.19
1.29
1.30
1.03
1.21
1.18
1.29
1.20
1.52
1.41
1.08
1.76
3.46
1.36
2.21
2.29
1.42
1.40
18.45
1.77
3.30
1.23
1.48
--
1.58
1.27
1.39
1.45
1.48
1.93
1.39
4.02
--
1985
0.93
1.19
1.26
1.44
1.50
1.05
1.29
1.23
1.39
1.28
1.82
1.56
1.12
2.09
4.72
1.50
2.84
2.48
1.64
1.62
19.40
1.96
3.89
1.31
1.71
--
1.90
1.41
1.53
1.55
1.74
2.03
1.56
4.74
—
1990
0.86
1.14
1.33
1.58
1.71
1.07
1.36
1.29
1.49
1.35
2.11
1.71
1.16
2.41
5.99
1.64
3.47
2.66
1.87
1.84
20.35
2.25
4.48
1.40
1.95
--
2.23
1.54
1.68
1.64
1.99
2.07
1.72
5.46
—
H-16
-------
Table H-14. FUNCTIONAL-SYSTEM ANNUAL TRAVEL DATAC
County
Adams
Urban
Ruralb
Arapahoe
Urban
Ruralb
Boulder
Urban
Ruralb
Clear Creek
Urban
Ruralb
Denver
Urban
Ruralb
Douglas
Urban
Ruralb
Gilpin
Urban
Ruralb
Jefferson
Urban
Ruralb
Larimer
Urban
Ruralb
Weld
Urban
Ruralb
Millions of vehicle miles
1968
198.0
15.1
182.9
86.5
--
86.5
471.9
211.3
260.6
95.3
--
95.3
3782.6
3782.6
--
207.3
--
207.3
14.1
--
14.1
273.3
--
273.3
443.8
134.5
309.2
593.4
106.6
486.8
1990
370.7
33.1
337.5
140.5
--
140.5
909.5
488.0
421.5
227.6
--
227.6
8467.6
8467.6
--
432.4
--
432.4
25.1
--
25.1
653.1
--
653.1
827.5
272.8
554.7
1020.1
209.5
810.6
Growth rate
1968-1990
1.87
2.19
1.85
1.62
—
1.62
1.93
2.31
1.62
2.39
2.39
2.24
2.24
--
2.09
--
2.09
1.78
--
1.78
2.39
--
2.39
1.86
2.03
1.79
1.72
1.97
1.67
Data from the Colorado Highway Department.
Includes all cities less than 5,000 population.
H-17
-------
APPENDIX I
The following gives a detailed explanation of the method used to allocate
fugitive dust emissions.
1. Fugitive dust totals, in tons per year, were obtained
from the PEDCo report. This information is given at
the end of this Appendix in Table 1-1.
2. Counties are divided into subunits, or zones. Each
zone is an area where land use is specified. State
land use maps are used to determine this.
3. Fugitive dust from agriculture is allocated only to
cropland zones. Fugitive dust from sand on paved
roads is assigned only to urban areas.
4. The county fugitive dust total minus the agricultural
or sanding emissions constitute the fugitive dust which
is allocated evenly throughout the county. In order to
do this, the land area of each zone is calculated. If
a specific zone is 20 percent of the county land area
total, then this zone is allocated 20 percent of these
nonassigned fugitive dust emissions.
5. The total fugitive dust for a given zone is the sum of
agricultural or sanding emissions plus the nonassigned
emissions total.
6. This total is expressed in final form as yearly emis-
sions per 4 km 2 area.
The calculations are given below. The first set of calculations is ex-
plained to enhance the reader's understanding of the approach.
1-1
-------
County Zone
Adams 1
2
Emissions (tons/yr)
6358 + 0.66 (19,700) = 19,360
0.34 (19,700) = 6,698
tons/yr/
Area (km ) 4 km 4 km2
2025
1050
506
263
38.26
25.47
Explanation
Zone 1 in Adams County is cropland. Thus, it is assigned all agricultural
emissions for the county, in this case 6,358 tons/yr. The land area of
zone 1 is 66 percent of the county land area (2025/3075). It therefore is
assigned 66 percent of the nonassigned emissions. The nonassigned emis-
sions for Adams is the total fugitive dust (26,058) minus the agricultural
emissions (6358), or 19,700 tons.
Zone 2 is rangeland. No specific emissions are assigned. The emissions
from zone 2 is simply its land area as a percentage of total county land
area multiplied by the nonassigned emissions.
County
Arrapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Zone
1
2
3
1
2
3
Sole
zone
Sole
zone
Sole
zone
Sole
zone
Emissions
821 + 0.34 (14,
0.31
0.35
6586
0.20
0.56
7437
8018
5629
(14,291) =
(14,291) =
+ 0.24 (13
(13,591) =
(13,591) =
(tons/yr)
291) = 5680
4430
5002
,591) = 9848
2718
7611
18,228
Area
(km2)
691
624
700
468
390
1073
1000
201
2267.5
340
tons/yr/
4 km2
32.88
28.40
28.58
84.17
27.88
28.40
29.75
159.56
9.93
214.45
1-2
-------
County
Jefferson
Larimer
Weld
Zone
1
2
3
1
2
3
1
2
Emissions (tons/yr)
2581 + 0.11 (15,221) = 4255
0.37 (15,221) = 5632
0.52 (15,221) = 7915
15,551 + 0.26 (20,203) = 20,804
0.62 (20,203) = 12,526
0.12 (20,203) = 2424
77,295 + 0.31 (37,317) = 88,863
0.69 (37,317) = 25,749
Area
230
735
1044
1773
4275
822
868
7681
tons/yr/
4 km2
74.00
30.65
30.33
46.96
11.72
11.49
102.38
13.41
1-3
-------
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1-4
-------
APPENDIX J
PROJECTION OF FUGITIVE DUST EMISSIONS
GENERAL
This appendix will describe the process by which future emissions of
fugitive dust were estimated, both with and without proposed control
measures.
Base data for the fugitive dust emissions were obtained from a report
entitled, "Investigation of Fugitive Dust -- Sources, Emissions, and
Control -- for Attainment of Secondary Ambient Air Quality Standards/
Colorado," performed by PEDCo-Environmental Specialists for EPA.
That report, which will be referred to hereinafter as the PEDCo report,
included a 1972 inventory of fugitive dust sources, estimates of the
possible degree of control by various techniques, and calculated reduc-
tions in emissions from recommended control strategies.
The starting point for the present analysis was the inventory data from
the PEDCo report, reproduced in Appendix I as Table 1-1.
The fugitive dust information from the PEDCo report was adjusted to ob-
tain a representation of dust emissions from various parts of each
county as described in Appendix I. Then, forecasts were made for two
cases and then re-allocated in the manner described in Appendix I.
The two cases were for (1) the degree of control required by present
regulations and (2) the additional control resulting from regulations
J-l
-------
proposed in the contingency attainment plan (Section V). Each of these
cases will be reviewed separately, and then forecasts of future emis-
sions will be reviewed.
ESTIMATING CONTROL FROM EXISTING REGULATIONS
The Colorado Air Pollution Control Commission has recently approved a
new regulation for control of fugitive dust. This regulation, Section
II-D of Regulation Number 1, is provided in full in Appendix E and
summarized in Section III. The regulation affects several types of
dust sources, each of which will be discussed next.
Effect of Regulation by Source Types
Sources are reviewed in the same order as listed in Table 1-1 in
Appendix I.
Unpaved Roads - The promulgated regulation requires control techniques
be applied to parking lots and unpaved roads with more than 165 vehicles
per day (vpd). To determine the effect of this requirement involved
several steps. This procedure is the same as was used by PEDCo but was
applied to a limiting volume of 165 vpd instead of 250 vpd as in the
PEDCo report. The procedure was:
1. A determination was made of the average amount of traffic
on unpaved roads in each county. This information had
been provided to PEDCo by the Colorado Division of High-
ways but was not included in their report and was thus
obtained from PEDCo in a telephone conversation. The
data are listed in Table J-l.
2. A calculation was made of the percentage of total daily
vehicle-miles of travel on unpaved roads which were on
roads with more than 165 vpd. That is, this calculation
determined what fraction of total VMT (and total emissions)
are on roads controlled by the regulations. This step used
the same procedure as used by PEDCo and is summarized in
Table J-2. For the purpose of this step it was assumed
that all roads with more than 165 vpd will be controlled
J-2
-------
Table J-l. ESTIMATED AVERAGE DAILY TRAFFIC ON
UNPAVED ROADS, BY COUNTY, 1972
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Estimated average
daily traffic3
30
30
40
20
30
30
20
50
30
20
a
Average daily traffic on all un-
paved roads, estimated by Colorado
Division of Highways and provided
in Reference 2.
Table J-2. CALCULATION OF AMOUNT OF TRAFFIC ON CONTROLLED
UNPAVED ROADS
(1)
Avg. ADT for un-
paved roads in
county
20
30
40
50
(2)
% of roads
w/ADT of 165
vpd or more3
2.3
4.0
7.0
9.7
(3)
Avg. ADT on
roads w/ADT
of 165 vpd
or more
225
230
230
230
(4)
Ratio of
C3) to (1)
11.3
7.7
5.7
4.6
% of VMT on
roads w/165
vpd or more
((2) x (4))
26.0
30.8
39.9
44.6
Source: Figure 4.1, Reference 1.
J-3
-------
to the extent estimated by PEDCo, whereas the regula-
tion requires control of private roads and of public
roads only to the extent allowed by financial resources.
It was assumed that all eligible roads will be con-
trolled by 1975, there being no basis for estimating
what financial restraints may prevail. Consequently,
the degree of control may be less than calculated here.
3. An estimate was made of what fraction of affected un-
paved roads are within the Priority I portion of the
county. (The existing regulation applies to only
those unpaved roads and parking lots within the Pri-
ority I area shown in Figure 26.) This estimate was
based upon judgment, using available information on
development patterns and traffic volumes. This esti-
mate is listed in Table J-3, which also shows the net
reduction in emissions from this source, using the
control efficiency of 60 percent from PEDCo.
Sand on Paved Roads, Agriculture - No control on these source categories
is included in the promulgated regulations.
Land Development - Control efficiency was assumed to be 60 percent, as
developed by PEDCo. This degree of control was assumed to apply to
the portion of development occurring in the Priority I area, as tabu-
lated in Table J-4, because the regulation applies only to that area.
Residential and Commercial Construction - Emission reductions were cal-
culated from the PEDCo report's control efficiency of 50 percent. The
area factors shown in Table J-5 were used because the regulation applies
only in the Priority I area.
Highway Construction - Again, the regulations apply only to the Priority
I area, so that area factors from Table J-4 (for land development activ-
ity) were used again, along with the PEDCo control efficiency of 37.5
percent.
Quarrying, Mining, and Tailings - The PEDCo control efficiency of 75
percent was used for all portions of all counties.
J-4
-------
Table J-3. DEGREE OF CONTROL OF FUGITIVE DUST ON UNPAVED
ROADS, BY COUNTY
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
(1)
Fraction of
travel
affected3
0.308
0.308
0.399
0.26
0.308
0.308
0.26
0.446
0.308
0.26
(2)
Portion of
affected roads
in Priority I
area
0.75
0.60
1.00
0
1.00
0
0
1.00
0.50
0.75
(3)
Control ,
efficiency
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
0.60
Net percentage
reduction in
emissions from
unpaved roads
(CD x (2) x (3))
13.9
11.1
23.9
0
4.8
0
0
26.8
9.2
11.7
aFrom Table J-2.
From Reference 1-
Table J-4. ESTIMATED PERCENTAGE OF LAND DEVELOPMENT
ACTIVITY IN PRIORITY I AREA, BY COUNTY
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Lar imer
Weld
Estimated
a
percentage
90
70
100
0
100
0
0
100
70
90
Based upon data in maps published
by Colorado Land Use Commission
(Reference 3).
J-5
-------
Table J-5. ESTIMATED PERCENTAGE OF RESIDENTIAL-COMMERCIAL CON-
STRUCTION ACTIVITY IN PRIORITY I AREA, BY COUNTY
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Lar imer
Weld
Estimated
a
percentage
90
90
100
0
100
0
0
100
90
90
rt
Based upon data in maps published
by Colorado Land Use Commission
(Reference 3).
Aggregate Storage - The PEDCo control efficiency of 50 percent was ap-
plied to all portions of all counties.
Cattle Feedlots - No control regulations were promulgated for this source.
Net Effect - The new emissions, developed through the procedures out-
lined above, are shown in Table J-6. (These should be compared with
Table 1-1 in Appendix I to observe the reduction in emissions.) The
emissions in Table J-6 were assumed to occur in 1975 and are the base
case from which all further fugitive dust computations were made. These
county totals were then allocated to the analysis zones through the pro-
cedures described in Appendix I, and Table 17 shows the result of this
process. (The 1975 entries in Table 17 are the ratios of the emissions
from Table J-6 to those in Table 1-1, after allocation by zone.)
J-6
-------
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-------
ESTIMATING CONTROL FROM PROPOSED ADDITIONAL REGULATIONS
The second case analyzed was for an assumed, more restrictive regula-
tion for control of fugitive dust. The changes were described in Sec-
tion V and are discussed below by source category.
Effect of Regulation by Source Types
Unpaved Roads - The regulation was assumed to apply throughout the AQMSA.
Hence, the total reduction was found by using the data from Table J-3
except that the items in column (2) were all 1.00.
Sand on Paved Roads - All emissions were reduced by a control efficiency
of 25 percent, as estimated by the PEDCo report.
Agriculture - No control regulations were assumed, in keeping with the
finding of the PEDCo report that controls are not feasible.
Land Development, Residential-Commercial Contraction, Highway Construc-
tion - The same techniques were used except that area factors in Tables
J-4 and J-5 were taken to be 1.0 because the proposed regulations would
apply to the entire AQMSA.
Quarrying, Mining, and Tailings, Aggregate Storage - No additional con-
trol was assumed.
Cattle Feedlots - Based upon the discussion in the PEDCo report, it was
assumed that emissions from this source category could be reduced by
50 percent; however, this was determined to have an insignificant impact
on emissions and be politically infeasible.
Net Effect - Table J-7 lists the total emissions with the maximum con-
trol strategy described above. Again, it was assumed this degree of
J-i
-------
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-------
control would be applied by 1975. Also, these emissions were distri-
buted among the zones with the procedures of Appendix I. The data for
1975 in Table 35 are the ratios of the emissions from Table J-7 to the
emissions from Table 1-1, after allocation.
FORECASTS OF GROWTH IN FUGITIVE DUST EMISSIONS
For each of the two sets of regulations, the two cases described above,
projections were made of emissions in 1980 and 1985. Change between
1972 and 1975 was considered negligible. One projection was made for
each year, and separately applied to the data in Tables J-6 and J-7.
The growth projections will be discussed by source category.
Growth Projections by Source Category
Unpaved Roads - No change is assumed. Increased traffic and increased
numbers of unpaved roads are assumed to be offset by increasing con-
trol.
Sand on Paved Roads - Emissions from this source were assumed to be
proportional to vehicle-miles of travel (VMT), in accordance with the
PEDCo report. Data on VMT by county were provided by the Colorado Di-
vision of Highways for 1968 and 1990 from the Colorado Classification,
Needs, and Fiscal Study. Based upon those data (summarized in Appendix
H), a linear interpolation was performed to develop the growth factors in
Table J-8. Emissions from 1975 (Tables J-6 or J-7) were then multiplied
by these factors to obtain future VMT.
Agriculture - This source category was assumed to remain constant. No
data were available for projecting any change in the amount of land in
agricultural use.
J-10
-------
Table J-8. GROWTH FACTORS FOR SAND ON PAVED ROADS
County
Adams
Arapahoe
Boulder
Clear Creek
Denver
Douglas
Gilpin
Jefferson
Larimer
Weld
Average annual VMTa
growth rate, percent
5.4
2.8
5.9
6.3
5.6
4.9
3.5
6.3
4.7
4.4
Ratio of future VMT to
1975 VMT* (growth factor)
1980
1.20
1.12
1.21
1.22
1.20
1.18
1.14
1.22
1.18
1.17
1985
1.39
1.23
1.42
1.44
1.40
1.36
1.28
1.44
1.36
1.34
Vehicle-miles of travel, from reference 4.
Land Development, Residential and Commercial Construction - Emissions
from both these sources were assumed to be proportional to the fore-
casted rate at which land would be converted to other uses, where such
data were available. In other cases, population and employment pro-
jections were used. Each case will be described separately.
Counties in the JRPP area - Forecasts were provided by the Denver
Regional Council of Governments (DRCOG) of future land use in the Joint
Regional Planning Program (JRPP) area. Data aggregated by county were
used, to be consistent with the other fugitive dust computations. For
each county, "total used land" was reported for 1970, 1980, 1990, and
2000. The amount of land forecasted to be converted to use (i.e., the
difference between two years1 total used land) was the parameter used
to describe the rate of construction activity. For Denver County, which
is wholly in the area for which socioeconomic forecasts were done in
the JRPP planning process, this parameter was used directly. For the
J-ll
-------
other JRPP counties, population projections were examined in order to
determine the portion of forecasted population increase (and thus,
assumedly, development) which would occur in the JRPP area. The total
growth factor for the county was taken to be the product of the growth
factors for land use and population. This procedure, and resulting
growth factors, are presented in Tables J-9 and J-10.
Counties outside JRPP area - Remaining counties were analyzed on the
basis of the area source growth factors developed in Appendix H for
other particulates.
Highway Construction - Emissions growth factors for this source were
calculated in a manner exactly analogous to those for development and
construction. The DRCOG land use forecasts for the JRPP area include
a category for land used for roadways, and this statistic was used to
develop growth factors for emissions from highway construction in the
JRPP portion of each county. The same population factor as was used
for construction and development was used to adjust for the expected
amount of growth (and thus, assumedly, highway construction) in the
whole county. For counties outside the JRPP area, the particulates
area source growth factors from Appendix H were also used for highway
construction. The resulting growth factors for fugitive dust from
highway construction are shown in Tables J-ll and J-12.
Quarrying, Mining, and Tailings; Aggregate Storage; Cattle Feedlots -
These source categories were judged to be unlikely to change markedly,
and no data were available to provide a basis for projections. It was
therefore assumed that emissions would not change over time.
Total Effect
Tables J-13 through J-16 show the predicted future emissions of fugitive
dust from the procedures described above.
J-12
-------
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-------
APPENDIX J REFERENCES
1. PEDCo-Environmental Specialists, Inc. Investigation of Fugitive
Dust -- Sources, Emissions, and Control -- for Attainment of
Secondary Ambient Air Quality Standards/Colorado. U.S. Environmental
Protection Agency, Office of Air Quality Planning and Standards,
Research Triangle Park, N.C.
2. Telephone conversation on 25 June 1974 with Mr. Robert Amick,
PEDCO-Environmental Specialists, Inc., Cincinnati.
3. Colorado Land Use Commission. Colorado Land Use Map Folio. Colorado
Land Use Commission, Denver, Colorado, January 1974.
4. Wilbur Smith and Associates. Highway Classification, Needs, and
Fiscal Study/Colorado/1970-1990. Colorado Department of Highways,
Denver, Colorado, August 1972.
J-21
-------
APPENDIX K
DETAILS OF THE CLIMATOLOGICAL DISPERSION MODEL (COM)
AND THE HANNA-GIFFORD MODEL
CLIMATOLOGICAL DISPERSION MODEL
The Climatological Dispersion Model (COM) calculates ground level air
concentrations of up to as many as two pollutants emitted from both point
and area sources. Much of the following discussion closely parallels that
given in EPA publication number R4-73-024, "User's Guide for the Climato-
logical Dispersion Model." The source input for this model includes area
source strengths in gm/sec for a grid square of known size and effective
height of the emissions above the ground. For point sources the emission
rate in gm/sec is also required but the effective source height is cal-
culated in terms of stack height, diameter, gas exit velocity, and tem-
perature (for both the stack gas and the ambient air).
The basic meteorological input to the model takes the form of a joint fre-
quency function (k, &, m) which contains 576 entries giving the joint
frequency of occurence of a wind direction, k, wind speed class, £, and a
stability index, m. The model requires 16 wind directions, 6 wind speed
classes, and 6 stability classes. A tabulation by punched cards of this
frequency distribution can be obtained for various localities in the United
States from the National Climatic Center (NCC) in Asheville, North Carolina.
The wind speeds associated with each wind speed class are given in
Table K-l. The remaining meteorological input parameters are the average
afternoon and nocturnal mixing height in meters. These can be obtained
from EPA publication number AP-101, "Mixing Heights, Wind Speeds, and
K-l
-------
Table K-l. CENTRAL WIND SPEEDS
Wind speed
class
1
2
3
4
5
6
Speed interval, knots
0 to 3
4 to 6
7 to 10
11 to 16
17 to 21
> 21
Class wind speed, m/sec
1.50
2.46
4.47
6.93
9.61
12.52
K-2
-------
Potential for Urban Air Pollution Throughout the Contiguous United
States." ^ The values chosen for Denver were 2543 meters and 268 meters,
respectively. The wind speeds given in Table K-l are assumed to be taken
at the 10 meter level. To account for the increase in wind speed with
height, the following power law profile is assumed:
U(z) = Ug (z/2())P (K-l)
where U(z) = wind speed (m/sec) at a height z
Ug = wind speed (m/sec) at reference height of z = 10 meters
p = exponent.
The variation of the exponent P with stability class is given in
Table K-2.
The variation of the vertical dispersion function o (p) with distance from
Z
the source (p) for a particular stability class is also given in terms of a
power law expression.
(p) = apb (K-2)
Values of a and b for different stability classes and distance ranges is
given in Table K-3. The physical basis for this expression for the dis-
persion parameter may be understood in terms of the definition of a :
(K-3)
'-j V *->
where U = wind speed (m/sec)
2
K = coefficient of turbulent diffusion (m /sec).
Z
K-3
-------
Table K-2. EXPONENTS FOR WIND PROFILE
Stability class
1
2
3
4
5
6
Exponent ( p)
0.1
0.15
0.20
0.25
0.25
0.30
K-4
-------
Table K-3. PARAMETRIC VALUES FOR a (p)
z
Stability
class
1
2
3
4
5
6
Distance, meters
100 to 500
a
0.0383
0.1393
0.1120
0.0856
0.0818
0.0545
b
1.2812
0.9467
0.9100
0.8650
0.8155
0.8124
500 to 5000
a
0.2539 x 10-3
0.4936 x 10-1
0.1014
0.2591
0.2527
0.2017
b
2.0886
1.1137
0.9260
0.6869
0.6341
0.6020
5000 to 50,000
a
_
-
0.1154
0.7368
1.2969
1.5763
b
_
-
0.9109
0.5642
0.4421
0.3606
K-5
-------
If the process of pollutant dispersal was one of simple diffusion the K
Z
would be constant and b would be equal to 0.5. Since this is not the case,
a different set of power law parameters is required for each range of
distances.
The orientations and distances of the point and areas sources with respect
to the receptors of interest what angular sectors and radial distances are
computed from source and receptor coordinates. The area sources must be
broken down into smaller area elements for interpretation. The actual
calculation process for all sources and pollutants is summarized by the
following set of formulas taken from reference 1.
The average concentration C. due to area sources at a particular receptor
is given by
C
'A
OO
.« f
2* J
16 66
k=l
qv(p) iL Zi (k,^,m) = joint frequency function
S (p,z;U ,P ) = dispersion function defined in Equations (K-4) &(K-5)
Ju HI
z = height of receptor above ground level
U = representative wind speed
X/
P = Pasquill stability category.
m
K-6
-------
For point sources, the average concentration C due to n point sources is
given by
*(k ,^,m) G S(p ,z;lL,P )
n * n Hn ' I m
n =
m=l
n
(K-5)
where k = wind sector appropriate to the nth point source
G = emission rate of the n point source
p = distance from the receptor to the n point source.
If the receptor is presumed to be at ground level, that is, z = 0, then the
functional form of S(p,z;lL,P ) will be
2*
exp
h
Ll/2
(K-6)
if a (p) < 0.8
(K-7)
if a (p) > 0.8L. New terms in Equations (K-6) and (K-7) are defined as
Z
follows:
o (p)
h =
L =
I ,
vertical dispersion function; i.e., the standard deviation
of the pollution concentration in the vertical plane
effective stack height of source distribution; i.e., the
average height of area source emissions in the kth wind
direction sector at radial distance p from the receptor
the afternoon mixing height
assumed half life of pollutant, hours.
K-7
-------
The effective stack height h is the sum of the actual stack height h
and the increment in source height A h, which is given by
-1
Ah=1.6F'u p' p < 3.5X* (K-8)
-1
Ah = 1.6F ' U (3.5X*r p > 3.5X* (K-9)
C /Q
where X* = 14F ' if F < 55
2/5
X* = 34F ' if F > 55
Ah = plume rise, meters
F = gV R 2 ["(T - T )/T 1
s s [/ s a sj
f\
g = acceleration due to gravity, m/sec
V = average exit velocity of gases of plume, m/sec
S
R = inner radius of stack, meters
T = average temperature of gases in plume, K
5
T = ambient air temperature, K
a
U = wind speed at stack height, m/sec
p = distance from source to receptor, meters
HANNA-GIFFORD MODEL
The numerical integrations required by the CDM for analysis of area source
contributors require large amounts of computer time and are really not
justified by the degree of accuracy employed in the original area source
emissions allocation procedure. For a simpler and more direct treatment of
3
area source emissions the Hanna-Gif ford area source model was chosen.
The model is based upon the integral of gaussian plume contributions from
upwind area sources. The ground level air pollutant concentration (X ) is
then given by
K-8
-------
X
oo y2
Qa(x,y)
dx/ — exp
o -
2a
dy
(K-10)
where X = surface concentration 0-ig/m )
Q = area source strength (p. g/
a
U = wind speed (m/sec)
a ,a = plume dispersion function (m)
x = distance upwind from the source (m)
y = crosswind distance from the plume centerline (m)
With this assumption that the plumes are narrow (i.e., y1 and y approach
oo) and that Q (x) is a function of x only, equation (K-10) becomes
3.
D
X = I I - ~- dx
(K-ll)
0
where D = limit of integration (m) for which further contributions is
negligible.
To integrate equation (K-ll) in closed form the vertical dispersion a is
z
again expressed in terms of the power law:
a = ax
z
(K-12)
If the integration distance is broken down into elements of length A x,
the following expression is obtained:
X =
- b
a(l - b) U
N
"o + Z
i = 1
(K-13)
K-9
-------
where X = concentration at the center of the receptor square
(i = 0) (ng/m3)
2
Q. = area source strength for upwind square (i) ([ig/m /sec).
In many cases the concentration contribution from neighboring square can be
neglected so that equation (K-13) becomes simply
- b
- b)U Q0
K-10
-------
APPENDIX K REFERENCES
1. Busse, A. D. and Zimmerman, J. R. User's Guide for the Climatological
Dispersion Model. EPA-R-4-73-024, December 1973.
2. Holzworth, G. C. Mixing Heights, Wind Speeds, and Potential for
Urban Air Pollution Throughout the Contiguous United States.
Environmental Protection Agency, Office of Air Programs, Research
Triangle Park, North Carolina, Office of Air Programs, Publication
No. AP-101, January 1972.
3. Hanna, S. R. A Simple Method of Calculating Dispersion From Urban
Area Sources. J. Air Poll. Contr. Assoc., ^1:774-777, 1971.
K-ll
-------
APPENDIX L
PROCEDURES FOR CALCULATION OF PROJECTED EMISSION DENSITIES FOR THE
DENVER METROPOLITAN GRID AND FOR THE CITIES OF BOULDER,
FT. COLLINS, AND GREELEY
Following the procedure outlined by Kircher and Armstrong, the calcula-
tion of carbon monoxide, hydrocarbon, and nitrogen oxide emissions from
light and heavy duty vehicle exhaust is given by the following summation:
n + 1
e = , c . d . m.
np i s= n - 12 lp lpn i
where e = emission factor in grams per vehicle mile for calendar year
n and pollutant p
c. = emission rate for pollutant p (grams /mile) for the ifch model
year at low mileage at a speed of 19.6 mi/hr. A list of
these values used for Denver is given in Tables L-l(a) and (b)
d. = emission deterioration factor for the i*-^1 model year, calendar
year n, and pollutant p. These deterioration factors for CO,
HC, and NOX are presented in Tables L-2(a) , (b) , and (c) .
m. = weighted annual travel of the i^ model year during calendar
year n. Table L-3 gives weighted annual travel for light and
heavy duty vehicles for the Denver area
s = speed adjustment factor for pollutant p and calendar year n.
s is evaluated in turn by the following expression:
s = Z-, r . v.
nj ji
L-l
-------
where k = total number of speeds
r = fraction of total vehicle miles traveled (VMT) for speed j
•^ during year n
' ,n = speed correction factor for speed j and pollutant p. Fig-
ures L-l(a), (b), and (c) show how tl
vary with speed for CO, HC, and NOX.
ures L-l(a), (b), and (c) show how these correction factors
Evaporative and crankcase emissions can be evaluated as follows:
n + 1
f = 2.^ h. m.
n -10 i in
i = n - 12
where f = combined evaporative and crankcase hydrocarbon emission factor
n
for calendar year n
h. = combined evaporative and crankcase emission rate for the it'1
model year. These emission rates are listed in Table L-4.
m. = weighted annual travel of the i1-*1 model year during calendar
year n.
To calculate actual emissions the factor eno must be multiplied by the
number of vehicle miles traveled (VMT) during a given time period. Aver-
age daily values of VMT for 240 grid squares (2 miles on a side) in the
Denver Metropolitan Area were furnished by the Colorado Division of High-
ways. A map of the Denver Metropolitan Area showing the VMT grid centers
is given in Figure L-2. These data, which were broken down according to
road classification, were for the year 1972 with projected values given for
the year 2000. The various road classifications and associated average
speeds are given in Table L-5.
The spatial distribution of average daily values of VMT according to road
type for the 240 grid squares are shown in Tables L-6(a) through (p) for
the years 1972 and 2000. These data were then interpolated linearly to
find VMT's for 1975, 1980, and 1985. Emissions of CO, HC, and NOX were
then calculated for each of these three years by use of the Kircher-
Armstrong technique discussed previously. The results are given in
Tables L-7(a) through (i). The breakdown of total VMT by light duty
L-2
-------
vehicle (LDV), heavy duty vehicle (HDV) and diesel is 94.7%, 5%, and 0.3%,
respectively.
Emission densities of CO, HC, and NOX for the cities of Boulder,
Ft. Collins, and Greeley were based upon functional-system annual travel
by urban area for 1968 and 1990 listed in the Colorado Classification,
Needs, and Fiscal Study. In Tables L-8(a) and (b) annual VMT for these
three cities is given as a function of road classification for 1968 and
1990. After conversion to daily traffic flows the VMT data was inter-
polated to find daily traffic volumes for 1975, 1980, and 1985. The
speeds used in the emission calculations for these cities are given in
Table L-9.
L-3
-------
1.5
1.0
Of.
O
u
O
i—
u
UJ
Q£
QC
O
P 0.5
15 30
AVERAGE SPEED, mph
60
Figure L-l(a).
Average speed correction factor for all model years,
carbon monoxide
L-4
-------
1.5
1.0
u
z
O
I—
u
LU
Of
oc
O
U
£ 0.5
UJ
a.
15 30
AVERAGE SPEED, mph
45
60
Figure L-l(b). Average speed correction factor for all model years,
hydrocarbons
L-5
-------
2.0
1.5
u
z
o
u
1 i.°
o
o.
10
0.5
15 30
AVERAGE SPEED,mph
45
60
Figure L-l(c)
Average speed correction factor for all model years,
nitrogen oxides
L-6
-------
DENVER METROPOLITAN AREA
STATE HIGHWAY DEVELOPMENT PLAN
Figure L-2. Map of the Denver Metropolitan Area showing VMT grid centers.
L-7
-------
Table L-l(a). LIGHT-DUTY VEHICLE EXHAUST EMISSION FACTORS FOR
HIGH-ALTITUDE CITIES (c^ )
Model year
Pre-1968
1968
1969
1970
1971
1972
1973-1974
1975
1976
1977
1978-1980
1981 and later
Exhaust emission factors at low mileage
Carbon
monoxide
g/mi
130
74
48
72
75
42
42
20
20
12.5
1.8
1.8
g/km
81
46
30
45
47
26
26
12
12
7.8
1.1
1.1
Hydrocarbons
g/mi
10
6.0
5.4
6.1
5.3
4.9
4.9
1.8
1.8
1.3
0.23
0.23
g/km
6.2
3.7
3.4
3.8
3.3
3.0
3.0
1.1
1.1
0.81
0.14
0.14
Nitrogen
oxides
g/mi
1.9
2.2
2.6
2.8
3.1
3.1
1.4
1.4
1.3
1.3
1.3
0.31
g/km
1.2
1.4
1.6
1.7
1.9
1.9
0.87
1.1
0.81
0.81
0.81
0.19
L-8
-------
Table L-l(b). HEAVY-DUTY GASOLINE-POWERED VEHICLE EXHAUST EMISSION
FACTORS FOR HIGH-ALTITUDE AREAS (c^ )
Model year
Pre-1970
1970 through 1973
1974 and later
Carbon
monoxide
g/mi
210
190
190
g/km
130
120
120
Exhaust
hydrocarbons
g/mi
19
18
15
g/km
12
11
9.3
Nitrogen
oxide
g/mi
5.0
4.9
4.9
g/km
3.1
3.0
3.0
L-9
-------
Table L-2(a).
CARBON MONOXIDE DETERIORATION FACTORS FOR LIGHT-DUTY
GASOLINE-POWERED VEHICLES IN ALL AREAS EXCEPT
CALIFORNIA (d. )
v iprr
Model year
1967 and earlier
1968
1969
1970 through 1974
1975 through 1977
1978 and later
Vehicle age, years
1
1.00
1.24
1.42
1.18
1.04
1.16
2
1.00
1.35
1.53
1.32
1.30
1.34
3
1.00
1.41
1.59
1.38
1.36
1.50
4
1.00
1.47
1.63
1.40
1.43
1.62
5
1.00
1.53
1.68
1.44
1.44
1.75
6
1.00
1.58
1.71
1.47
1.49
1.88
7
1.00
1.63
1.75
1.50
1.56
2.00
8
1.00
1.67
1.79
1.51
1.63
2.10
9 and
older
1.00
1.72
1.82
1.56
1.69
2.22
L-10
-------
Table L-2(b).
EXHAUST HYDROCARBON DETERIORATION FACTORS FOR LIGHT-
DUTY GASOLINE-POWERED VEHICLES IN ALL AREAS EXCEPT
CALIFORNIA (d. )
ipn
Model year
1967 and earlier
1968
1969
1970 through 1974
1975 through 1977
1978 and later
Vehicle age, years
1
1.00
1.12
1.10
1.05
1.00
1.14
2
1.00
1.18
1.16
1.10
1.13
1.30
3
1.00
1.21
1.18
1.13
1.22
1.44
4
1.00
1.23
1.21
1.15
1.29
1.55
5
1.00
1.26
1.23
1.17
1.37
1.67
6
1.00
1.28
1.25
1.20
1.43
1.77
7
1.00
1.30
1.28
1.22
1.50
1.88
8
1.00
1.32
1.29
1.24
1.56
1.96
9 and
older
1.00
1.35
1.31
1.26
1.63
2.07
L-ll
-------
Table L-2(c). NITROGEN OXIDE DETERIORATION FACTORS FOR LIGHT-DUTY
GASOLINE-POWERED VEHICLES IN ALL AREAS EXCEPT
CALIFORNIA (d. )
ipn
Model year
1972 and earlier
1973 through 1974
1975
1976
1977 and later
Vehicle age, years
1
1.00
1.11
1.00
1.03
1.17
2
1.00
1.18
1.18
1.07
1.37
3
1.00
1.20
1.23
1.10
1.53
4
1.00
1.21
1.23
1.13
1.67
5
1.00
1.22
1.41
1.17
1.82
6
1.00
1.23
1.45
1.19
1.94
7
1.00
1.24
1.45
1.21
2.06
8
1.00
1.25
1.45
1.24
2.17
9 and
older
1.00
1.26
1.45
1.26
2.32
L-12
-------
Table L-3. WEIGHTED ANNUAL TRAVEL FOR LIGHT (LDV) AND
HEAVY (HDV) DUTY VEHICLES
Vehicle age (years)
0
1
2
3
4
5
6
7
8
9
10
11
12
13 +
Weighted annual travel
LDV
0.013
0.075
0.123
0.122
0.101
0.091
0.092
0.089
0.074
0.059
0.052
0.025
0.026
0.061
HDV
0.003
0.095
0.164
0.121
0.114
0.097
0.088
0.064
0.054
0.036
0.028
0.018
0.015
0.103
L-13
-------
Table L-4. LIGHT-DUTY AND HEAVY-DUTY VEHICLE CRANKCASE AND
EVAPORATIVE HYDROCARBON EMISSIONS FOR ALL AREAS
EXCEPT CALIFORNIA
Model year
Pre-1963
1963 through 1967
1968 through 1970
1971
1972
1973 and later
LDV hydrocarbons
g/mi
7.1
3.8
3.0
0.5
0.2
0.2
g/km
4.4
2.4
1.9
0.3
0.1
0.1
HDV hydrocarbons
g/mi
8.2
8.2
3.0
3.0
3.0
3.0
g/km
5.1
5.1
1.9
1.9
1.9
1.9
L-14
-------
Table L-5. ROAD CLASSIFICATION AND SPEEDS
FOR DENVER METROPOLITAN AREA
Classification
Speed (mi/hr)
Freeway
Expressway
Primary arterial
Minor arterial
Collector
Centroid connector
Ramps
Major arterial
40
34
26
23
21
20
20
23
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r-i co
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Table L-8(a). FUNCTIONAL-SYSTEM ANNUAL TRAVEL BY URBAN AREA
(IN MILLIONS OF VEHICLE MILES) - 1968
Boulder
Ft. Collins
Greeley
Freeway and
expressway
34.68
0
18.77
Principal
arterial
55.94
60.18
27.40
Minor
arterial
39.31
28.94
39.39
Collector
10.98
8.21
9.79
Local
12.43
10.92
11.26
L-41
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Table L-8(b). FUNCTIONAL-SYSTEM ANNUAL TRAVEL BY URBAN AREA
(IN MILLIONS OF VEHICLE MILES) - 1990
Boulder
Ft. Collins
Greeley
Freeway and
expressway
70.73
5.00
41.04
Principal
arterial
101.28
100.63
56.36
Minor
arterial
104.42
63.07
71.11
Collector
29.85
19.69
17.17
Local
43.05
15.90
23.84
L-42
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Table L-9. ROAD CLASSIFICATION AND SPEEDS
FOR BOULDER, FT. COLLINS, AND
GREELEY
Classification
Speed (mi/hr)
Freeway and expressway
Principal arterial
Minor arterial
Collector
Local
34
26
23
21
20
L-43
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TECHNICAL REPORT DATA
(Please read Instructions on the reverse bcjore completing)
1 REPORT NO
EPA-450/3-74-053 _
4 TITLE AND SUBTITLE
DEVELOPMENT OF AN EXAMPLE 10-YEAR AIR QUALITY
MAINTENANCE PLAN FOR THE DENVER AQMSA
6. PERFORMING ORGANIZATION CODE
3. RECIPIENT'S ACCESSIOP*NO
5. REPORT DATE
September 1974
7 AUTHOR(S)
Dr. Frank A. Record, David A. Bryant, Gordon L.
Deane, Benjamin Kincannon, and Dr. Michael T. Mills
8. PERFORMING ORGANIZATION REPORT NO
GCA-TR-74-13-G
9 PERFORMING ORGANIZATION NAME AND ADDRESS
GCA CORPORATION
GCA/Technology Division
Burlington Road
Bedford, Massachusetts 01730
10. PROGRAM ELEMENT NO.
11. CONTRACT/GRANT NO.
68-02-1376
12 SPONSORING AGENCY NAME AND ADDRESS
U.S. Environmental Protection Agency
Office of Air and Waste Management
Office of Air Quality Planning and Standards
Research Triangle Park, North Carolina 27711
13. TYPE OF REPORT AND PERIOD COVERED
Final
14. SPONSORING AGENCY CODE
15. SUPPLEMENTARY NOTES
16. ABSTRACT
This report presents an example plan for the attainment and maintenance of air
quality standards in the Denver Front Range Air Quality Maintenance Study Area.
This is one of four such demonstration maintenance plans prepared as part of the
development and testing of guidelines for air quality maintenance planning. The
study area includes Denver, Colorado, and nine nearby counties; the planning
period is 1974 to 1985. Pollutants for which analysis and planning were done
include carbon monoxide, oxides of nitrogen, photochemical oxidants, and total
suspended particulates. Separate strategies are recommended for short-term (at-
tainment) and long-term (maintenance) aspects. Maintenance strategies were based
upon and coordinated with on-going comprehensive regional planning for the Denver
region. The report discusses the study area characteristics, emission allocation
and projection methods, air quality data and forecasts, and strategy selection;
and includes background information on emissions, regulations, and detailed cal-
culation techniques.
17.
KEY WORDS AND DOCUMENT ANALYSIS
DESCRIPTORS
b.IDENTIFIERS/OPEN ENDEDTERMS
c. COSATI Field/Group
Regional Planning
Urban Planning
Air Pollution
Land Use
Planning and Zoning
Air Pollution Control Agencies
Transportation
Air Quality Maintenance
Plans
Air Quality Maintenance
Measures
Land Use Controls for Air
Quality Maintenance
Regional Planning for Air
Pollution Control
13-B
18. DISTRIBUTION STATEMENT
Unlimited
19. SECURITY CLASS (This Report)
UNCLASSIFIED
21. NO. OF PAGES
642
20. SECURITY CLASS (This page)
UNCLASSIFIED
22. PRICE
EPA Form 2220-1 (9-73)
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