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]

-------
                                  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

-------
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

-------
                        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

-------
                          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

-------
                              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

-------
                        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

-------
                       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

-------
                       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

-------
                               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

-------
                       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

-------
                       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

-------
                       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

-------
                               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

-------
                         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

-------
                         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

-------
                       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

-------
                   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

-------
                   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

-------
                   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

-------
                  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

-------
                          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.

-------
     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

-------
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

-------
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

-------
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
                               xxv

-------
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
                               xxvi

-------
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
                                xxv 11

-------
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.
                              xxviii

-------
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
                               xxix

-------
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.
                                 xxx

-------
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.
                                xxxi

-------
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
                                xxxii

-------
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.
                              XXXLll

-------
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
                               xxxiv

-------
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:
                                XXXV

-------
     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
                                xxxv i

-------
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
                               xxxv11

-------
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

                                xxxviii

-------
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
                               XXXIX

-------
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.
                               xxxx

-------
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.
                                XXXXL

-------
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.
                               XXXXLl

-------
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.
                               XXXXlll

-------
                             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

-------
(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.

-------
    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

-------
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

-------
                                  l<
                                                   15
 II-
10
                                 It
                                 IE

                         ^.v
•^

^^
-r
UJ
I
O
<
_j
O
5,
< 1 	
s/\
V/3
UJ
5
i^ — i ^.
a r

                                                            cc;
                                                            UJ
                                                            CC!
                                                            O
                                                            O
                                                            Oi
                                                            u-l
                                                            J
                           10

-------
r
                                                                                                                       S-I
                                                                                                                       01
                                                                                                                       0)
                                                                                                                      fi

                                                                                                                       d
                                                                                                                       CD
                                                                                                                       o
                                                                                                                       8-
                                                                                                                       tn
                                                                                                                       o
                                                                                                                      •H
                                                                                                                       4-1
                                                                                                                       en
                                                                                                                      •r-i
                                                                                                                       W
                                                                                                                       01
                                                                                                                       4-1
                                                                                                                       O
                                                                                                                       TO
                                                                                                                       4J
                                                                                                                        CO
                                                                                                                       CO
                                                                                                                       CM

                                                                                                                        0)
                                                                                                                        3
                                                                                                                        Ml
                                  11

-------
r       -.
\    \   {  *'^\l
                                             CO
                                             
-------
13

-------
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

-------
 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

-------
s~\
CO
0
r-l
^3
M
hJ
:=>
53

U
f\
«
§
pq
erf
i
3
IS
H
§
§
F*H
N~^

O
rH
O
U
f\
erf
W
Q
erf
o
o2
CO
3
a
0
s
o
H
O
t-l
CU
, — 1
XI
cfl
H






O
co
cfl
O
Xi
d
cu
60
cfl
1









CO
cu
3
4J
cfl
M
CU
I"
-,
CU cfl
3 13
d
•H
s
CO
S
d
•1-1
S
1


0^0~0^^tSocM^c^ •
ininvo^>t-.r-r-vOv£>m
r-i r-i m

^
ZSIZZZZZZZZI S
CMin<)-CMOO
CM CO i— 1 CMCO-d"~. 4-1 l-l
4J s~^
Cfl CO
*o ^
cu -a
60 ^

> ••-"

CM CU
0)
CO M'l


cu cu
N CU
CU r4
CU 4-1
4-1 CU
60
""O cO
13 CU
o 
cfl 5
rJ 5
4J
CO
cfl ••
.. cu
cu cu
N r4
(U
4-1 CU
4-1 M
CO O
Cfl 0
r-l CU
4-1
0 4-1
CU CU
cfl i— 1
cfl
• CU W
x: So
O cfl •»
r1 Li of-
•i-l CU i—4
CN 
-------
    JAN
FEE
 MAR
    APR
MAY
JUNE
  JULY
AUG
SEPT
    OCT
NOV
DEC
                                               LEGEND
                                                 WIND ROSES SHOW PERCENTAGE
                                                 OF TIME WIND BLEW FROM THE
                                                 16 COMPASS POINTS OH WAS CALM

                                                 « INDICATES LESS THAN 0 5% CALM

                                                   25 HOURLY PERCENTAGE* 25
                                                   I i  , ,
                                                          ^^^•CAI.M
Figure  5.    Monthly wind roses for Denver,  Colorado
                            17

-------
   3800


   3600

   3400


   3200


   3000

   2800

   2600


   2400


^  2200
4>
?  2000
x
§
x
<
LJ
1800

1600


1400

1200

1000

 800

 600

 400

 200

   0
                                MORNING
                  M
                      M
                          MONTH
N   D
Figure 6.
     Monthly mean mixing heights at Denver, Colorado
     based on an 8-year period
                          18

-------
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

-------
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

-------
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

-------
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

-------
    0.10
E
Q.
Q.
<

CC
UJ
o
z
o
o
                               8
     (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

-------
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

-------
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

-------
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

-------
 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

-------
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

-------
                 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

-------
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

-------
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

-------
          •  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

-------
     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

-------
           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

-------
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

-------
                           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

-------
 CO
H
e
•
a

o
o
• •
M>
I
6
•
CO

O
O
• *
O
I-l

e
0
•i-l
4J
CO
3

O
CJ
CO





a>

o
a

3
H


T3
r-l CJ
CO 3
4-1 O
O &
H 4J
3
O
4-1
•H
O
CO
a,
CO
O
4-1
O
6-2

^
a>
,J2
§
z
O to
0)
J-l O
CD CO
r\ p.
JT

bO
£
•r-l
^
Jj
CO
FM

M-4
O


0)
^
-U
U3
1
"-M
<4_|
o

0)
4-1
CO
^
•r-l
J_j
PM


o>
Q*\
•
0





0
F-%.
vD
»\
o
CM



OO

in
OO




OO
as
00
rC
i— i

in
OO
»i
0
CM

0)
0)
^1
4-1
CO
1
14-1
M-l
O

o
•t-l
r-l
r~i
3
PM


O
CO
•
in





0
o
00

i^O
! 	 1



CTv
•
CN
00




in
CM
^
CM

OO
vO
T-t
f
CO














^
J^
3
o


o
in
.
i— i





0
o
o

CO
>^J-



tn
•
>j-
OO




CO
o
CM
^
CM
a\
CM
VD
•X
00
CM












r-l
CO
4-1
O
H
                                                                     4J
                                                                     O
                                                                          0)
                                                                         ,0
                                                                          Cfl
                                                                       -  c
                                                                       •   03

                                                                      C3  H
                                                                     4J  M-l
                                                                     CD   O
                                                                       •   Ci
                                                                      CJ   O
                                                                       «  ClJ
                                                                     4J
                                                                     •i-l
    0)
^ J2
3  4-1
                                                                      O   n)
                                                                      H   O,
                                                                      3   (1)
                                                                      O   ^4
                                                                         39

-------
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

-------
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

-------
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

-------
                                                                               M
                                                                               0)
                                                                               0)
                                                                               Q

                                                                               C
                                                                               CO
                                                                               4-1
                                                                               •i-(
                                                                               j—I
                                                                               O
                                                                              O
                                                                              OO
                                                                                I
                                                                              O
                                                                              O
                                                                              ON
                                                                               c
                                                                               O
                                                                              •1-1
                                                                               3
                                                                               O.
                                                                               O
                                                                               CO
                                                                               C
                                                                               o
                                                                               •^
                                                                               00
                                                                               0)
                                                                               S-l
                                                                               en
                                                                               a)
                                                                               M
                                                                               CO
                                                                               X!
                                                                               03
                                                                               §
                                                                               O
                                                                               o
                                                                              c-O
                                                                               0)
                                                                               5-1
43

-------

                                                                                CO
                                                                                01
                                                                                t-i
                                                                                ti
                                                                                CO
                                                                                O
                                                                                8-
                                                                                i-l
                                                                         CD
                                                                         U
                                                                         •r-4
                                                                         14-1
                                                                          00
                                                                          a
                                                                         •H
                                                                          (U
                                                                         4-1
                                                                          CO
                                                                          CO
                                                                          s-l
                                                                          O
                                                                         ,-H
                                                                          O
                                                                         O
                                                                         'O
                                                                          a)

                                                                          §•
                                                                         I-l
                                                                          (U

                                                                          0)
                                                                         ID

                                                                          CO
                                                                          (U
                                                                          so
                                                                          •H
                                                                          fS
                                                                          O
                                                                           0)
                                                                           en
                                                                           CO
                                                                          PQ
 0)
Q

 Q)
J2
4-1

T3
 d
 CO

 O
"U
 CO
 ^
 O
I— I
 O
U

4-1
 O

 c
 O
•rl
 4-1
 CO
.-I


 I
 a.

ID
 0)
 4-1
 O
 OJ
 P4

 13

 CO

 4-1

 (U

 (U
  (U
  M
  3
  M
 •H
Ofn
   44

-------
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

-------
   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

-------
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

-------
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

-------
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

-------
                                                             01
                                                             en
                                                             r—
                                                             en
                                                                       C
                                                                       0)
                                                                       J-l
                                                                       O)
                                                                       §
                                                                      O
                                                                      •H
                                                                       O
                                                                       3
                                                                       O
                                                                       CD

                                                                       O
                                                                      •H
                                                                       t>0
                                                                       cu
                                                                      O
                                                                       0)

                                                              s       §
                                                              2       §
                                                             o
                                                             to
                                                             O1
                                                                               c
                                                                               O
                                                                              •H
                                                                               &0
                                                                               cu
                                                                               CU
                                                                              Q

                                                                               C
                                                                               CO
m   to   to
 O   0)  T3
     cu   d
 ^   >>  to
 CU   O   CO
                                                                               d
                                                                              •t-i
                                                                               3
                                                                               O
                                                                               &0
4J
U3
3
                                                                               fi

                                                                               8
 01
4J
 O
 0)
•I— I
 O
 M
                                                                               C!
                                                                               ca
                                                                               cu
                                                                               CA
                                                                               
-------
      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

-------
                                  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

-------
                                   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

-------
        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

-------
      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

-------
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

-------

                           ;,;.:::.;::".:l   *Source: Denver Regional Council
                           -"
-

'€=.
4

Sj
.
Iliiiiiiiii
>"
-------
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

-------
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

-------
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

-------








g































H
i-J
3
as

iPARTMI
0








































o
Q
Pi
cq
Cd H
"*^ '^^
CO P^




§
M
CO
O S
H D
. 1 . T
b b
CM pi
Pi Z
M O
<: o












^™

	












,_J J>-<
< &
r ~\ •<{*.
IECHNK
SECRET;


OLLUTION
NCE BOARD
P-I 





1
1
1
1
1
1
1
1
1
1
1
1
1
I





^
Pi
H
Q
0
§
H
i-4 13
cr> 2
M
Pi >
 Pi
M M
Q O




Pi
ABORAT
IVISI01
n3 fi

NISTRA-
SERVTCES
M pq
< H











...


§
M
CO
M
M
O

















1
M
l-J
CD
cx
M
<£

1
i— i
H
H
CO


MOBILE

S
o
H
b pi
^ 0
O
pi PQ
M <;

-------
o



pq
•3
H





























(U
r-l
•H
<"N
0
S


)>-,
4J
•r-l
r-l
CO
3
CT
H
•r-l
<
Jj
(0
c
0
•H
4-1
cO
4J
1
co
•H
c
.H
e

<


, 	 |
CO
4-1
O
H


r-l
Ol
JS
4-1
O
CS
O
•H
CO
CO
•1-t


O
O
J-i
O
4-1
cO
O
rd
co
CU
O
}-l
3
O
CO
(U
O
ti
CO
r-t
r-l
•r-l
CU
(-1
3
CO

co
CU
o
S-l
3
0
CO

CJ
O
•H
4J
cO
M
W

vO
VO
m
CO OO
r- o
r^





m
ON
CO CO
r-l -
OO
£j
•co-

ON
r-l
OO
CM ~
r-l ON
in
r-l
<0-
_.,.
in
CM
n
oo m
o
i — 1
<0-
cn
i— 1 CU
60 CU U
C r-l CJ -H
•HO) (3 >
<4-l > O V-l
m cu co cu
CO r-l r-l W
4J CU
CO PH
































































60
c
•H
4-1
cfl
l-l
CU

O
1^,
CN
CO
00
o
1— 1























o
0
CO
t\
in
CM

<0-











CNI
0
n
CO
CO











CO
CU
co
£j
CU
Cu
X
CU


r- 0
*^O ^O
0 00
<)• CM
vo in



o
O
>-£>
n
CO


<0-


K*^
r-< C3
r-l CO i-l
CJ 4-> 4-1
^ 'H 3
CO Cu O
M CO
H U
vO
CO
CO
^
CM
CM

<0-
0
in
^o
A
CM
CO
•C/V















vO
OO
^-O
n
r-i
ON
r-l
<0-



























r-l
to en
3 cu
4-1 O
0 -H
CO >
!-l rJ
4J 0)
C! co
O
CJ
O
in

00

r-l

£
r-l
00

•*
OO
m

oo

00
n
^J-
oo



o
CO
CO
CM

^D
CO
r-l
<0-




r-l
CO
4-1
O
H
                                             62

-------
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

-------
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

-------
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

-------
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

-------
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

-------
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

-------
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

-------
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.
                            70

-------
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:
                                 71

-------
      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
                                72

-------
     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
                                73

-------
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
                                74

-------
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
                                75

-------
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
                                76

-------
                   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
                                 77

-------
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
                                78

-------
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.
                                 79

-------
          (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
                                 80

-------
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
                                 81

-------
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,
                                82

-------
 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.
                                83

-------
         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
                                84

-------
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.

                                  85

-------
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:
                                 86

-------
     (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.
                                 87

-------
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).
                                 88

-------
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
                                 89

-------
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.

                                  90

-------
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.
                                 91

-------
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

-------
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

-------
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.

                                 94

-------
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

-------
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

-------
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

-------
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.
                                98

-------
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.
                                99

-------
                             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.
                               100

-------
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.
                               101

-------
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.
                                102

-------
                            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
                                 103

-------
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
                               104

-------
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
                               105

-------
BOUL
                                                      Legend:
                                                            County Line
                                                            JRPP super
                                                            district
                                                            boundaries
           Figure 21 .   Six  county JRPP area - by super districts
                                 106

-------
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
                               107

-------
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
                         108

-------
       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.
                                109

-------
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

-------
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

-------
   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

-------
                                                                                                      o
                                                                                                      oo
                                                                                                      •o
                                                                                                      o
                                                                                                      o
                                                                                                      o
                                                                                                      
-------
 I
o
"«*•
o
CM
O
o
o
oo
CO
 I
o
o
CO
                                                                                                        o
                                                                                                        oo
                                                                                                        «o
                                                                                                        o
                                                                                                        •o
                                                                                                        >o
                                                                                                        o
                                                                                                        CM
                                                                                                        •o
                                                                                                        o
                                                                                                        o
                                                                                                        o
                                                                                                        OO
                                                                                                        o
                                                                                                        CM
 I
o
•*»
CO
                                                                                                                             1
                                                                                                             O
                                                                                                             CO
                                                                                                             cO
                                                                                                             ,—I
                                                                                                             60
                                                                                                             3
                                                                                                             O

                                                                                                             O
                                                                                                                             I
                                                                                                                             p
                                                                                                                             0) CM
                                                                                                               .  g
                                                                                                              0)   4J
                                                                                                              O
                                                                                                             ^3   C
                                                                                                              CB  -H

                                                                                                              03   CO

                                                                                                              bl   fi
                                                                                                                CO
                                                                                                                              •H   M
                                                                                                                              4-1   CU
                                                                                                                              •H  4-1
                                                                                                                              M) m
                                                                                                                              3   0)
                                                                                                              ro
                                                                                                              CM

                                                                                                              0)
                                                                                                              J-l
                                                                                                              3
                                                                                                              to
O
CM
CO
                                                                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

-------
      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

-------
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

-------
                             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

-------
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

-------
                              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

-------
oo
•8
H














CO
•J-J
p3
Q
1
o
o















>i CO
S-i 13
CO S-i
13 cfl
SI
O Cfl
CU 4-J
CO CO
CO
>•> 13

CO CO
•r-l d
S-i cfl
PLI 4J
CO



60
c
•H
60 CU
CO B
S-J -H
0) 4-1
*3j



4-1
d
CO
4J
3
i-H
i-H
o












13
j_)
CO
13
d
cfl
4-1
CO

r-l
3


cfl

>,
S-i
cfl
13
d
o
o
CU
CO
cu
XI
H

en
B

60

o
*-O

en
a

60
=^-
iri


o
•H
S-i
4-1
g
o
O)
o

r-l
Cfl
d
d

cu
4-1
cfl
r-l
3
O
•H
4J

Cfl



60 1
d d
•H O
CO O
CO CU
CU CO
co
CO S-I
co 3
o
S-i X!
0 1
4H 
0) •
CO -i-l 13
•H XI S-i
O CO
/~** cO i3
•o d
a o co

60 CO
=L &

O Pn i-l
vD M cO
v— ' CO 13

en
en B *-s co X-N
B --- a cfl >>
--, 60 ex ^
60 ii. ex cu cfl
O u~i cfl -r-l
O O • CO S-4
in en o ^ ex
r-l i-l N-'
en en Ben B en /-NCO x-\
a a ex s ex aaaa
~ — ' — ex *" — ex — . ex — •- ex
60 60 60 60 ex 60 CX
~^~ O i—i cyi in
o o • in • o o en
vQ OO O ^O O r-l ^-^ -3" *— '
CM v_x m v_>

i
XI
4-J x-s
XI -H d Xi XI XI Xi
S-i S-i CO S-i S-i S-i S-i
/-N 3 
O 13
i-l "r-l
cu s-i d X
4-1 3 O O
4-14-1 XI d
cfl r-l S-i O

co u

1
d i
0) -H
W 8

< .-H
•r-l
B S
3 01
•H XI
•g U
co TD
n C
d co

a *•
N Cft
4J O
r-l H
Cfl
CO ~
x-x
CO CU
3 -r-l
O 4J
3 co
d -H
•r-l SJ
4-1 XI
d u
o ^-^
o
0)
O) 4J
XI -H
H

CO S-*
cfl >-i
S-i
0) cfl
CO -H
CO i-l
^ ex

en 7
B ex
--- ex
60
-^ Q
O •
o o
I-l V^

1
XI
•l-J X™ S
••-< d
M CO
<£ cu
~— B

t-1 O
Cfl -r-l
3 4-1
d cu
<3 e





d cu
CU 13
60 -H
0 X
S-i O
4-1 -r-l
•r-l 13
23



1
0)
i_,

CO


13
cu
co
O
ex
0
ij
ex

d
cu
0)


0)
>
cfl
X

0)
o
d
0)
o
ca
cu
d













































^
0)
*^j


.
13
0
rC
4J
B

W
i
1—3

CU
XI
4-1

S-i
o
M-l

CO
4-1
d
cu
B
OJ
o
CO
r-l
ex












































.
LO
f-^
^
t— 1

•
d
cfl
>-5
X
XI

d
0
ex
3
13
0)
13
•r-l
O
0)
13

0)
XI

O
j_i

§
PL,





















































•
/-N
0)
d
o
N
o
\^^

en
o

CO
CU
M
3
co
CO
01
e

^i
S
rT[
0)
XI
H

CO
cfl


S
CO
CO
V-X

en
^e

60
ii
O
vD
r-l



XI

3
O
XI
I
r-l



r-l
CO
O
•H
B
cu

o
o
4-1
0
x:
PM




































/-^
j>^
i-i
cd
•r-l
}_|
ex

9"

ex
00

•
o
v~x
















CO
4J
d
cfl
13
•H
X
o

60
d
•H
CO
•r-l
>
CU
13

O
4-1
CU
13
•H
3
60

CO
CO
•r-l

•0
S-i
cfl
13
d
cfl
4-1
CO

u
K

d co
CO X!
TJ
•H 4-1
X 0
o d

CU CO
X CU
4-1 O
cu
> 13
0) S-i
•r-l co
XI T3
O d
Cfl Cfl
4-1
O CO
4-1
C_>

—
PL, cu
M &
CO H


x-x
^,
J_(
frt
•iH
J_l
a*

^
a

.-4-
^J
•
O
'


s~*
e

CO

CJN

O
4-1

S

CU
d
CO
XI
4J
Q)

C-*
o
d




•
4J
CU
B

co


13
cfl
13
d
cO
4J
CO

4J
Cfl
t)
•H
X
o

CU

4-1

M-l
• rH

4J
^











































                                                                                                                                     o
                                                                                                                                     en
                                                                                                                                      d
                                                                                                                                      o

                                                                                                                                     13
                                                                                                                                      CU
                                                                                                                                     X
                                                                                                                                      CO
                                                                                                                                     •H
                                                                                                                                     i— I

                                                                                                                                     •§
                                                                                                                                      cx
                                                                                                                                      CU


                                                                                                                                      CO
                                                                                                                                     13
                                                                                                                                      o
                                                                                                                                     XI   •
                                                                                                                                      4-1 

                                                                                                                                     5  I

                                                                                                                                     4-1  (3
                                                                                                                                      O  O

                                                                                                                                      d o
                                                                                                                                      O  "
                                                                                                                                              cfl
                                                                                                                                              cu
 o  o   cu
 co  .      cu
 4-1 CIS   CU
•H PL,   o
r-1 O   X
 CO      01
 3 CM
         CU
                                                                                                                                           d
                                                                                                                                          •H
                                                                                                                                       cu r>  4
                                                                                                                                      XI C7N
                                                                                                                                      E-i ^
                                                                                                                                     CO      Xi
                                                               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

-------
§
u
o
w
CO

H
<

CO
H
M
Q

§
O
o

 OJ
 to
H
01
00
M x-s
0) -C
k-1
3 T3
0 C
£ CM

S
A
O
s?

C CO U
cfl 3 C
v q o
OB
O M
rJ
• co
O 0)
Sampler
height
c
o
•r-l
CO
a.
o
q
O
•l-l
4J
4J -H
•H M
C/l CJ
01
Location
County
00
o
•o
c
u
u
o
&
en
e
00
^^

I-M








1-1 r-. o> co
OO O O m
CM CM CM CM
r-~ 00 t-i o
rH
in -^ co
CM O O O
-tf ON f^ rH

es en en en
in o in in
rH CM en rH
CM , O V V
•i-l I I 1
333
C
0)
o
State Health Dept.
Hull Photo
Julian Street
Sloans Lake
Denver
SXssS

«M m m fo tn

-1
00 0 00 0

mmmmm
o o m en ON

^.^^

T3 1 1 1 1
1 .H -H *H -H
3
C C C C
01 01 Ol 0)
CJ CJ O CJ
0)
S g
00 00
•o *n >.
rH • r-l CO
4-t PQ W CQ 5
C 00 tJ
CO • -O • Cfl
rH B r-l B 0
< < CO
01 U CO U rH

en


CO
o
CM

en
2
CN
rH

U
1
•l-l
CJ
c
0)
Castle Rock
Douglas
en



o
•X)

CM
o

CM

o
1
s
c
0)
CJ
Blackhawk
c
•~t rH rH CN CM

1-H CM

O O O t-4 rH
.•^.x,

en en en en en
o o in in in
rH CM rH en rH
CO CO \O £> rH
r-l CM CM
en O co
rH

O O rH
ON CO O
sf r* co

en en en
in O -3-
en cn CM
O r- , >>
B) CJ CJ
rJ
ft c q*
0) 0)
u o
La Porte
Fort Collins
Love land
I
o o
CM CM

^

<*.*

O O
O CJ
>* ><
CJ CJ
c c
01 V
CJ CJ
q
0
i->
<4H
X =»
>-* rH
V
01 •
M u
O tu
0)
ON O O
CT> CM 00
CM CM CM
in CTi co
CM rH m
r- co O
CM O CM
CM m oo

m en en
CM rH CM

^l"!

B w
O CU
CJ Prf
C ,X X
1 1-i "r-(
Jl U CJ
3
q c
0) 
-------
                                                            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

-------
 0}
r-l


•3
H

41
O

O
;z
J_l
8
4-1
.
3
»-3
0)
e
3
*~J

1

O.
<



0)
b

Q
•-J
Location
X
4J
e
§
o
^- o oo 
o -* cr\ f~-
r-i 
co in
OO CM
CM
CO O
*t oo
CM
o ^o
m
N*
o r-
Boulder
Longmont
Boulder

o

0



o


o

o
CN
O

O



o

o

0
Idaho Springs
^

Ll
o
h
nj
J u~l PM CO O
o m m -^- -^- o ^-<
^•ocMor--inoom

CO O CM LTi ^D
o^oo^^ooooo
t-t r-l CM
oo o o>
ooooooooooo
r-l r-( r-t
i-t r-t MD O*>
OOOOOCTiOQO^D
CM f^
O O in r-i r^ co
omoococMr-^vo-3-
1-4 r* i— t i-H CO
moo foror-oOMsr-
i-« ro co c>j CM -*
O co o oo ^o in
^ooOi-ior^-Qor^-
co in ,
^: a* 5
p — •QJOflJtJ'-^
coX'-jwwcnowcM
V4
QJ
>
c

0

_,
r-^.


0

0
o

o

o

o

0

o
X
u
s
V
(-4
4J
CO
(0
o
Douglas

o

0



0


o

o
0

o

0

o

o
r-

1
.u
8
PQ
c
1-<
o>
r-l
•H
o
CO \O i-i OO <)•
in in i— i '•P sj-
CM CO SJ"
co * ^0
1-1
ro '-O oo
0 VD r^. in
rH r-l CO
r-l m ^- rH
sj CO CO
^ 00 O OO O
m rH in PH o

O CM \o o ro
oo ~d~ d" rH CM
O> .4- r- o> O1*
rH CM
O o in r-*-
O> O m CM rH
rH rH rH j
O CM
co CM
CM co
o m
CM rH
m o
ON CO
*-t CM
\£J rH
O CO

m ^o
r-. O
CM
CM >*
lA -4-
rH
OO CO
m oo
rH
\o in
r— CM
oo r^
>d- oo
I-* rH
^ CM
r- in
•-« CM
m uo
m co
v
rH
C
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

-------
servati
Occur
o
£3
O 0
4->
\-< co
3 M
0 4J
42 C
1 O)
00 0
0
u
0)
u
a a)
bservatic
Occurr
0
C3
O 0
U T-l
u
H CO
3 rJ
O 4-1
42 C
1 0)
.-1 U
o
u




M
o
EC
(U
4J
cc
Q

'i'
a
a

•5
60
e
M
3
o
rC
•<
Station
oo oo oo oo oo oo
OO OO OO 00 OO OO
vO ^O vO vO OO **O vO '•O **O **O ^O ^O
i-l i-l i-l r-l O I— 1 r-l i-l i-lt-l i-lr-l
ooc-j r*» r~. i— i i— i ON oo ON i— i i— i
r-l CM r-» i— 1 i— (CM CM CM i— 1 CM CN i— <
CM CM i— 1 i— 1 i— 4 i— 1 CM i— 1 i— 1 .— 1 CNCM
r-^i— 1 r— 1 rH i— < r— 1 i— 1 i— 1

i— 10 ,-iro n ro£) -cj-oo
roro . i— i i-i CMC^ i— i •— i
CMCM i-l i-l i— li— 1 CMCN i-l CM CMCM
CNCM i-4 i-l i-l i-l CMCM i— 1 i-l CMCM
i-l i-l i-l r-l i-l i-l r-4 i-l
S~~ \ /-** ^~\ /— \ /— S S~\ /— S S~^ S— \ S~** S~*i /— \
CTii— 1 r-l i-l CM i— 1 r-l CM CMi-H CMCM
Or-t OOi-l CMI^- i-IO <)-C^ 'OCM
\OLTl , ...
>->UO i— 1 60OU U
cflOJCl) 3 30)0) 0)
goo >-> 43 42
cootfl co a)oa) a)
t-)Oin '-J faspn fe
i— i CM cn ro ro co
r^ i^~ h-. r^. r~- r~.
CJ** C^ CT^ t^ O> ON
r-l i-l r-l i-l i— 1 i-l
a i •
CO T3
•H W >
1-1 td 1-1
3 <4-4 PQ
T> r-l OT
0 • C
(-(Du uo CJOLOOCfl
0) 0 ON • r-l O M T3
>cd O 4J • O O 3 «
CU CMcflWCJCMpJ>
<1J M
0 <
00 00
o o o o
30 \£> \O \D
O i-4 •— 1 i-l
i— 1 i-4 i— 1 i— 4
CM CM CM i— 1
CM CM CM CM
i— 1 i— 1 i— 1 i— 1

UO LO LO CTi
i— i r~~ vo vo
CM i-4 CM i-l

^o 1-4 co .
60 r-l
3 3
J 4-> (U
1-^ Cfl 43] OO 4J
in O i-i r-- en
SI
                                            156

-------
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

-------
CO

 a)
i—i
,£>
 CO
H












/-v
>,
ct>
T3
51
s^
CO
c
o
(0
en
i











•o
01
VI
So
o- d
(U O
ional r
reductl
1-1
T3
3




J3
CO
rategi
CO
s:
3





CO
a
0
•H
U
(U
0
s.
U
m
m
CO
M
4->
•s
t
S
iS



i-4
1— I
(0
s^


H
tO •-!
U i-l
H



y~\
X
i-H
§
§
^^






U
U
U
1-1
J3
o
>
X
w
•0
U
J=
00
3
rH
a
a



vehicles
6-S
>,
a
•o
DO
X
co

I-H
CO
g
•tf
r^.
J_>
o
PJ
*^D^roooooo
m o.-(cOcMooiAm
i-HONr-io\i— i-juicoo
COxO^LO-d-COCNlrHi-l
O 00 •-!
co o oino
vOl — r^oooOOOONOO
CO cO rO rO CO CO co co f^-cONd--oo*»f^"'(^tT*a\ONcytaNCjNc>c^cTiONOscr>ONa*ONa\ON




























CO
CU

•g

01

co
3
a-
en

01

CO
01
CQ

)H



U
CO
CU
U
CO
HI


O
0
CU
•o
U
CU
i-H
JO
•iH
CO
T3
§J
4J U
CO IH
IH cu
Q.
cu
H CM
3 •
i-H i-H
•H CM
CO
UH T3
a

0
in ^o
N^ «

OJ
•0 j>>
B cu

4J «r4
CO 4J
01 U

GL.
cu en
,-1 ffl
•O IH

cu
I"

CO CO
3 0
o


H U

i-H »D
CD 01

§•£
CO 01


P CQ
cu en
U3 •<

..
00

-
HI

PH
irculation.
rcent.
U CU
cu a.

ON
CO •

00 -^

4J T3
CO £
3 CO
CO

X •
OJ I--

JS >^
•H 111

•i-l
•O 4J
01 U
01 01
i-H £L
,n co

^

TJ

E

cn
cn


•

--^
M

r-4
CO
3
e
C
CO

T*

0)
w

..

-------
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
>.
O
o>
OO
Z
O
   30,000
   20,000
O
u
   10,000
                           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

-------
w
w
a
CO
w
CM
CO
 CO

H



o>
o
C!
O)
5-1
to o
C U
0 O
•H
4-1
to
0)
to
o
p.
O C
0
^~j *r"J
3 4J
o to
1 4-1
r-l fi
0)
0
C
0
o








































V-l
3
0





Q)

CB
P






/~^
J3
CX

CO
B
•*- —
60
— ^









O
•H
S-i
O)
Q.
60
C
•H
t— 1
O.
G
a
CO






C!
o
•r-l
0)
4J








SO OO OS OO
oooo o o
CM vfl O
OO CMCM f-li-l r-l r-l
• • •• •* ••
OO OO OO OO







^O VO ON O ON ^t" CO CO
r-~r~. r—ir~- i— i o ^ *
C 50 -1 bO
«8 3 3 3
•n < ^ <
TD
r— 1
PQ
0
r-l
J-» 0
co u C
o

cfl 3
, I *> ^•f-l
r^ 3 W
^ M-J •
*-> i-l OT
O
r-i ci^ in o u"! rt
o) S cy* o *r3
> BJ O • O CO
do CM w CM >
O) i-l
Q 



Cl
o
to 01
•i-l r-l
H 01
rl 0)
CO AJ
O co

t^J t-£J

(-] J^J
J-J >J 4J
r*^ ,0 1 oo
m r-
-------
  12,000
            FT. COLLINS

                    C	:BOULDER
           I   I    1  I   I   1  I  I   I   I   I   I   I   I   I   I   1   I   I
       1970    72     74     76    78    1980   82     84    86     88    1990

                                   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

-------
*w


 3
 tJ
 o

 I
 OS
 s
 >
 w
 a
 H


 s
 «

 s
 3

 CO


 1
 en
 to
 H
 §
 1
 n




  (U
  to

 H













>
n
*o
.*!
Emissions














•o
b
•i-t
3'
D*
V
U
CO
c
o
ft
>r4
*O
3
(
.
^





Xi
en
QJ
«H
(U
*J
(fl
M
4J
10
x:
s


CO
g
i-4
U
0
•-]
o
VH
(X
(J
4-1
<4~t
U
j_l
&
£
"n
ij
*
B





°0
O
vl
4J
s1
•O


.
4
c



f— 1
fi
V—









§






% all
vehicles
«-!
>,
CO
T3
j?
>,
H
1C
5 §
i 4J
CO
ij
U
>iO
M to
Q C
35
-1 CO
J «
J 6
0 0)
CO
O
H

s


l-i
CO
*
r"--tot^.
oc^r^. ^D.oromo\<±r*-cNO
vc^om'-lO^
CT\OOi-HCM COCO
i— I^Hi— ICNCNCSOJCMCS
cncr.rOioesicTir-coeN
inr^cNmcNiCMy3 tHU~i
Lriirimu^in^ysr^r^

^oor^in~d'^
oocNioootncsoj^oo
oocnnio^t^ooooon
c^cMvou^i/")r-.r*-fHat
toincoi>d"O^
o^-d'^tcoc^
u^^jin\or~>coc^Oi-HCNfri"*"^'^t^aooo
r^r^r-r~-r^^-r*r-^r^oooooooooooooooooooo^
^OO>ONO>CTiCri(TvCTlt^^O*ia>^t^CT*CTi
r-l























&
oo
o
n
pe{
fc
oo
ro
x^
fi
CO
i-H
o. t





>s
CO
tJ

^

t-f
CM
CM

tO
vO



CO
C
0
•H
to
CO
•H
s
0)

0)

J3
CQ
|
iH
<
•n
                                                  173

-------
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
              O
              I—
              <
              oo
          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.
                              182

-------
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

-------
                              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

-------
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.
                              185

-------
    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:
                              186

-------
     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

                                187

-------
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.
                                188

-------
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

-------
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.
                                190

-------
    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

-------
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

-------
   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.
                                193

-------
  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 .
                                 194

-------
   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.
                               196

-------
                              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

                                197

-------
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

-------
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.

                               199

-------
        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
                               200

-------
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

-------
 cfl
H




w
C
o
•1-1
4-1 O
0 0
0) O
.p— j ^]
o
i-i M
ex o
m
PM
g
r~5






•°-
t-i
o
•H
4-1
CO
r-1
o m
a. oo
to ON
CU i — 1
4-1
C M
•H 0
m
jj
rrt
w
0)
a
•H
rJ































d
to
j.-!
CX

PM

2
r™3






4J
r* yj
oj -a
co C
01 CU
i-i i-i
PM 4J


C
CO
cx

PM

3
1—3






4J
Crn
UJ
CU 'O
tt> C
CU 0)
l-i )-i
P-l 4J




r^
ON
1-1






















O 0
o ^o
r-~ in
*O i—4
CM  n
CM r-4





O O
0 0
r-~ m
VD i-l
CM -l 00
oo co
r~- i-i
r^ oo
*\
1-1





0 O
o o
o o
m t~-
\0 CO
i^. oo
r\
1—1

in co
\o m
CM m
CO CM
O CO
CM m
1-1





C 4J
o c
•^ (U
CO ^
r4 O
3 r-l
a ex
o e
a 
r^ o\ m
r-< 1-4 in
r^. in







o O o
o o o
vO O CM
CTv CO ^O
v£> CM  i— i m
m >
0 C O
•i-l 0) i-l
CO K** £
•-I O Q)
S i-i
P- a. n
0 B M
o.  > >
ti a s
a) a) CD
Q Q Q
O CM CM
vo  r^.
O O t-4
o m <^
CO O CO
CM i-4







o o o
000
O -•>
o c o
•r-l Q) T-l
^ F 8<
c3 ^ 6
i-l O CU
3 r^
a. P- Q
O 6 pq
a. a) o

H M 1-4
0) 0) 0)
T3 TJ T)
i-l i-l r-4
333
O 0 O
PQ PQ PQ
i-4 i-l
ON Cs|
O ON
0 r^
CO i-l
r^ oo
r,
CO





P-. OO
ON i-l
CM CM
O vO
 -M
•r-l
to 4-1
T3 -r-l
1 0)
0 C
4-> CO
3 to
Q) 4J

>, >>
i-l r-l
•r-l -H
CO CO
n Q
vD vO
cN r^
i — o
r^ co
CM 
^r-t >,
i-l -H r-4
•H Q -r-l
CO co
P Q
 §
•H
 60
 CU
Pd

 to
 CU

 G
 0)
Ct
0)
u
1-1

o
co

CO
4J
CO
      C
      cfl

     O
     00
     ON
                                                                                                         1-1
                                                                                                         o
                                                               202

-------
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,


                                203

-------
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

-------
                                       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

-------
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

-------
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.

                              207

-------
    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
                              208

-------
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
                               209

-------
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

                               210

-------
                                 JOINT REGIONAL PLANNING  PROGRAM

                                          HIGHWAY PLAN
                                        	 LIMITED ACCESS FACILITY
                                        	PRINCIPAL ARTERIAL
Figure 42.   Joint Regional  Planning Program highway plan
                          211

-------
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.
                               212

-------
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

                               213

-------
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.
                               214

-------
     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
                               215

-------
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

-------
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
                               217

-------
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

-------
o
CM
s
H
w
w
o
PH

BS

O
CO
H
M
O
m
 TO
H


















CO

ON
i— i

C
4-1
»-*
<

























M
CU
00
s








cu
4J
TO
•i-l

cu
cu
4-1
c
H











t-4
cu
3





cu
TO
4J
cu
0
i-i
cu
PH

cu
4J
3
t-l
O
CO
CU
60
TO
4-1

CU
0
J»l
CU
FU


CU
4-1
3
t-l
o
co
3
60
TO
4-1
0
CU
o
cu
PH

CU
4->
3
t-l
O
co
"<













o
O
i — I





CM
CN
 r, r\
CM CN r-) i-H ON
•CO-



ON ON 1^ O CM 00 "">! O
CM r-l i-l 1 00
1




CO CO vO ^j" vO O OO O
co  *> **
CN i-l ^3

0 C
O O CU C
.,-4 -rl M CU O
4J 4J tO Jj -rl
tCS O TO 4J
4J O ft
J-l 60 r-l g
CO 60 O d TO t-l 3
c a ft -,-1 £ TO w
O TJ W J3 O 0 ^i g
O 'QWC't-'CO'rlCU O
O 3 TO O J-l *U ^ O
^. O O !-l i—l fl^ CU 4-1
i— 1 ExjttiE-lOPMi^O i"-l
•rl <®
G 4J


^O







vO
ON
ON




in








ON
m






m






00
co









CO
6
cu
4J
•r-4

!-l
cu
5
O


o-







CM
CO
^O




in








CM
CO
*sO






^o






00
vO
•J*



-0
TO

K*"»
4-1
•t-l
secur
bility
i-l TO
TO CO
•t-l -r4
O T3
O
CO


f^.
t-l






ON
l-l
ON
"
CM


CM
i—l







CM
i— 1
m
r\
t-l




ON






r-
a^
vO



TO
4-1

CU
E
O
O
a
•r4
T-l
TO
c
O
in
^
cu
PM
 >>
tH
 3
 03
 O
•A
4J
 CO
•t-l
4J
 TO
4J
C/5

 M
 O
,0
 TO
                                                                                                                  3
                                                                                                                  TO
                                                                                                                  CU
                                                                                                                  C/l
                                                                                                                  0)
                                                                                                                  o
                                                      219

-------
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

-------
                            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

-------
               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.

-------
                                           Air Pollution Control - Page B-4
                                           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

-------
Air Pollution Control -  Page B-5
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

-------
                                               Air Pollution Control - Page B-6
                                               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.

-------
Air Pollution Control -  Page B-7
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;

-------
                                            Air Pollution Control -  Page
                                            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;

-------
Air Pollution Control -  page B-9
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;

-------
                                             Air Pollution Control - Page B-10
                                             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:

-------
Air Pollution Control -  Page B-ll
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.

-------
                                           Air Pollution Control -  Page B-12
                                           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.

-------
Air Pollution Control -  Page B-13
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.

-------
                                          Air Pollution Control -  Page B-14
                                          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

-------
Air Pollution Control -  Page  B-15
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.

-------
                                          Air Pollution Control -  Page B-16
                                          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.

-------
Air Pollution Control -  Page B-17
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.

-------
                                            Air Pollution Control - Page B-18
                                            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.

-------
Air Pollution Control -  Page B-19
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.

-------
                                            Air Pollution Control -  Page B-20
                                            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.

-------
Air Pollution Control -  Page  B-21
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

-------
                                         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-

-------
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.

-------
                                           Air Pollution Control -  Page B-24
                                           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

-------
Air Pollution Control - Page B-25
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

-------
                                           Air Pollution Control -  Page B-26
                                           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

-------
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

-------
                                         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

-------
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.

-------
          APPENDIX C




40 CFR 52, SUBPART G - COLORADO
             C-l

-------
                             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

-------
                       § 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

-------
§ 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

-------
   (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

-------
  (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

-------
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

-------
   APPENDIX D




HOUSE BILL 1041
       D-l

-------
                                                                 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

-------
     (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

-------
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

-------
     (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

-------
     (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

-------
     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

-------
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

-------
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

                               D-9

-------
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

                              D-10

-------
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

                               D-ll

-------
 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
                              D-12

-------
      (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

                                D-13

-------
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

                            D-14

-------
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.
                               D-15

-------
                             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;

                             D-L6

-------
     (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.
                                D-17

-------
     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

                           D-18

-------
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.
                              D-19

-------
     (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.

                             D-20

-------
                             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
                              D-21

-------
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

                          D-22

-------
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

                              D-23

-------
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
                          D-24

-------
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
                               D-25

-------
                APPENDIX E

 COLORADO EMISSION CONTROL REGULATIONS AND
AMBIENT AIR QUALITY STANDARDS - AS AMENDED
                    E-l

-------
                     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.
                                   E-2

-------
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.
                                   E-3

-------
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.
                               E-4

-------
  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
                              E-5

-------
                             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.
                                  E-6

-------
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,
                                 E-7

-------
                             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.
                                 E-8

-------
      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
                                    E-9

-------
    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)).
                            E-10

-------
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.
                                 E-ll

-------
   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
                E-12

-------
                           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)).
                                   E-13

-------
         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)).
                           E-14

-------
       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)).
                    E-15

-------
            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


                                 E-16

-------
     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

-------
           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

-------

... L ' .K. -
M ;
i i i i i
i i t , . . - P
i i ,

._::;" r:_v
.._ r 	 ' '
„:. . •' _""
• ! 	 ' -


j
i !
!-) •- • ! 	 i 	
                          8
 j'[~|"~iT |";  "~~"
         i        .  i . ..
   _!_.!_LJJ	U_-,r
   «j 10 ^t   fO   

HOISSIH3 '
                        0
                        O
                              o
                             x:
                             M-l
                             o
                             CO
                             g
                             •l-l
                  :znzj   $
                             H
                             O
                             H
                                4J
                                a
                                60
                                c
                                0)
                                )-l

                                M
                                •r4
                                PM
E-19

-------
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

-------
       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

-------
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

-------
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

-------
                [1~b"'_4_L' iLJ	L
                 i i r i      ;  .  i '  r
_J	;	^_._ ._	.	!__.. _|	|_
                         _	[_  t  	I '^- , i _' 	i	i_  i
                          : -«-L_4.i4-i-U
- -i - \ — —r~:—r—p-r—
 _LI\    ' L_L-
                    _L_LLI_LJH
                                                      o
                                                      43

                                                      CO

                                                      o
                   W
                                                            cu
                                                            j-i

                                                            j-i
                         CO
                         CO
                         (1)
                         o
                         O
                                                           CN


                                                           §

                                                           bO
                                                           •H
                      NOISSIW3 319VMOTTV

                        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

-------
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

-------
         (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

-------
         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

-------
      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

-------
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

-------
 W
-P
 0)
 !H
•H
 3
 D1
 Q)
 O
•H
P
P
 G
 (D
 O
 G
 O
U
 O
•H
 M
 •JJ
••H
 g
H

 0)
 U
 fN
O
4-1
 O
 O
•H
•P
•P
w












c/)
W
o

D
O
W

££
W


























W

u
A
8
U)

O

H
EH
W
H
X













H
^4
K£
Q

M
^
H
EH
U
W
fcl
fn
W







G
O
•H
-P
m
M
-p
c
a)
u
G
O
O


3
g
•rH
X


"
e
ft
ft

o
o
in









G
O
• M
4J
rrj

£
G
0)
0
g
u

G
r^
g
•H
X

rt

g
ft
ft
o
o
in




G
O
•H
-P
ft
O
TJ
S, 0)
.U
G r3
O Q
•H
4-1
 1
u ••

M O
4J 4-1 G
W O
G T3 -d
o a> w
U G W
cn T!J -H
Q) -H a >i s
Xi w id fu w
0) T!
0 13 g \ B
4-> ft W 3
0) ft G B
CJ XI O -H
U 0 EH X
M 4-1 O (0
3m LO in S
O 3
W g







































in
r*-
CTi


v
r-{

J>(
^|
fd
3

fo
^







































- -a
ro G

•
O W
21 o
r-H
G 3
O TJ
•H 0) •
4-^ ,f^ LO
H3 0 G
r-l W re!
tn  QJ rH
4J H O
•H -H M
g rO P
fl -P G
3 Q) O
CO T3 O










LO
r^-
01
H

^
r-(

J>(
r-H
3
^








































G
ego
ft B -H
Q\ S W
-H W
0 X -H
in nj £
i — i S H



I
§
i



§
•H
W
to
13 -H
G >, B
id ic w
g \. B
ft W 3
ft G S
0 -H
0 H X
O ifl
in in S





00
E
CT»
rH

^
»H

^*i
|kj
flj
JlJ
c
US
I-J
                                                           E-35

-------
    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

-------
              ^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.
                                  E-38

-------
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.
                                    E-39

-------
   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
                 E-40

-------
                                                 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
                                    E-41

-------
                     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.

                                     E-42

-------
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.
                                E-43

-------
                                          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)
                                                        E-44

-------
 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
                                               E-45

-------
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.
                                     E-46

-------
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.
                               E-47

-------
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.
                                      E-48

-------
    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.
                               E-49

-------
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


                                      E-50

-------
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.
                               E-51

-------
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
                                 E-52

-------
     Emission Control Reguiations for
     Existing Wigv/am Waste Burners
Colorado Air Pollution Control Commission
                        Adopted:       May 25, 1972
                        Effective date: August 1, 1972
                  E-53

-------
                        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.
                               E-54

-------
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.
                               E-55

-------
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.
                             E-56

-------
                  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.
                               E-57

-------
                      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.
                                  E-58

-------
   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

-------
                            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.
                                  E-60

-------
             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.
                         E-61

-------
                      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.


                                   E-62

-------
        Regulation No. 6

Standards of Performance for
   New Stationary Sources
      Colorado Air Pollution Control Commission
                           Effective: May 1,1973
               E-63

-------
                         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.
                                 E-64

-------
                                              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

-------
                                               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

-------
                                              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

-------
                                             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.
   
-------
                                              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

-------
                                            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
 I tfi 4> O (-< I  ti »*
•3 a ^: ^ «> f5 rt o
""! v ^ "* 3 ^ ?-<:j
P., ° ii! —"    ^. Vt   ,H   £>   ii ^ ^
^ Vi '" ' sn "t-i ^ ^   ?v '  "•' " • "^ ^


g8"llleli ''^I2§!
tog  *c)ci>r_1^;c'H
?, g  £ S* 0 ^ ^ ? jr '
*J f ""*  pi'o ^ ^ r^ ^ r' *•" o ^ o fo y
  S S  o t» S o S °, ^ X ••- i ^ K S

                                                                                         o
                                                                                         o
                                                                                         o
                                                                                         a
                                                                                         o
                                                 SiNIOd
ci "a ?>   §'
" r4 "^j   ~*^
tc Q
•a,
o
^
                                       S  S
                                              "  2
                                                          P *• a
                                                          •i^l
                                                                 S »
                                                                 ^ c

                                                                               b  aj ,-3
                                                                               -  S S
                                                                      a}?^ a
                                                                      cfi ~H

                                                                           -4 C
                                                                        0 T^ "S
       te ', *^
       381
•a

a

•'' uj
poi
at
clo
e t
ers
ampl
:i,
lin
ia
st
§ S K
t< ft V.
" gP
!•»*
                                                                                           3 13
                                                                                           a1 «
                                                                                           on

                                                                                           3 "
                                                                                      C, jj j) p. «
sa
duc
                                                                                           O «
                                                                                        5 o o '
                                                                            ri ci
                                                                                E
                                                                                      cs -a.
a
_o
'S
S
cr
                                                                                               -- -
                                                                                               tci bo
                                                                                               G a
                                                                                               j »-< *H  1
                                                             g&'SSJBBS!





                                                                                      i  bo cl  i ".
                                                                                      S«§'2£

                                                                                    S«S1!5
                                                                                    O O)  O! '2  n  n,
                                                                                    ci-Q  i3 S  3 .a
                                                                                   = 5 g£3gs
                                                                                   r-72 " ^ 0-g ^
                                                                                   T^ p: -rj r~l CN a) p


                                                                                   lllllll^
                                                                                    « 4J ^ (V, -^ > "O

                                                                                    i S to 3 'w to §
                                                                                      i i? o c S t?
                                                                                      1 S ^ =; n. Q
.
olumetic flow rate of th
shall be determined by usin
nd traversing according t
1,
e
                                                                                     is
accor
samp
mum
corre
(2) '.
tal c: '
ethoa
                                                      E-71

-------
RULES AND REGULATIONS



•4->
0
CL
0)
>
*)
*J
'i-rt

7-
•5
1
M-
OJ
GJ
e
-a
o
«
o
Q)
O
CJ







i-
-V-*
rO
"O
E

C
O.
t/l
s-
-

CM

CM

CM

•-

•-





•-

CO

to
*
CM
t-
3 -P
CJ
> 
CM
CO
to
VJ-
"*
r--
10
^

CJ
ro
in
ro
en
co
«3-
M-
en
•*
r.
in
r^
to
CM
CO
in
o
t~-
2
c\i
ir.
CX3
CM

in en
in r^
o r^
to co
f-« r-
ID Ol
in a
h^. o
in in
CO CM
en to
en ^
ca i~-
»— h-.
r— i— •
U> 0
r- CM
•«)• to
S CO
in in
en CD
CM r-»
,C3 CO
in ro
r^. 01

<0 ^f

an r\i
cr> n
to ID
n 5
o in
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
in in
co en


in u>

.- ^i-
J5 ^
O CO
CO •—
r—  in
CM CM
VD ^O
CO Cv%
CM CM
n in
CO 1-^.
CNJ n
UD ^f-
U3 fO
co to
to o
*u- in
to vo
^r ^h
r^. tr>
r- ca
tn r*.
G\ 
CM 0>
to co
O CO
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-
o to
0 1-
CO CO
r^ co
if r—
in o
CO 01
ro en
CO t--








r- CM

CM hs.
o t~
U> t£>
in en
co ro
to »•*.
CD to
in en
CM M-
i — in
CO CO
in in
co en
CO CM
«*• CO
en 01










M ^h

coou>cncoinr»u>cooi
TMt*.or»«>e»«s»«i'«oco
r«.b»txicocoeoo«rno>o»
eMO«3-«rroomeft
to CM in «o r— «i- «o fa
r».eoco ro »- r-
ro *^ o ro 10 co
co to en en en en
i — in to to
en CM in co
co en u* en
r- «•
in co
en en












u>u>r^eae»or-eMf>-*

                                                                     a



                                                                     <
                                                                     o
I
0 { 0
1
1
__ _(
1
6- ' o
i
t
i
i
O 1 0
1
1
1
i
o i.a
i
i
	 1 	
t
t
> o
1
I
1
! o
1
1 *~ «-
1
1 O
1-- — - — — -
t
I
I 0
1
1
                                             cr
                                             a>

                                             CM
                                             •o
                                             Q)
                                             TJ
a
0)
v~
ra
                                             V) _ >

                                             O 5
                                               ,
                                             .? Q>

                                             LL c3
                                                                     o
                                                                     o
         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
C£
UJ
i— ee
UJ UJ
*>; t—
\ 1 S
S %
I ^^
^S^jfSi—^Sfen .—vj
*^ i... — 	 — ' hi -,r~\ ^f
y- t .•] 1 J
H "H
Ul 1 I
> 'i^rj, — ~v/'d
ui $ fit rTYf!
3 "^-^ 111 i/ / L
^ ^> ^X-ii^o

t (rO^^^
rf^ n
°^"-J
_< ^ TV
K W flo
II X tV^1,^,

/f/Kr^-pi^v.'! :^fy^~^^
I "^^r IV^IT
1 L^-- 'f^'. , ^^
^^yvj l-'^l.*..^^

^^\-^'f^
rn ^ Ki.^°
Lfe o V^
\
I I
uf*^^ ', ' ^
a* I O
S !! g

ul
>-
-JC
-^o
C/l
»—
z
h . 1
--•2 s °
2
o>
C
"a.
^ I
S ?
Z (U
Cu ri
S ^
t-t 5
CJ '-^
e
^^2 V
r •*

i^
S
w e
s '|-
f— ~>
LL-^Z,
-5 *r-
<
i— ,
0
ec


X
o
Tl
Q
li
>- >
UJ p,
^ Pi *
dtf
O S!
^ *—
t/i
3

UJ
S
H-
-XL
O
o
1
o


























,

























































































































































g
75
c
'§
,2
 tj H » o ^r > «» w -• d ' J4 I •** S d'°rH?>S'c*? £ T* "S ri^
^ g So g o£ S> ^"So5aS"<5^S^^^£g«c35g§ S^ 4< S §£
I tal I ^ i I fi ? l^s&l lrqi°? «5sll5ofi |^ . § s u s
- ps ? a JdJ 1 a ||f:l MjasS ffiB^sS^ a2 S 5 « 5 .-
o St;0 £ S^*^ S c"o.<429. _rt^«, S c
2 g.o T 5 l*8d- 1
MU.Ht n
R t- S ^h ^^o^iu J;
S a 3 g'» o U^H o S «
S fHii!! !l!4
? ti'as S"T! ^ » j » -rt^ui
5 ,&o^5^« l5E«2ss
-. . H C
v,Si- .r^ M - .'SB
s :i|« lii^f ^pSM! f! 1 Mai l«
i ;iin mm : i s ?:i?
1 S.^8-^ ifnSls .|4|-|l^3 55 S *IlSS~S
1 fillt -J§3^iJitl^3l| I? 1 ? ^Isli1-
! li A 111!
0. C) P °° ~ '- - "§ f'1 4i >, o S ^ " "" -5 ^ •" ' " -" " c C ~ 'S 5 " '
S S Q 5 3 o S c 3' s r i. ^ o ° - . ;.j ;" (j< _, j. 5 g 9 ^ ."- "- >• 2 2 x L
TitfiH^i-^°Uci!^ Oi^Q-^w O o Uoti.HiE^CoJ-S^
Cfg ^ P rt •" ° o^rt~° "^ -3 •§ 14 h £ VI
6>DHW'M'*"io •roi;t--1codro-i"r,''-|Hm'^^ -1l'ot!).,ofi
^4 irt - ^3 • ^i • P ' GJ • ^* • • SH ' fc' * ' w C CJ "2 • ' ^< 4j> Ss ^T ^ . MS ij ^H r; ^i i. .-. t>,5N rn f ^^ ^> |! r-t
i" -*J i-1
^ -, ti^
' ci Si K ii
/Ills-
" r"; H S 5 0 " ""^W O , °t?
Sls:^t^° M !;* s|sp^:ii^a H
ti^isi-s8:-i is i is Pi&isy^jM ;&
*^«rMpl! s l|! "igl^i^fif i-
•?K-^S^^ 2" ^8 l^lPlnp! P
i^IpfPr ' *Mfs^ IfE'lIfaili
E> »^ m 3 pj T , M .T^-*-1 ^i n,t-jcl-'^^'^ou«^&'rj a> .Q o ta Q
!l|ll| 1
§^ W
      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

-s
_ X

1.9
-i
> through
ndard coi
'B.*'
i »
WJ «
" 9
^°
ol
|-S
~3
OJ •
.« o
M 0
U
0 1.
In c..
5?
3.
fi^
S3
w «
V. 0 53
3 "M
C^ ci fcw
"I5
E
V
d
d
v»
0)
s
£ .
ci »
. j;9
*; rxu;
ri v [2
ill
<
ii
ternperat
S
a
3
M
i^>
1
<

s .
3

trt t-%
\f> m
t* o
o a
.!£
"Is
"5
                                                                   is
               o"i   9.6




                                                                       «     S



                               B
                                                                                         I
                                                              f *! S > oS °^
                                                                 sslo  §




          O P (3 £> frf1 v
                                          di r«
                     " 0 " -u i '.
                                                        x
                                                                ag
                                                                    S!
                     t
                                                                                      *
  •|S^'3||s2 g||
                                                                U   O
                                                                                >f5H>>
                                                                                                    u
                                                                                                    a
                                                                                                    3
                                                                                                    X
II
  -
JS2
"3. j>
Oj
  W
a S
 -    w
 c;  -
 i £ «i N.
 s&r
                                                        T3 75
                                                        C B
                                                        C5 o

                                                                        ;!&!^§SJ,

                                                                        ' ""* ^ ^5 ti O J S tj) ""
                                                                                   ^ 3
                                                                                    3g>p-*   Cl,£3   ?O  pi
                                                    «
                                                    o1
                                                                Is
                                 i. .i ^ li ^  c.
                             S  I O i
                                  P w  S- ,
                                - ' ti 00    '
 d           o^-Jaa a    «  o^S-'.«-



15    § .«G»:3ut..c££i!J.2a)£;i/!e>£i:.£;i. -3  n
                                               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
•-1 e>" • • i
CO ;_! «J C1 O
g « 0 0 ,3
| | 3 I |ijg
x*-"~r" ^x w 4, «4 « o £ f
^ ' "*i
3,2 s lasers
i B fl w * cS K O g £
-f- r, I'l _, ,.
E""i vi ej ro t*» -' f]
J: ci i_ t' D, ^ -*-> " fi
5 fcD fl, .*-! O /^ •£ £ 0
"X I.IIiSKl
^ ~1 < n £  > *^
" ' L
p ^ > "
JH>
"*
•4- "' t.'lO
^K::3
^ ^

C) ^' j^> -^
_U ^ /J f)


S 8 ^ ^ ;• r- j-j b ?: ?:• 2
^tss -^:lMs
is £ Ci c C r ? 1 £ "j g
" S ° .3 < » '- S £ S £
.0 S tl ^
 =»-< 4-3 O f4 '=•
I to • o 4) ^
'£ ^ ^ 7-' o "
"5 ^' *-'t; ^ ^:
^> rf £ £ . F;
|^ Q O 3 to
1 S « q" ^
tV ^ o --1 o
« ^ -C M *"
£ ", ^ -g «
o i! ^r c* *^

•^ ,t, u-7 ,., o


-- ; - ^ S >-• ll
w r- i/; O 9 J
•" — ' r; o ^
"^*J"O ,E Ow^,,
'- ^ "J S ^ - • 't ? S ^ 2 t!
j-J -J °, o G - '* t" " if *- P ^ 2

"- v t. d>
K, -^ ° ^ S
£ b' 7- < ex
w
00
^o
"S
* ^3
3 O*
.^! w
-.'
d dl
o "1^*
tf ^ -o-
° ^S "
3 J>
^

id — '
70
~^ ti
T
o
i— <
X
cc
o
II
11
i'
o








?0
- J
i — " „• r "
c "
L't-'
- . J
- :-'
•' j;
tr ^*-

s °- L
§ * '

^ < ~.'
	 " — 1 — T- |__
k 1 "i j

C1 i
^_ _sj

fc' »• s b" '" ° .5
*• i
	 . 	 _. 	 ,
|3?l

a«. 1
^N'-l
C T- t-;
ii i
u " i' ll
Ii ^ -^

^ ^ i''


f fc E- '

M "

t: I
0 (.-

i?§
^

«
.
f
'
<
i
i
•
+•
<.




'
'


















—.

_



—





























p
4
^
j
i
^ "
i
3
1
*




S
3
H
I/I
S
^
^

0
J
11
5,
5












_



-





























c
I
t
I
. "c
1 c
t-
K



-t
a
r"
3
3
a
o
>
;'
j "
T-i -
'\

rt.






"

_










_





























i?
*-
*  t«
i
• ^
ir
i
* ~
' t
2



a
j
-t-
t
f
•x
'
ij
^



1
C
c

c
c













































1
,
'--
'-




j r
Xi b
j ^
j C.
^ £
5 b
J
- C
j \
\ ^
J C
> -
J
D
<
D
D













































O
*c3
(O
1
"o
B
o
j]



)
"C
^ "
^
' *^

- r>

H



















—





























i
-t^




ta
CO
t'
ii*
o
t

_.
H
i:
>

















_





























3
a1
w
g
tr)
4 J
Vi
b
o
o




QJ
O.
S
s
o
t-1
0
•d
c>
^
c

ti

















































r-4
!
a
o









s



















—





























•
1
t



rinm perchlorate
n
JD
c
o

'o
^
>













I



1_





























1
^
^
3
S
3
O
a
g
3
Q


O
s
a
3
D
•a
c
=
"

"t!


















_
I



























«

"3 j. *
^
^

—
/••-
'
c
s
C
t
X.

C








C
^
3
c

"o
Cb

'p-
rt
O
rt

o
|
g

.£
.-;
"

?
i
ii.
„
u.





a
q

QJ

OJ
"a
a



*

" 'S S ^ § "" ^. ^" ro"^ ° " 2 .^ H §
S ^t.- ^K,i^ s •« ao.t:GA:.5
v p^iS w ° j,- 1° S 3 "* ^ -n. £ o
g | 3 §"?|? S 0 - § W o o- « ? t
«S~ *&S^ S §3$ c I85"! 1"*
*o ^57 ° "• ^ '?' »:" 5 u g - s „ .". S 3
2 l^"13 SoM^n ^"i i gSiSfeS S2
^ i Iiiiiiililliifiii
^£^"7J!lir"'-'^^)rt5S*-|t->_^'«<^

t~<1sS«8°c3l IS^I'oi
T H|" |^sf ^| 1^1 Is i
v'n W ' ' >' ^ ^ 77 ^ (•» ^1 "
_O ^ fcc tD O r ^J 2 ^O M O 3 -o -g
* ^s ll-h^s'lu ^ll °S ~
', c|glig°i-'-N •^?^? > fc H > . -
li^ li 11 il D Ii G <
TO > ^ t > W>
O «-n ^ « K
« x > =
i " i!
r<

H ''" v, '"> '?I;i ^ o o 5; | p 3, o ° S S ^ 2
c ii « -- 1! 7: % ? ^ S "? I S3 ,: K » o E ^ «
+-> c "t< ^ r*^ p ^ c; " •t-' ^ y QJ c/ ™ p£j ri

*-; 5 ?. r:,~ '- I ";: %j £ 5 '3 B S ^ *C +, Ug O

g o L _ . o a, .n. rj i; M ^ * -,
j; v _ J! C3 C o ;- m o. C p:*j^ (St. ^ 01 O
» t, i = ° ' X - « ' H ', " -" ' ' S ^ =>-""£
5 -j o o « i; g ;: 5 o' — -3 f- "^ •§ iJ "« vi "g ^ , ?
S?a5S|r.-S'=1g^-a-°^o O"'2 "£§.&«.
ft " ^ g s ^ £ g ? "3 £ I; S S 5 3 S £ u os ^ ?•
o | S o I § | H, ': 'I o I *0 § « S | S S 'S o * §
5 b >; 3 "2 ^ ^ r= £ ^ S -S c. •« S S ^ j> § ? f- 2 ^
S-'S S ,. " 3 " °, *^ _j o - S £ -^ ° 5 w w -, « -
EU^Sjo-'^^Cri^'^c:"?" S^Ort-i ^
SH' V*JS'p^s3.I!«2-p^" ^M*Jti5'-So
,"C p '" l", *^ " -^ ~ v^ O rt L. pC "'" 'v K(l -^ ^' ^J t4 ^ ^ ji

,c S 2 ? ^ S S 3 S <« S ;/c d # g ° S g 5 *o ^ S


CGo"^ "Q ?',^^i."*~>pC'lM"';"'i''o

ii'in'c ':<^t^ o rt ,„ i Pj ™ t? ^i "tr iJ™^Q,'riG'^
^ 3J t- ',i . -- . t- C/ tj'1 *' ^ — ; ^J ^.j " r, f c^ •-; l>
-• is £'-,"!'-' - ~- a, ^"; M Jo ^ ^ ^.' ^-" "^ •— ' ^ *" *j a c3 j^ ^j
* / " ,l r -^ "j " " ' "j ^ V- — ' : - ; ' H

; . r" - " _^ ^ -• - " ' , ^ : "; *" o '": 1
^a^^-^c^sfl^SJl^^Sii^ll
'inKp!^lofi*(SH^>-^ri-4-itJ'O-*-' P, ?3 C rt W *J
           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

-------
                                          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

-------
        (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

-------
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

-------
   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

-------
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

-------
                            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.


                                       E-122

-------
                                 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)).
                                   E-123

-------
                "L         I9"
            i, j»,<». e> jf^   /*^ i.at

            ^tiio   uy
          "*•*   vt »!.'  : '-' !' i •. i>
          jr   ^ss^Wti fa tii H
Colorado Air Pollution Control Commission
                 E-124

-------
                       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
                               E-125

-------
                                   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
                                            E-126

-------
                                   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
                                    E-127

-------
                                   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
                                         E-128

-------
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
                       E-129

-------
        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

-------
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

-------
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

-------
                           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

-------
                                                     00
                                                     c
                                                     o
                                                    T-(
                                                     00
                                                     4J

                                                     a
                                                     to
                                                     D
                                                    O*

                                                     Ij
                                                    •H
                                                    <

                                                     O
                                                    T)
E-134

-------
                                          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

-------
                                   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

-------
                                           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

-------
 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

-------
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

-------
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.
                             E-141

-------
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

-------
              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.
                                E-143

-------
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.
                            E-144

-------
       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.
                      E-145

-------
     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





                            E-146

-------
    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.
                       E-147

-------
     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.
                             E-148

-------
    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.
                                E-149

-------
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.
                       E-150

-------
                     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.
                                      E-151

-------
    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.


                             E-152

-------
    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.
                                E-153

-------
    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.


                                E-154

-------
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.
                             E-155

-------
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.





                         E-156

-------
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.
                             E-157

-------
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).
                         E-158

-------
    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

-------
    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

-------
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

-------
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

-------
                  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

-------
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

-------
O
to O
W
O M

>< a
D «
W 11
   tH
   W
(N <
    U
    D
    (IH

    O
    o
o  <
Z  K
    O
    1-1
    O
    CJ
EH EH

   g

   M
   EH
   to
   W





























c
o
H
-U
d
H
VH
O
C

u
o
-U
o
d
[-1

C
O
H
n
u
'i
r
'^;
















T!
o
rj
H
d
4 )
.a
o

d
4J
d
Q
















O
O
Vi
3
O
co






C)
u
Vl
'J
o
l/J














o
CJ
c
o
J-<
CJ
UH
o
K.























Vl
o
4J
CJ
d
t-_j

rj
O
rH

L"i
H
fi
U















r
G
H
t_















IT
i,
O
41
O
1 .
d
V i
d
D.




*'•
V<
O
C
o
4 )
(-•
u
in
o
u •
VH O 1
3 ;: o
O 0
in 4J a
1 U U •
4J 13 CU O
l/)r-l C
3 4-> >, H
Q C J3
O
CJ CJ - 01 4)
•rH • I/)
4J rH VH -H
•H O O i-l
Cn VH T) d
3 4J In -ri
fc, C O 0
O O
UH CJ -^ D
O w to
Tl d
C C SH rH
O IB d
•rH « 4J
4J •• T C
n LI *f o
en c o t
•rH O O C
4J -H 1 O
t/) CO C-l. rl
CJ CO O -H
> -1 1 >
C G 03 C
M CJ CO t:










o
rH
•H
E

CJ
r-H
0
•H
x:
CJ
>
v^
n
X!
rH

r-

m


.
4J
Di
a n
Q >.
d
o s
•^_; ^
d Cn
V -H
O S
r-H
O <-4
U 0
T3
O
rH 1 CJ
O C IP
> 3 d
d VH
VH UH CJ
EH O >
IB
n en U
Ql C) X rH
r-l r-H Ul
rH "\ 'O U 1
: : n d d
O VH
O II VH 4J
rH
o — 'O :•
r{ r | f_) r-'
,rj ; ; > ^
CJ > d r;
> — &-J
cn
•U
d
O
C:'.

'O
CJ

r;
f,
f.
L-i

UH
o

r-H .£
O in
VH H
±> f~-
^ d
o •<
u-t»
Q
-a
c: cn
d -
CJ r^j
"• r-H f~-
4J 4J Cn
r/J 4J rH
O d
CJ o
CO •
*• in
4J c: i
f. -H CM
C' r-
£ JJ 1
CJ (f) C,
vi 3 <:
3 Q
IP
d u .
O .( >,
^ U-i rj
U-J rH
d d 1-1
-^ in d
:-' t- >










01
rH
H
E

o
rH
o
H
d
CJ
>
\
n
JD
rH.

r-
rH
•

rH rH
d -rH
c u
o c.
H 3
&•> o
C.I CJ
c',
CJ
VH H
r; '4-1
r' U <
r, d
C) VH
Q EH





UH
0

Vl -3
CJ C.
'> d
E. cn
3
X X^
4 t
X H
^
— .
[H If)
. ^'1
.> d
" rO
•o
o
^ !•"•
d O
r< r;
c,T ,,
C — r 1
o c
L'l 1 1
•:) "„' H J
:: d f
-; o c,
co r-. o


o -a i
T) C
H-d -
3 rH < •
'J £1, Q T
O CT 0
H O 0
• U H
O
^ C •
-H O 'A • ' .
cj o cj
M rH 4-J U
3 O d -rH
^ VH -LJ >
-U co Vj
• C C)
2 O in co
• U c
>-> -H c
c n o
'O O ^ -H
r: -H a, 4J
d in d
O 4J >
• M d VH
o c_: o ci
VH (,';
a 'a U c
c o
~-H O U
r^S x:
H 4J r-H
"' VH H
H 0 C O
CJ UH H CO

^ ^
C n VH
•O 'O ^v O si VH
•H fH M 4J 4-1 O
Olio C U T3L'14J
O4JO-H O Id -HtOCJ
VHdVnUH 4J UH SOd
CJ --^ ID -H "-i
xlSTj ~cn ^tlc
3OTJCJ >i Ul VH rHOVn
-•H C -H 4-1 C) O CJ -rH CJ
- 4J -H rH VH -H C JJ ^- -H M >
> VH 3 -H d I-H .r: w o cn "H c o n
- d 4J o H tj> M d w ci cj i-
j auH >,n 3 a UH a ^ C cj
O O "HH \ -H Or--* rH "J H CJ r-H
N' 'O uj o T3 VH VH c U C VH 1} > C
MCJCOMOd O"OO -HO
13 O O VH CJ C) -H 4-1 -rH 4-J - 4) -H
-^ c -H n d a ',1 o n d w I-H VH d ;r,
irl o 4-1 CJ \ ~^ <-J c £ £ r, 3 ±j r-
r-j cx o n n r-H o u-i cj H o -C —> o o
o in d ci E rH VH V-, ^ rH p ^ O cr> (_•
• 3VHOOOCJ3HCJ--lCdCJ"-
~— in UH 1-1 4.j co ic to 'U tJ 3 u-i > 'rj
II II 1! II II — ' II II
IJ] If] " -
^) u M u; u I-H >

^ IIH UH
O 4J O O
H D, rH
-u a o • • 13 o
d Q VH 4J 4J ' C VH
> • 3 C^ Q. -rH 4J
VH n 4J CJ O CJ 0' ": C 13
CJ-rHQVHQVH OC
U D 3 3 3 VH CJ d
tj 1 O O HJ O 4J O rH
O CJ -H 'O r-H rj ,-H UH £ ^
CJ CJ VH d 3 rj a O O
• H [Ji VH O V< CJ G H VH — -
•H > < O H O -rH "J /] CJ CO
HVH rHVHrHVH -IQ CJ
O O «H O Cn O C> 3 IH C 01
C/JCOOCJi CJ
•y o xi
n, n, u
:-i >i o -H
CH EI Cn 4J
ra d
-H Ci CJ t
rl 0 VH -H
O V, U rH
W U < CJ

o
',,
3
4J
-(
3
CJ
• 1
M
i ^

















. — .
4J
VH
O
a
o
K

CTi

^
in
IB
EH

O
u
Q
W
&,
' —

CI
VH
V
x: ,
> «.
VH
• O
VH 4J
>i U
\ d
CJ UH
14 0",
cj cj in
d H O
^ ^1 "^

SGO
O H rl
4J rH «
CJ C
X C
cj •;
r j x: H
~1 4J "3
-H
o n

• O



c
~O 0
IT: -H
d in
J n
•rH
0 E-
~J £
d O
VH CJ
O
rH CJ
0 -n
U 3





-o
Cj
fL,
o
. — 1
CJ
>
CJ
Q

o
Cn
d
o
Vl
u
<

4J
fjj
CI
i:
CX
O
r-l
11 CJ

.-1 Q

















. — .
iJ
VH
O
Oi
OJ
K

CTi

^
in
IB
H

O
U
Q
U
Oi
*"-•'








U-I
O

_,r->
4J
C
O C
E 0
\ H
O 4)
VH U
CJ 3
d VH
\4J
« Ul
t: c:
o o
^J CJ

CO



Lj
Q
l/J
O m
VH >, o
J-l 4-J * U]
cj cn LI ip
-- 3 VH ^
O CI
VH CJ Ci -^,
o r: HJ
> - H C
c u -j- d
a o r; 6
a cj u) u









VH
OJ C
'O O
C rH
3 4J
O
CJ 3
u> VH
d 4-1
O in
VH C
O o
< CJ
rH C
.H - .U C>
d rH r f r 1
rl d O -)
4J H Vl O
c: VH Q i 'l
CJ 4J E, Vl
"J n [ 4 )
•( :> O r,
'/i "J CJ I.
11 C^ O
C-, M 0 CJ

















—
jJ
VH
0
a,
o
#

Ol

V
10
d
;H

O
U
Q
LJ
rii
~ —







UH
O

r--
4-1
r-
5

\
C)
VH C
0 0

\ 4-1
 U
•~. 3
O VH
u +J
rn l"
— 1 C
c^
• u
--l U
L


.
4.J

O L^

(""
o >•

-j "c

o r*
	 ,
O l*^'
U 0




c;
o
>, H
rj 4.J
•^ u
.h ^
"tri -^
'1 -iJ
T" L".
[H
~i ( Q
O L>

n !-.
O O

r-n| r-;
;: ^>"
c*
o

4. 1
D
"-1 "5
f'J i*
: A'

, , r.
.~ CJ

















— >
tJ
VH
O
a,
o
(^

01

X
n
•3
EH

0
U
Q
;j
(X,






VH
n o
O -H
>|4J
\ d
CJ C
VH H
CJ rH
d U
\
n -
c U
O
4J C
O
c~\
• CT'
C. S
H
O '•J VH
4-' C G
0 4-'
OJ « W

(N ^ U-i




*"!
o
a

o
•o
d
VH
O
rH
5




- CJ
in cn
rj> d
C M
•H O
f-l 4J
•H CO
d
E-i -0
C
UH d
O
•.
(/) O
O i-1
VH a
o d
< 3



C.n
C ^ (^
rH ' ,
:^ in c.
vi :'. •*
r' :' r '

u :: 'i

















- — •
4J
VH
f)
Qj
CJ
2*

cn

^
in
d
rH

O
CJ
Q
~J
^H



rH
O
'^>
d
"O VH
C 17
d
in I

l
>-!
• >.
VH \
^ r
\ Cj
c ^
o ^~
4J P
\ L'
'."] CJ
C 4J
O
4J L-l
r-
un o

O C.J


V

O
..J
r-
UH 1,
0 C
'"^
^ o
'J
~J -. J
4-J1 ^
*-* •"
"





O
4J
d
Cn
ri
Vl
cn

l-'t

tl
o r,
c

r °

r' CO



C)
i i

C.^ "C '
; ' ~'\

.' C.
'< yi!

















- —
4J
VH
0
a,
q
^4

CT>

J^
71
d
EH

O
O
C*
.J
c*





\. *HH
"3 O
d
:> CJ
.d N'
•rH
o n
o
O f
-H O

o rj»
^
0 H
~ "J
c
'-, 'J
' U.
"- <-] 4J
tJ 0|
o -^1
,j *. t
Jj jl

^ 3 ii
-H >,i.i|
	 1



C
O
'-<
'Jl
o


1
M
< t 4
."- -H
— -i T-*








-W
G

^1
'"J
O
XI

- J -1)
O -H
., j
• *-J
:• -j
* '. LJ




•Ji
4 '
"J O
1 • 1
.' ~)
"- ...
_> iM
                                               F-8

-------
o
W
                  Ul
                  rv*
                  5
                  CJ  CM
                  U  l~-
o
LQ  I

2 ><
O H  K
M r:  rj
oo r^  o
LQ O  <
H CJ
r:     K
U Q  U

H <  2
O     U
2 ><  O
Q d
    O
U O
> w
M H
EH <
M U
O
D U
Cw U
                      O
                  rJ  Q
f-1
c
o •-<
r-i ra
O1 4J
0 0
K fH

C
O
"in
M
CO
U-l
U-l
CJ
C
-.H
a
rH
•r-l
CJ
W
ra
rH
en
3
O
Q



r-l
a
^>
c
CJ
D

v-. y.
n co
CJ 0)
rH VJ
u u
rH
o
15
3
0
til
C
•o
r-
(0
a
ra
V-|
^


U)
6
rt
13
<
U
C)
JJ
O
E
rt
VH
CO
Oi

CD
U
r-l
3
O
CO



• t>1
V-i
o
en
CJ
4J
ra
u

CO
CJ
M
3
O
W

^0
«-r
-
O3
CO


rH
f-~
CN
h.

CN



[~~
O-
CN
w
CN

r~-
VD
O
fc.
rH
rH

CO
cn
en






CO
M3
*3"
fc
rH
rH
rH
"
in
• — i


LO
in
rH
•*
CN
rH

rH
CN
CO
w
CO
rH

1H
C)
D.

in
O
rH
•rH
e

co
r— (
CJ
•H >-,
,r, ra
Q) 13





in
T>
ra
o
t-i

•a
CJ
>
ra
DJ
C
°
Cl
OJ
in
-
o
O
0
CO
-T
OJ
OJ
*.
r-.
CO
^D
-

.
Cn
O
C



.
Cn
CO
c


CO
CN
r^
*.
rH
O
CO
t.
CO

Cn
O
C

rH
CO
l-l
CO
*£>
ro

^r
CO
r-
»•
«3«
in
CO
UD
in
U3
>.
CO
Ol
CN
i-H
V-I
CJ
a

in
CO
rH
-r-l
E

0)
rH
U
•H >,
rC C
o ro
to
ra
o

r~l
ra o
O t-i
> 4-1
co d
a, o
u
c
o ^
o
T! C
c in
fO —
I/}
r*i
O>
CO
«.
in
CO


o
r-
rH
..
rH




•
Cn
CJ
c


00
CO

O
13

CO
tji
ra
o
Vj
o


4J
c
Cl
G

o
rH
O
r>
O
•a

13
C
CO
F-9
o
o
05
•.
CO



0
in
CTl






O
o
r-(



vn
[^
i-H




r^
o^
i-H






o
0
vo


CO
1^





in
«3«
CO




V
in
TO








V_l
o
13
C
3

CJ
Cn
ra
co

u
1
in
3
13
C
M

«.
i-H
ra
•H
JJ
C
C'
TJ
•H
CJ)
co
K





































































C
O
•H
4J
U
3
l-l
jj
LO
C
o
0

1
V-i
a
E
j-
d
u

d)

•-
rH
ra
•H
Vj
4J


















































































c
0
-rH
4->
o
3
V-i
JJ
LO
C
0
CJ

rH
CJ
•H
0

CN
CN)
U3





r__
en
rH






•
Cn
CJ
C



•
en
CO
c


CN
CO







o
CO
CN


rH
n





CO
CO





Ch
cr\







ra
1^
rC
"t"
• H
rC

UH
0

10
0

o

1
CJ
3
Vj
4J
LO
C
O
u

^>,
ra

i
D>
•rH
X

































































c
o
H
4J
U

^
4J
LO
C
o
o

(-I
C)

c
3













r^
O
•H
JJ

-T
rH
O
«-
rH



CN
CO
i-H






in





1-1
^3*





O








in
CO
VD


«*
O
1-1




CN
in





o
*3*





CJ
- Cn
in ra
Cn Vj
c o
•H JJ
rH LO

ra 13
4J C
ra
UH
o -
o
LO 4J
OJ LT
v-i ra
u u

Cn
c
•r-l
C
•rH
E
in
- Cn
Cn C
C -H
•iH rH
>i -H
v-i ra
Vj JJ
ra
3 03
o
O
O
ao
••
CXJ
^r


o
o
CN
^
^




O
0
r-



o
o
*3*
«.
i-H


O
O
CO
V
r-i
i-H




en
o
c

o
o
in
m



o
o
in
^
en


o
o
CN
^
0
rH

O
-P
ra

a
V-l
D"1
o-
ra

Uj T3
O O
Vj
10 O
C JJ
O LO

a
en
ra

O
4-1
in

o
4J
ra
Cn
o
Vj
0^
Cn

C~)
O
oo
*•
in
r^-





«
Cn
CO
C


•
Cn
CO
C


o
in
r^
«.
^T




t
en
0)
c



*
Cn
co
C

0
o
o
o
CO


•
Cn
CO
c



o
LO
o
>.
r-l
^j<

UH
O
13
13 CO
ra o
O UJ
r^
C
uj o
O
O
VJ r-H
O -P

';'. ra




in
jj
0
rH
•a
O
Cl
UH

Cl
rH
JJ
JJ
ra
u
•a
 o
13
 3
r -I
 U
 C
•r-l

JJ
 O


 CO
 H
 (3

•a
 o
4-1
4-1
-H
 E
 CJ

 CJ
 r-l
 (U
 4-1
 in
 3
 TJ

 U-J
 o

 in
 4J
 C
 3
 O

 ra

 4J
 c
 ra
 U
 •H
 U-l
 • H
 C
 Cn
 •H
 CO
 c
 •r-l
                                                                                                                                                                                  13
                                                                                                                                                                                  C
                                                                                                                                                                                  rfl
                                                                                                                                                                                  rH

                                                                                                                                                                                  R,
                                                                                                                                                                                  O
                                                                                                                                                                                  1-1

                                                                                                                                                                                  U

-------
s
w
I
s
8
to
w
EH
in
8
EH
H

B
PH
O
K
D Q
o g
in <
     «
^ .« U
o & a
M O <
w o
W W H
M EH U
~ < p
U U L:
     <
fH W Hi
U) O
               O
Ef< CO

O W

fc, U EH
   [-1 S

10 H D
«N f^ U

w <
r*-^ f\«


C rH
O is
•H JJ
tj* O
CJ E-*


fS

D



•3
O
U

C
o
JJ
' 01
C

X
in
IS
3

u
•rH
|j
0i
•3
0)
W
in
a
•H
rH
rH
•rl
r;
04

C
n)
0i

O

c
IS
01
o
^

CJ
e
•H
M
IS
^


IH
O
JJ
O
IS
1^
iS
a.

0
u

3
o
Ifl



£*,
o
0i
o
JJ
IS
u

o
u
V-4
3
o
w

LTt
(Tv
h.
in

1-1
CN
CO
cri
^
CTl
rH
VD

CN
O
in



CO
rH
CM
^
O
CN



CO
ro
in

o
rH


O1
CO
r-H

*o
rH

cn
CN
\^>
^
vD
rH
CN
CO
CA
-
CT,
^

O
r-
rH

CN
CN

rH
O
Q.

in
O
rH
-r-l
E

O
rH
0
"H >,
7) -3





10
•3
IS
0
l-l

•3
CJ

IS
a.
c
D
n
in
CN
^
rH
rH
CN


0>
Q)
C

CO
in
(N
rH
r-H
CN


.
01
OJ
C






0i
OJ
C




•
01
8)
C




.
01
CJ
c

t
01
CJ
C



,
01
CJ
C



V-l
CJ
a

m
CJ
i— t
-rl
6

0
rH
U
•rl
£.
CJ
>
in
•a
IS
o
M "
rH
•3 O
CJ r-l
> JJ
IS C
a. o
0
c
o s
0
•3 C
c in
d —
1/1

Cl
u>
^
en
m
o
r-l
00
CO
r-
«.
n
o
rH
ro
o
CO
CO
in
n

o
CO
o
*.
rH
VD




O
O
r—

o
rH
i-H

CTv
ft
CO
^
CN
in
rH
o
rH
f~>
^
rH
CN
rH
in
r^
r-
*•
CO
""•

CN
n
CN
..
CN
r~

CJ
•rH
JJ
•H
CJ 01
a UH
o
Ul 01
u c
IS -H
JJ
rH JJ JJ
>i co -H in
(S JJ C 3
-a p cj -a







0)
rj
P
JJ
rH
3
U
•H
Vj
DI

o
"3

T)
C
IS
tJ
CN
r-.
«3"
^
CN



•
01
0
C

O
O
"





•
01
Q)
C





.
01
CJ
c




•
01
CJ
c




•
0i
O
c

o
o
rH




CN
1 —
cn

r-H






V-i C
a o
'O -H
C JJ
3 U
3
CJ l-l
01 -*J
is in
Cl C
M O
U U
<
1
in
3 1
Tl In
C 
-rr




C
O
•H
>, JJ
IS U
:•: 3
r1, 1,4
•r-l LI
X c
0
UH U
O
r-l
in rj
o 3
u 3



I
u
3
l-i
jJ
in
£
O
0

>,
rj
s c
_-: o
01 H
•H Jj
a
c-i
CNl
m




0





rH
rH





O









o







0






CN





r-H






in
rH
C°0



CJ
I/I IS
0i IH
C O
•H JJ
rH in
•H
IS -3
-u c
Cl)
*JH
0 -
o
in JJ
O in
IH IS
o >
<




0i
C
• H
c in
•H 0>
E C
•H
* rH
>i-H
IH IS
IH JJ
rj
3 ^a
O
o
o
rH
*
CN
CN

0
O
"31
^
rH

O
O
°I
'T'



o
o
r>>







o
o
t^.





o
o
r*^




o
o
t--



o
o
CO
-•
CN


O
0
CN
..
O
r-H

O
Jj
d
0i
o
01
01
iS

UH '0
O CJ
M
in O
C JJ
O in
jj


CJ
01
iS
IH
O
jj
in .

0
jj
IS
01
O

01
0i

O
o
CTv
^
•3*
^r
"
o
in
•>
*•
in
n
o
0
in
r-T
rH
"

O
o
o
*•
r^>





o
o
m
*
r-



o
o
ON
*
CO


0
o
o
-
CO
CM
rH
0
0
m
*•
r-~
o
rH

O
IT)
r-.
..
CN
0

iw
O

•a -3
IS CJ
o a

l*-j c;
0 0

IH CJ
CJ -H

"2 is
3 O
"



w
O
rH
n.
CJ
0


o
rH
jj
jj
IS
u
























f
T)
QJ
T3

r— t
U
•H


Q
c

O
«
_,
C)
Jj
j J
•H

QJ
0
QJ

•^
^
tn
U-4
Q

CO
Jj
c
o
3
j 1

C

u
•H
•rH
Cn
••H
r"
5
•H
x:
fj

'
*P
.$


o
u-*
in
C
T]
a

U


*~7
^








                                                        F-10

-------































CO

K
EH
w

^
S
< i

CN
PJ r-
U cn
El rH
3
O 1
to

2 EH

M 3 U
woo
t/) U <
M
s c J
U 2 W
< a

CO >-> CO
' — ' n^ i i
D (3 ^

cu (.-, *^c
> [H in
M <
EH U
M
U P
3 U

3
O
^ to

CN >(

3
CU


iy
U
rd
ft,
m
rd
E
-H
C
<;

in
ft



0)

o




O
c

if.)
u
1!
•3
£C


4-1
C
o
E

IH
bn



o
10
rj
a.

rH
u



p
o
4J
10
3
CJ


<1J
CJ
^H
U-l
rC
.c
u





P
0
4-1
0 a
u c
P C
3 \A
O O
CO £X,




>,
p
CJ O
U C'
p C1
3 4J
O d
10 U
^
rH
cr.
*.
m
rH
r- (


r-
o
n
.,
00



o
KT
O
*.
o
i-H

f^.
^
CM


O
rr
CD
«.
rN
i— \





o
CO

t.
1— i



CO
ro
r-
*.
ro





t— \
t— .
CO
•.
j--





o
cr>
vn
^
Cn
IT)




cn
cr>
rH
*
Tf



in
o
in
-
IT)



t/)
0)
•- <
•H
s

a >,
rH CtJ
O Q
H
f, p
CJ O
I> d<





T3
O
> in
r3 TJ
O, O
C O
D ft.
o
o
o
~
CO
o
o
«•
rH

,
Cn
CD
2




.
Cn
0)
2

,
Cn
QJ
2




•
cn
CO
2






,
tn
0)
2




•
Cn
CO
2






*
Cn
O
2





o
o
o
K
CO
o
o
h
rH


•
Cn
00
2




•
cn
00
2



l/> r-CJ
CO Cn
rH (TJ
•H 00
E r4
O Cn
01 N < C
rH n: -H
U Q rH 4J
-H C 4J
J^ 'H 4J H
00 O g
> a, EH u

?» «,
C3 O P
^ C 3
CO — 4J
C »- rH rH
O 0 3
in n U
T3 13 4J -rH
C ro c H
C3 O O Cn
CO C^ U r
v^
O
*•
CM
fH






•
tr*
0)
52



in
ro
cr.
*.
o^





as
(N
m
*.
CO





t-H
r^-
VD
•.
in
Lfl




c^
*^*
*T
».
ro



fv
iH
ro
-
^r
rH


4->
W
P
Q

QJ
>
•H
4J
•r-l
T1
D
tl4












r-
r--
a
•*
m
o
»H


o
CO
o
*.
CN


tn
in
r-{
h.
^H
iH


m
e>
in
*-
0
rH
CO
CO
0
»
rH







«
Cn
CO
2



CN
o
r-
>.
ON
rH




rH
r^-
VD
•.
m





ro
0
CM
..
ro
CO




CO
CTl
r^
*
rH
CM


C
r~










•O
co
co a,
C7* o
fj rH
o a

u o
< a


c
o
[-
d
0
rH
n co
c >
ra o
>J a
o
o
CO
«.
CO





»
Cn
CO
2


0
o
CN
*
CN


t
Cn
CO
2 .


o
o
T









.
Cn
CO
2



o
o
in








•
Cn
CO
2





.
Cn
CO
JT






o
0
CM






•
Cn

2



p
0) C
•a o
C -H
D 4J
U
C) 3
cr -H

Cv W
V-, f*
0 O
< o

rH C
rH * 0 O
C3 rH H -H
•H C! O 4J
4-J -H ^ U
c P a 3
cj jj e p
•a n G 4-1
•H 3 o n
n -r, u c
CO C O
t, M ^ U
^
m
rH







•
Cn
0)
2


CO
CO





•
Cn
CO
2


CM
rH










•
Cn
CO
2



.
Cn
OJ
2






CO
CN








.
Cn
O
2






>
Cn
CO
2




10
CM






U
C) C
•a o
C H
D 4J
u-i O
O >. 3
ft Lj
10 ;j 4j
O -C W

0 -H O
< K CJ

C
o
•H
4J
O
>. 3
CS P
"< 4J
i in
UT C
•H o
S U
ro
ro
un
».
rH




CN






ro
rH





•3"





r-
rH









0
CO
ro
••
rH



O









*&
CM
rH







O









rH







O
Kf





1
tH ^0
-H
^TJ CJ
EH 4-1
!/)
UH r3
O S O
Cn
in - r!
CJ n '-t
^' ^ O
O C ~»
< -H CO


h.
tr>
c ^ OT

N tr c
lH C «H
Li -H rH
rJ c -H
rD -H O
o^: H
o
o
CD
••
^




0
o
CM
••
^T

•
Cn
CJ
2




o
0
f~»



o
o
r^








O
o
I —





•
Cn
CJ
2






o
o
CO
b.
CM





.
Cn
CO
2






*
Cn
co
2




O
o
r-




i
o
^
CP'D
Cn O
< P
O
U-J »J
o in

11 O
C 4J
o a




0

C3 O
Cn cn
O d
IH p
Cn O
Cn 4J
< to
0
in
o
*•
^r
rH




•
CT>
CO
'f*.

O
O
in
«•
CO
rH


•
Cn
CO
2


t
Cn
O
2








»
Cn
O
2



•
Cn
O
2






<
Cn
O
2






0
in
in







•
Cn
00
2





•
Cn
0)
2


T)
rfl
0 C
CC C

U-, OJ
O rH
4-1
M JJ
O rS
J2 U T3
E 0

2 O fc,




tn

0 O
1 — 1 rH
4J TJ
4J CJ
r3 CJ
U LLI




































•O
oo
•o
3
rH
U
C
-H

4-1
O
c

QJ
p
cd

'•O
CO
4-1
4-1
•H
£
O

OJ
p
CJ
3

4J
to
3
TD

in
0

to
4-1
C
3
0

(B

4-1
C
rd
O
•H
t-l
•H
C
en
•H
in
C
•H

r;
O
• H
_r;
S

E
O

UH

m
•a
c
rH
, a
o

o '


	 ,
rH

F-ll

-------
CO
&
O
H
P
O
pq

J>H
PH
o
E
1
g
O
H
LO
H
W
O
Q
f3\
K
S
o
U

ffi
tn
Pn
O

>1
P-I
I
S

J>H
pQ

^.
SOURCES

FH
i^i
s
H
H
(5
H
CO

1-1
r-l


§

[Lj
PH
H
E~*
y
a
U
H
Pi


a
6
tn
H

<
t4
M
<
1

^
0
EH
§
2

«^r
6
H
to
M
S
0
a
$
0
j
o
CJ
rH
CO
O
rH
JQ
ct)


















, — .
K
<
W
><
W
?J
• —

H
U
U
0
c<
r_,
to
^3)
Q
M
^*
H
rH
^3
Cw





K
CJ
O
1
K
£
?.
U
Q
O
K
r-l
H
,-T
r-;
t-i
C)


d
LQ
Cn
[,-
I-i
U-.
^
•-,
K-

v_!
M
0
t/J
f<
'
c

o
D
K
(4
^>
^;
L]
Q
[J
H
U

C^C
U
CJ
r:
r.:
c
^
LJ
O
CO
U
O
^-
•3
<
<
en

^
o


















^
4J
C
n
O
U
\
L
o p

*H C)
6 a
to cj
CN in CN ro r-
CN O CO f l
o r~~ to co
rH rH in



• I — t£> •& O
Cn r- o co
CJ r-t iH I-,
C


to co
• • »
tr en tn
0 00
C C C

CO rH tO CM
• *3*
Cn
G
c


f^ 0, ,., f-^
tn cr\ T co o
O ro ^o rH r-
C
CN


• • • \£i co
tn tn tn CN rH
C> O CJ
C C C



rH O1 ^T n l£)
CN CN O
rH CN •«•




o rH to co co
tr> CN r—
H rH in


rH CO ^0 rH CO
in en o LCI
rH m in co














rH

to
o
a,
c in
O tn H c
•• in -H a) D o
to 3 jj m .H
Wo in in o a-)
CJ a) 3 o 4J ca
P^ c .n i-i to 4->
t-3 o F:; r3 V-i
C -H o in '^ • O
tn H cj in (i
a o "O in
< L) r-H (J -H C
W 'Jl CJ O rH d
^ H 3 VH O .H
•^ £ [H ci< w H
c
r '-
r-
cx



r-
rH
o
'
rH

C^





CN
m





r-
CO
CO
»-
c^


CTi
n





rn
to
t^-




cn
to
CO


0
o
rH

CN














U)
0)
O
>-t
3
O
to

ffl
0)
 • CM CN
in en in in in en en
~ V * V
rH C CN C


•«'
co DI en CN IN o-i >H en Cn
cj\0 CJ cr> o^TOCJ
C C > - - C C
rH CO rH


m m to cx> 10 o rH *3* m
o in co r~- co cr> in CN o
^rin incNCN ^rrorHrH
^ fc. K
O VD rH
rH
.
inr~~ rHintn c^tDTtn
OO CN[~*O mi — ICNCJ
CM CO OO Ql O CO *3* CJ^
CO rH CO

*TC-\ COOCO tOO^TT
or^- m^co \r)CNto^T
r^-cn COCNCO CNCOrHrH
- fc •. *. «.
CM rH tO CN rH
rH
to
Cn
q
•rH
iH
• H
CO
H
c
O "O
tO -H C
M 4.1 C "3
CJ to CJ O
K -a y •* *
O n .-l 4J Cn o
O o 4J 4-> O C Cn
tn ex crOtn3'Hr3r/:
-- o c c u a LI 4J
H n TJ rH i; co O 4J H O O
to ro cj O QI rj 1,0 ^ 4-> r-H
OfTJ>^OOrH C eOTI
C-O^4-Jr^rHC3rHO *• d
tX£i,c: 3 cu-Hfdrj enc,' CJ
'-3 Q4-I>4J-H C4J(K
>T3 CCJrH o CO N-Hfl
^H OO 3QC)*-(f3^>iCnO
C-<> *?U 'OO!3^OrH
IH C3 rg Q .H 'O ._| f; _- ^ l_| Jj
U CLCC ^ C tnf; L^crJ L714J
— ' C f3tO enn) CJO-H 3 Cncc
-1
V.I
•r
CO
rH


rj
0
CO
*-
r^
rH
CO
CN
CN
*
cc
rH
c>
CM
tD
*.
in


CO
r-l
O
-.
CO


r-

^3*
V
r"


r-
r-
r-\
•-
O
CM

CN
rH
rH
in
rH
CO
in
o
-
to
IN












rH
CO

0
H

Jj
n
3
Q
O
>
•H
4J
Dl
3
U.
O
ri
cr\
oC
to
rH


rH
| —
*T
•.
r^
CN
r-
p^
CO
*
0
CN
in
CN
rH
»
r^


CM
CM
O
••
CO
rH

tD
r^
•a1
*•
t—


rJ
CN
CO
w
CO
CN

CN
rH
in
,jT
CN
L.O
rH
to
-k
o
VT




















^
{£
S
H

Q
I
O
F-12

-------
 o
 1
o
«
    K
    m
    H
   W
D H
CO [H
                  O

                  to
                  U
                  M «
                  [-< U
                  K £<
                  <
                  CL, W

                  i  6
                    E-i
                  O H
                  t- U
                  '^ IJ
                  O to
                  M D
                  to Q
                  o
                  u
                  CJ
                 rH
                 X!
                        K
                        U
                        O


I')
1-1
r"
b
t-

r^
\,\
D
*>-*


Q
t-H
,.£

d
H
c
^
M
r~
t/j
^:
u
M

C
f j
U
LO
CO
r^J
M
rH
^
r-1
^
a,

,^
r^
C1
c^
C
*'-
,^
<,
o
o
^
u
l^1
M
c^
<
J











^
4J
c
3
O
u
\
V,
1-1
a c
U U'
>-i o
3 4J
0 r,i
Ita u

rH r— in o >.o
n rH m in vr
rH ^T n CN
(N iH


ro *r in in
CTl rH T CM
O
C


T 0 0 T rH
a* o CN
CM rH in
rH



i — [ • o cr* *£>
tjl rH CM rH
a)
c


^D CO O
CM • rH rH
tn tr>
O C)
c c



U) rH CN
• rH CM rH
Cn tji
C) CJ
c c



^ m en vo ID
CN «? a CN
rH rH



rH r~ O~\ O> rH
C*") C^ CO



O~\ CO rH CO in
rH co o") CM in
t^ CN -3-



1
cr*
(•^
•H
•r"1



CO




IT)
CN
C-,
•H"



vo
in




„
in






o
T






o
rH
CO



^
CN
CM


^
r^-
^r
•^
rH



CV
rj
•-•*,
v
oco mor~~- mrNvoco
t^ rH O m ro rH <"O in CO
r — c*~] ro u~i n r~~- \x^ m
CO'j CO O C*1 rH CM rH
1 I rH O
II ^

w1
c
r:


~c"v
^>
^J-
in"




C
o
c


CO
CO







•
rji
e.1
c




o




o
CM
ro


0
^0
O
•^
fN

co • rr • • - ro in
COt/5 ^D"!^1 tT^trrHfN
-J1 rj vr rj a) 0) CJ rH
- C - G C C C
f~> O
rH -CT
vo co un in o in co fN <~^
fH rH O~i CT* CO fN CO Q->
CTi rn fN rH CN r*- r~-
f""} t^ rH
ro r~*


r- • rH • • • • CN rN
•^ Cr* in tTi tJ1 U"1 D1 ro
u^ CJ "^ CD CJ 0) QJ
•* C - G C C C
ro co
rH
•^ CN in (N in
rH » u~i • » u~i • m
rH CT1 CO L7* CT^ CN tJ^
^ CJ •* 0) CJ 0)
r- c VD c c c
rH


CO m fN rH
fN • m . t • * *3*
f^ tT" vo Cn CP tT1 tji
•• o - o o a> o
0 C rH C C £ C
rH CN


T U3 LO CM n
OJ« i — !•• *rH ^
CM tr1 rH rji Cn tr> CM
*• o » a a) o
rH C CO C C C
rH
co m o o co r^ *3*
CO • CN • CO en O
T tT1 O tT1 ^* CN
^ 0) •• Q)
<~> C r^ c
rH rH
rHin-
^X) • minr- ^ CN CNJ ^
cr,tr» tnmm vom rH
^ a
•* C in rH 
^r
rH


CN
ro
i-H
«.
CN
fN
CO
m
fN
*.
*y
fN


^T
O
vo
w
CN
ro


rH
O
*o
k
T
rH
O
0
f~n
*.
rH
ro
^
1-^
r^
«.
in
ro

en
rO
vo
rH
•-T
ro

m
rH
«»
Vj*
in
m
CO
c\
rH
fN
rH


CO
CO
rH
••
fN
CN
O
O
T
•«.
T
CN


P"j
m
"O
s
fN



CO
rH
rH
*.
LO
rH
^
TT
CO
*.
rH
rH
CT>
rsj
N
en
ro
10
tn
C
(T)
C
O T!
W '"* r. 5
*H Ct3 -U C ra
n) t_) tn u O -H
n W K "O 3 -H cj

d, U O O -UiJUCtTi O
C 01 U to Si C T3 U 3 .H O n t*
om-HC3 '^ occr-ic^-u
•• n -H u Q o o to
tO 3 JJ Ul -H W H
w o n in oj J-> tJ
Ocu 3 O-U n cdrx
'-• C .Q r-3 10 -U C) ^
.'- rj f- a ^1 M O
OH 0 V) 2 Ojj-^ c J-* ^-< o o
^>rO CO1 — t O CU >I-H C3 S EH
H O O .3QCJ^f3>-iU"'O1'H:
EH P* !^U TDCJ^^CJrH^ Q
M fyJ T3 O H'O HC,C^ !*-( i-jjJ'H XI
O cxnc IH c win tT>d tr» aJ tr> 5
£5w-<,3auxa<35 o
                                                             F-13

-------
w
^
o
1 	 1
o
w
rt
o
h

>H
g
g
P
p
H
H
^
O
H
U)
CO
H
^
w

o
Q
<;
K
S
o
u
H
g

fa
0
%
1
^!
w
rt

r-H
m

V.
CO
w
u
;ti
I."j
CJ
C/J
M
fe
<
o
H
[--.
l-l
i^i
CJ
H
CO

t-1
|J
ft.
>*
O
«
IH
Pi
W
H
g
W
EH
3
D
U
H
EH
V,
ft.
S




><
>J
^
o

CO
U -—
f-> C-1
^ <
1-5 y
CJ

EH U
Ci Cu
ft- CO
1 O
ill
S
O EH
H U
"Z !J

> O
^ K
M ft,

^ EH
O CO
co Q
LO
S >
a M
O M
Q O
c2 S
o
o
u

m
n

OJ
rH
fj
rd
H
U
a
I

w

§
to
§
to

, 3
<
0
[H
K
1-1
t_J
1 J]
t-J
tH
o

n
t-j
D
fij

^i
2
rC
(Xi
CO
Jl,
M
75
^

CO
u
3
fj

O
^
<;
t;
t:
n
H
o
^
u
rx
tM
O
W
fC
G.
3
tt
U
E-1
LO
ID
U
U
f-«
t-<
l^
r^
**"*
u















>,
4J
C
3
O
U
\
'•>,
u
0 O
U CT.
>H 0
n .u
0 C3
CO U

m cn rj oj in
i^ rs  -H in oj
C


, .
o tri co ro Cn
o CJ "^ O
rH C C


rH cr> r- ro T
LD (-- (N
r-H



C> rH *T CO ^T
r*i m p"- in
rH fl


co Cn Cn vO Cn
fN O CJ fN Q)
•H C C C




O fN Cn O '
CO rH !£! Cn
CO O
C












rH
fd
in
O
a
c to
0 tO -H C
•• CT -H O Q O
CO 3 JJ tO -H
U O lfl tO O -!->
U O 3 O 4-1 ra
r- c .q J m jJ
D n j? 0 ^
O rH O tO S O
CT rH LJ OT Qj
C) CJ T3 10
< O rH U -H C
:^ in O O rH nj
^ H 3 >H 0 W
< a tn ft, CO EH
"
rj
n
(N

1
CN




-J-
CO
ro



rH
if)



CTi
UD





O
rH



rH
in
rH



o
fN



r-
rJ^
in


in
rH




r-H
l^J
•cr















tn
a
O
IH
a
0
CO

ro
C)
l-l
F^

rH
ra
o
H



r :
•*T



Oi
C '

^
[-^
o
•*
m
-H
^D




CO
I —





rH
"I
CO

u

r-H



I
vr
o
>.
CO
r-H
0

T
k
(N
Cn
0,)
C




,
C"1
O
c



















Ui
u
(J
cr:
— )
o
CO

f_J
M
0
ft.

en ^r o in c j rH o u't in
co in cc> in r~ co r^
O rH O rH fSJ rH fO
P^ rr) f\J fN)
r^ in VD
O » ' O • • rH »
O Ln Cn T Cn tj' D1 t7'
- cj o mm ij o
in C C C C C C

r^ . coino r^^TrH .
r^cn cnr^^r rHO^fCn
r^o cnrHco rOrH CJ
- C ....... c
1X1 -31 fN CM rH
rH
f~>. . *3" CO . • O • f^
^DCn fNrHCn tJ'cncn^T
rH CJ r^ CD C) fN CJ
C - C C. C.
rH

oCn c^orM coo Cn
vo CJ vo fn en fN o
- C C
CO rH rH


cnCn CnCnCn tnofNCn
O^ C! O CJ CJ CJ r- CJ
end CCC Ccn c
fN

. ,
men "^•f^Cn cnCnt^Cn
CN O O fN O C> O O Cy
in C l£>rHC CCCC
fsi in

fi mm. fN « r~~ *
i — 1* inoD1 '^'Cn Cn
men <~irHCJ fNCJ cj
- o ~ c c c
in C rH rH

O rH rH in «3"
cn*? fNr^» ...
fN in r~~ ^J* Cn Cn Cn Cn
^ - CJ C) 0 CJ
DrH IJSxOC CCC
^J" rH
*3* tT^ f~*- O O CJi CO CT^ CT1
ro GJ LO uo VD CJ CJ CJ
coc -Trscn C C'C
*. fc w
(N rH ^T


vr» rH LO -i
Dr3>^OOrH c COT5
QOrC-P^rHr-irHO ^ CJ
Ciftid 3 CJ-rHrJtJ CnCJ CJ
'J O -U > -D -H d -U U<
> 'a ccj'H cj cu >,-H rj
HH CJO 3QOHf^>1Cno
Hr* SU "CJ^ii-HCJrH
r— * flj'OO'HTZ' rH:^^ iHrH^J
o ace*HCt,iGcnrJcn.t»
3 r: ra CO Cn O C! O -H 3 Cn rj
t Dcov-'

[•».












rH
r3
jj
0
EH

j_>
to
3
Q

0

•H
4J
•H
D
tM

V 1
0
P")
o
r^
in
o
».
VO

CN)
LA
vC
*•
cc
V
ro
O
(~O
K
(N
O
^D
CTi
*•
fN
rH

CO
^
rsj
rH

•*?•
O
m
CO

o
i"T
m
s.
VD
OJ
CO
tn
o
s.
CO
2
'-X>
V.
C^i


cn
^T
^T
s.
CCj




















t-P
^
H
O
^

Q
1
o
                         F-14

-------








LI
6
n
EH
00
^
O
H
TH
U
B
S

d
H
CO
to
H
s
H
CJ
w
EH
U
H
O
a
CM
LJ,
b
[fj
™
t ^

i-i
' ' i1 H
W E"(

- ;"J
T^
"TJ c
£-- ^_
u
»H

1 J
LJ
•H
LH
i :
b
p
O
(J









R f~3
fH h-t
LO tj
H M
H ^
•-3 H
;•_ u
H H
t H >_,
UJ UJ







Q
C
Ul
n
q

O
(J


	







O
H
"j
j
o
LO
CL'
>H
O
o
to
H
U
10
y
b
w

o





C r w
•M ' 'U
f" ( ^
4-> -- O
4-1 U i-j O


^^^_^t 	
/ ~" '
>C >-^ ft. >C >•?

in o o in o




J_T)
£
••H
L rn
•-< r-
O -H

n c.' --H 6
O ^ O 4J

o 6 ::
:J O 4-1
— ' :> o c

0















•

>•*

in

^*





-
"r
p ,j
LO U
• H
i 1 ( , — i -^,

0
r-H
















•£P

O
rH










LO
Q.
O in JJ i Ql G

a. o u.
3 O C
'u JJ
•rl O \!
CL C r
C C'
D O i,'
T1 r— ' i-| CJ C' U
CJ ,-i -1 'C1 .J -^ X
' x; - o :r o 4J 4-j
i — 1 Ll
a u
.Q C'
n LI c
4J Cl -H
b a'
L. '-' U O

H L) (,,'
C -V O CL
II O JJ .r,

QJ L'J U ^' U(
"ci
LO +> ->
-o n o
ID 2 i-J
0 H C-
* H
•- Li


Q •
• r- -7-1
HOC1
H > rH

T3OC,
C "1 Li
(3 - JJ
A r- , — .
IN1 6 O
n £ y 45
M X f E
H
rH




n

o


•o
o
^>
o
CL
c
LJ
3 -Q 3
0



















C)
C
O






•o
OJ

'0
d,

C
O LO
•o
•D 13
C 0
ID L,
to
~ C- '.H J.
-•c • C
U -M 0
•H G. -rl
Li Ci -P
-D o o
LO 1>
G) • Ll
L, O C
rH 10
TJOC
0 U 0
•o u

ft) C rH
O -H
0 >, O
C C 10 10
,Q Ly
• - • il
u*' LO T 3
t C < 0
CO r_
• -H IH O
H 4J O E
H
r-1





01
Li

4j
rH

U
-H
Li
CJ|


o





rH •^ ~"
fO
C
0 >,
•H r:
JJ '
u -o
o n
a o
0 L,
Ll •
O--C • *

>*l].h s

JJ -C '"71 O
L' Cl J 00
CJ L, C) >—
Ll rH
• H O "J
Q JJ E








>^ Li
" 0

•DC C
7 0 C -.1

o

















H

o
in














IH
o
LO

0
CM
















i<

O
IT)





...








LM
o
10
O -H ^ TJ rH C ' r— C.'
!J iS, L,
u^ "3 tn
O i , r-^ O
JJ C Ll
r-l O
rH O
•tH
0.1 JJ Cl JJ
-i a pi ^

>i<.; L, | a. 3 : o. 3
.^ :: HJ >• en ' cji
-HO £ C
SU 0 it)
u




i
o
Ll rH
O •

p •
C) H
H
O
i m
JJ O


O JJ
-rH "H
JJ rH
3 "3
U


4-J
C
O
EL
o
rH
OJ
;>
Cl
•0

•g

o
1-3
OJ Ci ; C) 01
OH C) Li
•
- 1
^ ro c:
•a u o
O O -H
-4-1 t3 -Ll
JJ -rH -H IJ
•-H U L; 3

^ in O -J
3 -H U I.

C rH O
JJ G IT, U
P rH — 1
3 a u LI
e oo
»^ 	 ( CL u
O W
rH L, P
• JJ LO C
Q C 3 O
• O rH -H
H U CL JJ
I — 1
^



G
o
rH rH -rH
rj ^ -*J
-H -H u
JJ O 3
C Li Ll
0) G -U
•o e o
~H F- r:
LO 5 0
01 U U



6
rH 4-1
rH Ll L--
COS
'4-, IH O LO
U ~
J-' LO LJ
o c; ci ci

£2 -H T;
rH -H JJ
LO CJ Li O
3 "J CL. p

f- 3 T) -J
u c r:
13 O
rH CJ U
• JJ "3
Q C C T1
M !/ ° §
H
. r-l




c
o
-H
4J
U
3

C 4J
> L7
X C
CP O
•H U
I

O











•a
Ci O >«
JJ C^
X C LO
L7' lj l^
•H CJ
O > IH
^ D O

«^
^ ^ " \
^ ^? ^(? ^ ^^

o o in O LI
CL cri CD in i_n




C
o
•rl
i-i a n -a 4-1
cj r- LO CJ c u

LO -H it -rH C.
C rH O Q. C !'
fti ;: — i u .v c (5
-J 6 JJ rH O JJ
•rl H 4_l .- rl
O JJ rH O LO -U f ,
Ll r 0 jC C G
O Li Li JJ LT ^
rH C JJ CJ It C L.

:'. 06 o H c1 i.
I- U ^ t1 IJ-



•H rH T)"
c-3 5
0 U Ll
• a ci o JJ
o a, MH c
,-l Li LO 0)
0 C' LO F;
U L: - c o
•H O O U
LO P LO -H
3 rH JJ "U
i — 1 'H O r3 C
O, O Ll <3
•- Cl
- 3 P T3 Co
rH C 1 iH C
• O JJ 10 -H
Q L L) C C
• " >i O rH
H a ii u e
rH
r"J




•o
c

too LO
C - tn
•H CT C
>, C —1
L, •-_ -H

r? -H ID
3 E JJ



O



















o
in














n LT
r$ cj
"O >
rH 4J (T1

[J r-1 -H
r* i — 1 Ll
t? i — ' C'

u &i


















i — I
Q
H
l~+
rH







G'
4-J C'

Bi C
V,
U O
CT' 4-J
&i n
""
O in (^ o
v, r
U P I! 1!
i-l C' rH
O LJ* • r-(
— • Li ~0 rj
£ i3 :> w















o
OD

















CT1

"~i
i4
C'

^


















rH
Q
H
H
•"^



4J
O


CJ
MH

OJ
i — i
4J
JJ
T)












X
4-1
— 1
rH

XI

CJ
u
L.
C
Uy
c


CJ
rH
0 "q
•H Cl
E -<
-u
f si Lv
^^ C'
rH 3
cr
C!
£ o
^-j
-T r.
LI "
O "C
i — i U
C1
LT Xj

t"- o
o •*-*
rH
t3 ^

O r-<
U
i-j
O C
V-i O
•H
CrO -I '
C' U
p ""'
^ "Ox
rH Ci
O i-j
^>
c
u o
-rH -H
V-. O
U-i ^
r" H
1, G
4-J C
•—< r1
C -H
L<
— t -O
r ^
T "U
L1 3

u
ui C
C1 -Hi

c^ ->J
-r4 n

* *
*
1
F-15

-------
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

-------
          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

-------
   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

-------
               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

-------
                                                      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

-------
    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

-------
    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

-------
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

-------
      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

-------
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

-------
    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

-------
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

-------
 I
H

 tl)
i—I
rQ

H

•o
rH
01
3

a
•H

a
J
§
«
01
IH

•->
a
•H
o.
rH
•H
O
QQ
a
rH
00
3
O
o
01

c
&
01
M
U

^4
a
01
CJ
01
•a
rH
3
0

1
a)
a
a
u
H


OJ
3


09
U
U

3
O
03

4J
•o
>
•H
U
•H
1


^
1-H


m
m
ITS
CT»

-^
i— t

0
5
r-T

CM
CO

0
r^-
i— i

f^
CO
m

l-l

^
f^
vO


p*.
00




CO
0


o
rH
m
o
CM

00
3
P-.
CM"
r-4











o
-o
8

01
1































































a
o
w
•o
0)
>
a
a

1
K
00
rH
CO




00
01



rH
00
CM



00
01
z



,
00

in




^.



0
CM

n
rH

in
00
CM




o
0

CO
CO
00
00
CM



g
•H
U
U
2
4-1

g
U
grH
a
T-4
'a u
•H a)
S §

•rt o
^H
^
CM




in
O




00
3
CM



oo
01
z



.
bO
0)



CM



l-l

o
n
CO

0







CO


VO
CM
r-l








c
0
•H
-U
U
2
4J
(0
§
U
a
4
•H
33
00
00




O
CM
in

CM


*C
in
0
rH

rH






00
CM
CO




00
0)


cr.
rH
-4-

rH

rH
in
CO

rH


rH
.j-


O
CM
CO


a
00
.g

<0


1
M

1
C
"0

00
C
£*"»
P
3
O1
CM





CM





rH
rH


CM






^





O
00





00
01
z


CM
rH



-a-
CM



IO
rH











01
oo
0)
M
O
09
01
.U
a
oo
2
oo
CO
o\




rH
rH



CM
rH


^.
rH
rH
in


m
CO


00
0)
z

CM
CO
r-T

oo

00
01
!Z
CM
CM
.
00
rH

CM
CM





00
01
X
CJ*
CM




00
rH
O
00



oo
01


in
0
rH



r^
CO

n
^


r*.
r-i

0
CM
CM

00
01
z
3
rH


r-l
rH

rQ
00
o
\o
CM








4J
09
3
•0
09
4J 01
0 >
rH 1-1
•O 4J
4) -H
oi oo
01
rH rH
•U 4J
<0 0
CJ H
                                                            co
                                                            4-1
                                                            CO
                                                            O
                                                           U
                                                           Q
                                                           W
                                                           FH

                                                            6
                                                            o
                                                            !H
                                  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

-------
vO

>->

 0)
I—I
,n
 etf
Emissions of fugitive dust
(tons per year)

T3
r-l
0)
Larimer
Jefferson
Gilpin
Douglas
Denver
CS CD
0) 0)
c_> o
Boulder
Arapahoe
3
/ s-1
/ CD O
/ 0 6£
/ MO)
/ 3 4J
/ O cfl
/ CO O
oo 00 in o ^3- OCM r-ien
•vj- r-l Ox Ox O OOCM OX
ox en CM r-~ vj- r»»
ox r —
CM f-~
CM r-l vo P-- vOO enin
oo inovo r~.cn r-ir-4
in i in CM oo vj- vo r-i
en in
r-l r-l
i— i i— i oo ox r~ in <± vo
r~. oo oo r— i in vo

in i~* r— 4 in en in ~f CM ^**
os f^x CM vo in vo ^^ i~~i
CM en oo in vo CM r-i
l~- r-l r-l
enoxooovo oxO >j <±
ox ox m r-i in oo r-4
O r-4 VO i— 1
i— i
r-l
in
vO
OX
o
r-i
o
o-
t-l
CO
r-l
r-l
r-l
CM
1— 1
OX
i-l
CM
OO
I-l
r-l
OO
CO
in
0
CM
r\
en
en
VD
OO
r-l
i— 1
•\
vO
i— 1
CM
CM
O
CM
i— 1
OX
r-4
CM
CM
c a B
CO T3 4J O O O
TD 0) d 1 r-4 T-l -H r-)
OflJ M ^Ctf'HCJ CJ«CO Q)
4-1 O 4J J-i S-i !-i Cl 60 C 4-1 M 4-1
T3 dcOr-4 r-l dd)4J >,4J'i-ldT-l tSOj
cu OT3 3 01 vugco cam >,T-II-I QOJ-I 
-------
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

-------
f-
 I
   -j- vo ^-i
f\ | rv
CN m
.— i i— <
i— i vo oo ON r^ m CM O CM r~- o O i
 cr> co
•\
r-l
covovDi— ICM vooo cMm
i— it— I 00 T-I co m<± CMO
OOOOCMOOO CMO •-!
v£3 ON OO CO m CM i— 1
VO ^-1
VO-J-OOVOCM CNO ^oo oo<)-
co -d- co - 1-1
•\ r* *» »t
O i— I *£> t-i
^-i
^0

 at ,4JT^c-i-i coca i— i
0) O-O 3 -,•!-( ^-i bOS-i  njo >-agci!scl}-(Ci''-|(uoi-i 
-------
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

-------
ON

1-3

01
r-l
^3
CO
4-1 Cfl O
JS CO 4J
O 0) 0
rl 4J Cfl
60 CO 4-J
J_l
01 ,C
5-1 m 4-i
3 r>- £
4-J ON O
3 i-l rl
U-l W
o
v-l iJ p-
0 4-1
CO -H
O V >
•rl 4-1 T-l
4-1 Cfl 4-1
Cfl M U
Pi CO




CO
0)

o
cfl

„
CO
4J
CO
PH cfl
PH O
Pi o)
>-o ri
0
fi U-l
&-« M— 1
•H
PH
T3 PH

cfl 1-1
i— i
ri
ID 0)
01 D-
CO
r-l 4-J
co a
•W 3
0 O
H U

14-1
O

C
o
•H
4-1
0
a








in
oo
ON
•— I






O
OO
ON
1— 1




0
ON
i— I



O
ON
ON
i-l
0)
60 O ^->
C 4-J CM
cfl ^
& o
O 00
ON
r-l





O
00

r-l



0
00
ON
*. i — 1
0)
60 O /— .
Ci 4-1 .-1
cfl v-
f. O
I-H

O
r^.
ON
r-l


4-1
a
~j
O
U





vD
f^
•
O






00
00
•
0




CO
vD
CO
00
oo
CM




m
in
in
r\
I—I
^J-







00
o
00

^D
»«^~
CN




m
CM
00
r\
CO
vO

CO
00
ON
*\
CM
00
i— 1



CO
e
§
"O




CM
f^.
•
0






vD
00
•
O




CN
r-l
O
CM
CO





CN
00
^J-
•V
VD








0
CO
in

m
CM





CM
I— 1
CM
f\
ON


00
r-l
CO
#x
v^
I-H
CU
o
JS
cfl

CO
J_|

'O
r-l
rj
O
PQ



f^«.
ro
•
o






ON
v£>
•
0




OO
m
ON
^
CO





~1
















•
O
r-l

CO
Cfl

d
cu
CO
4J
01
4J
CO
rl
in
r^
ON

C
e
3
i-l
O
U

o
4-1
y-N
CN
^
g
3
3
0
U

o

o
•r-l
4-1
CO
r(
CO
•r-l
0>
4-1
CO
!H
in
oo
ON
CO
cu
4-1
CO
J-J

m
oo
ON
i-H
C
CO
in
r-.
ON
]

M-l
0
01
60
cfl
^i
CU

to
CO
•1-1
O!
4J
CO
rl
o
oo
ON
                                             J-13

-------
173
3








HI
60
c
CO
J3
u
a
opulatio
P-.





4-)
r<
60
•v
4-J
•r-l
>
•M
4-J
O

4J
rt
o
o
o
•H
4-3
ca
at
t^
4J
C
O
O

in
oo
r— 1
O
oo
ON
r-l
/^.
in
y-s
^
CO
v— <
CM
£1
i— 1
td
4-1
O
H
to
PM
Pk
Pi
t-;
^
Total0
co
PM
PM
Pj
County
 •— I u~l
00 00 r-N VO vf 00
O O O O 1-1 O
r-l O CO 
f^ O r-( F-l 00
1
O •— I 1 — t— I O
<)• i-< i-< LO
o O eg m CM
!— 1 i— 1 CM t— 1 i— 1
I-(
o o » CO  60 «*1
(5 « 3 Ci P <<-l
T3 >-i O 0) O 01
^ <; CQ o Q >-!






















































.
o
o
0

P

E
Q
M
14-1
4J
3
0
4-1
C
•H
^
Q.

I-l
0)
4-1
3
a.
E
o
CJ

«•
O)

j-i
3
0
CO
co
CO
•H
O
•r-l
en
14-1
0
C
3

0)
I-i
CO

T3
C
CO

en
0)
•I-l
4-1
C
O
u

I— 1
CO
3

•H
P>
•r-l
13
Cl
•r-l
J^
rt

01
p
CO

tn
4-1
en
CO
o
0)
0
14-1

o
ON
ON
r-l
*—*•

60
C
•H
C

CO
r-l
CM

U-l
o
C
O
•1-1
en
•H
>
•r-l
P

0
'O
CO
•H
O
r— i
O
o

• •
Ol
u
I-l
3
0
t/1












































































.
ON
1
r-j

01
(—1
Xi

H

E
O

pt|
O


.
en
I-i
0
4-1
u
CO
eu

m
00
O"\.
I— 1

•o
C
to
m

ON
i—i

14-1
0

01
60
tO
J_j
0)
to

en
•r4

I-l
0
4-1
U
fO y^
v-i in
^~s
Xi
^ P
0 3
I-l r-l
60 0
u
o
00 TD
ON C
r-l CO

^^
• CO
o ^

>— i g
E
01 3
XI r-l
O
0 U
14-1
C 0
III
^ 4J
tO U
4J 3
T3
I-l O
O M
4-1 a.
u
co en
M-l T4

(~! p
4-1 0
3 4-1
o u
P 10
60 4-1

m in
r^ oo
ON ON
f— 1 r^
•O








•
^,
V4
CO
en
en
01
o
01
C

O
C

en
•r-l

4J
C
01
E
4-1
en
3
•U
CO

C
O
•r-l
4-J
CO
1— 1
3
CL
O
a.
0
en

M
CO
01

CO

u
tn
CO
o
01
1-1
0
U-l

PH
Q
>~1

C
-r-l
x:
4-1
•r-l
5

^-,
r-l
r-4
O
x:
3

en
•rH

V4
0)

C
o>
P
01
                           J-14

-------
M
H
O
§
1
ca
H
ca
tO O S-l
13 4-J O
60 CO CJ
•r-l 0) C8
J3 4J 14-1
CO CO
CD r-l OI J3
S-I 4J 4J
3 C cfl 5
4-1 O S-l O
3 -H H
<4-l 4-J in 60
cj r^
4-1 3 ON >,
O S-i i— 1 4->
4-J -i-l
O CO >
•H C -H
4J O 4J
Cfl U U
pi co




£
4-1
d
3
O
CJ

U-4
0

£j
o
•H CO
4J 0)
S-i 5-1
O U
O. CO
PM «
PM CO
pej JJ
1-3 co
ca
C! 0
•i-l O>
S-4
CO O
>. 4-1
CB
15 PM
TD PM
cfl pi
o "n
S-i
S-4
s-i oi
o a,
14-1

0)
CO
3
T3
C
cd
^







m
oo
ON
r— 1






O
OO
ON
r— 1






O
ON
ON
i— 1



0
ON
ON
n r— 4
01
60 O X-N
C 4J CM
cfl ^<
rC O
C_3 OO
o*^
1





o
00
ON
i— I






0
00
ON
•* r— 1
a)

Cfl v_>
,C 0
U P--
r_4



O
r^-
o^


4-1
C!

O
Q_}




**D O *»Q CO
r^- r^» <)• CNJ
• • • •
o o o o






oo m oo CNJ
oo oo r^ \o
• • • •
o o o o





r^ ON **o vo
m o CM ~j-
vo r>» r>» CM
•\ * ** *
O O **O **O
r-l r— 1 t—l






o 
CO cfl 3 c!
T3 S-i O 0)
<) <; pq Q



r^. vo
in VD
• •
r-l O






ON ro
CM 00
• •
1-1 O






CO 
r>

C
o
CO CO
CO S-i
i— 1 0)
60 4-1
3 4-i
O CU
Q >~i












O
•
r-4

0)
C\

0
4J

a
cu
A!
CO
4-1
0)
4J
CO
S-4
m
r**.
ON

g
^
r-l
O
U

0
4-1
X-N
CN
N — '
C
3
T— 1
O
U

14-1
0

0
•H
4-J
Cfl
S-i

CO
•H
0)
4-J
CO
S-i
in
00
ON
CO
0)
4-1
cfl
S-i

m
oo
ON
r-l
Is
cfl
in
ON
1— 1

4-1
0

0)
60
cfl
£_|
0)

CB

co
•r-l
0)
4-1
CB
S-i
O
OO
ON
                                   J-15

-------
 I
t-i
 cd
H
0
co co
a L<
o o
•H 4J
co u
co co
•1-1 14-1
0
cu J3
4-1
4J |3

O
cfi
M-I
•fj
O
5-1
bO
!>,
4-1
• H
>
•H
4J
CJ



LO
oo
ON
,—1


o
oo
ON
,—1




s~\
CM
v-^*

00
ON
1— 1


o
oo
ON
1— 1



fl
O CO
•H 5-1
4-1 O
CO 4-1
•-I 0
3 cd ^™\
&, M-I 1-1
O N_,

oo o
ON J-l
i-l 60


^-
4-1
c
3
O





 60 >4-l
cd cd 3 cl 3 M-I
t3 5-i O cU O D
O

 I


 01
 cd
H

 0
 O
 S-i
                                                                                                     cd
                                                                                                    H
                                                                                                                  H  m

                                                                                                                  3  O
                                                                                                                 r-l  4J
                                                                                                                  O  O
                                                                                                                  U  CO
                                                                                                                     M-I

                                                                                                                 "2
                                                                                                                  CJ LO
                                                                                                                  cd OO
                                                                                                                     ON
     3  LO
    i-i  r-
     O  ON
     U  i-l

  •  M-I  LW
O   O   O

.-I   4->   CO
     O   60
 CO   3   cd
 cd  T3   5-1
     O   0)
 C   5-1   >
 
-------
§
H

3
B
00
r-l
 I
cfl
H
Emissions of fugitive dust
(tons per year)
>,
4->
c
3
0
o /
T3
I—I
0)
s
Larimer
Jefferson
ci
•rH
D.
r-l
•H
O
Douglas
Denver
!-i A!
03 0)
0) a)
.-I H
U U
Boulder
Arapahoe
Adams
/ t
01 O
U o£
M QJ
3 4J
o a
t/> U
OO CN in  i~-
i #\
o\ r--
CM r~-
CN i— i iri ro 
r~~  vO c>0 O
- 1 1 CM O 1 <)• 1
m CT> i i co CM i i
vD
1 — CM CO u~l U")
oo i i n m r-i m i i
 ro ii
CO  CU Q)r-ICl)4-l 4J
Oco j-i BCS-I-IO o«ra to
MO, 3 O, -i-l us 3M)»60CU(l) W
4J O 4J M !-i l-i C 60 C 4-> 60 O
t) Cicnr-l r-4 Cial4-l S»i JJ -i-l C 1-1 Cfltfl r-l
o) OTD 3 a) cuSco tflcn >,-rJr-i t>05-i CUTS
> cfl u >T30C &C M C -i-l OJOr-icU
C8 T3O -i-l T3OI -i-l O O .CO S^-HtO M4J 4JCU
a, cs-i ^i ci-o cooo MO cdB4J bOco OJM-I
fiWbOtflOi -i-l 3 OOCS
Pco-
r^
<^
o
«t
oo
CM

O
H
                                        J-17

-------
§
w
en
PM
C/3


§
h-l

CO
CO
H
CO
g
w
 i—l CM O"i
01  i i i i
r^-
i— i
t~- O CM u-| CM CM CM
CO 1 00 r^ v£) 1 CM
LO i LO ro 1-1 i
•V »\ ».
i— 1 LO i-l
ON CM LO LO O
- vo LO
OO  *• II
CO vD
m oo vo -sf vo  OCO VOO
t^r^ioro<)- Oco i-i
r^ vo 1-1
LOOO^-II^-O v£)- i— i i— i
coi— icoovo coo <(•<)•

00
i-4
00
ON
00
vD
O
vO
i-l
i-l
\O
CM
vD
1^
i-l
CO
CN
VD
00
CM
r-~
CN
to T3 W DO
TD Qi C 1 i— 1 -H -H
C0> (1) OJi-lCflW 4-1
OW ^1 gCB-r-IO O«tO tfl
S-lCL, 3 Q,-r^o3 3oO«60, 4J -rl C 'H tfltd i-l
0) O-O 3 0) (UgtO «tO >•>•!-! i-l 00^ (UTJ
> «0 >TD0dSCViC-'-li-ira
-------
cfl
H
Emissions of fugitive dust
(tons per year)

-O
i— 1
0)
S
Larimer
Jefferson
Gilpin
Douglas
Denver
n X
cfl QJ
0) CO
i-i 1-1
u u
Boulder
Arapahoe
CO
0
CO
T3
0
v. County
Source ^v
category >^
LO o LO oo co uo CM 1-1 co
CM 00 CT. O OO CNCN C^
VO CM CM i— 1 OO vO r~
•\ ft
co r~~
CM r~
CTi t— 1 O ^O v£JO COLO
CTi mi— 1 ^D CT\ CO i— ( i— I
i— i i in CM i—< LO vo t— i
CM LO r- 4
I— I I— 1
•-i CM OO co O  <}• O ^D CO O O 1
 r^
r* r\ r\ n
O i-l VD i— 1
1— 1
CM
CO
v£)
OO
o
F— 1
o
OO
-*
o
CO
00
1-)
CM
*t
r— 1
1— 1
LO
o
CO
•t
LO
F-l
1-1
cr\
oo
r>
CO
CM
m
CO
»1
v£>
CO
1— 1
ON
M
LO
CO
r-l
r^
v£>
1— 1
CN
 0) (Ui-lcfl4J 4J
OC8 >-i pctj-r-lu o«co co
ViQ. 3 O.-HO3 360«0cucu -U
4J 04-)W!-i MCOOCWbO 0
ID CiCOi-( r-t CCU4J >,4J'HC!-i-l COtfl i-l
0) OiD 3 (U CU0CO cflco >-,-Hr-i 60S-I (UTS
> coo >rapC|5Ci-iC'f-icuoi-icui— i
tdT3O'r4faa)'^ooFco W-HCO ^4J4J
-------
 I



 0)
I—I


 cd

Emissions of fugitive dust
(tons per year)
13
r-i
cu
S
Larimer
Jefferson
c
•r-i
a
r-l
•H
o
CO
cfl
1— t
M
0
p
Denver
Clear
Creek
Boulder
a)
o
•s
a
cd
Vi
v County
Source X.
category >^
m o m co oo o CM 1-1 co
CM CN CTi CO OO t^-CN CTi
>i> co CM i— i o i — t*»
#\ *\ *»
oo r-» 1-1
CM r~
o r-4 co co ^OO COLO
O> U"> »-D O «3" CO I— 1 r-l
i— i i in CM CTN r^ vo r-i
CN IT)
i— 1 t— 1
T— i oo oo r^ m vo-cf v£>
r-~ oo CM ^-i o r-» vo
 CM i
« ~ « i
m CM i— i
VD CM CO CO r-l
vO O
ON 1 1 —i i i i-< i i
#\
vD
co vo oo 1-1 m
co i i 1-1 m -l CO
co i— i vo  csm
r-IC^OO^OVO OCO VOO
a>mmco<|- oco r-t
•\ * *v
r~ vr> •— i
OOint-IOCM OO<|- CMO
ooocMOOoo mo t-i
VO CM OO CM O r-l r-l
n * •*
VO i— 1 i— 1
VOCOOOCMC^ OOO ~d"
S
cr>
O
i— i
O
CM
-d-
•\
O
CO
CO
m
&
«*
o
r-l
m
r^
CO
•\
m
r-l
0
C^
m
•V
o-
vD
-J-
CTi
M
vD
CO
O
t-i
#\
r^
cr\
CM
 0) CUr-(tfljJ 4J
on) !-i gtfl-i-iu o co co
S-iCL. 3 O. T-I O3 3tJO"OOcUQ) W
4-1 o W V-i ^J I-iCoOC-PbO O
•a Ccoi-i r-i ciai-iJ >i-u-i-iC''-< tdcti t-i
a) OT3 3 cu cuScn coco >,-i-ii-i oo^i CUT)
> tfl 0 >T3@d > C Wd'-H CUOr-ICUr-4
CdT3O-HT3CU-r-IOO.no Jj-r-ICfl H4J4JCU 03
d. C J-i M di3 cnou bOo cdgw Men JJM-I 4-1
dcfloonicu -1-13 oofflo
izjco^^oi trio' 
-------
                       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
                    L-15

-------
                                                                 O    O    I*
                                                                                                      o    o
                                                                                                                  o    o
                                                                             in
                                                                                         o     o
                                                                                                                  o    o    o
                                  o    |O     o    o    o
                                        oo                :
                                                                       o
                                                                       CM
                                                                                          o     o
                                                                          o    o    o    o
a
crt
O    CM     Ot>     O    !O
      *0     ••4'          '
      •o     in
      O^     *O          '
                                  0,0     ooo
                              ~l    O

                              o    o
                              in    CM
                                     in
                                     00
                                                                             o
                  -I    CM
                  00
                  •t
                  03
                                                                                         cn
            00
            CM
            CM
            CO
      CM    •-!
                                                              00

                                                              •0
                                                              -O
                                                                                                            O    O    O    O
                                                             o
                                                             CM
                                                             -O
                                           00    P-l
                                                 SCO
                                                 in
                                           •*    CO
                                           •t    CO
                                    in    o
                                    r»
                                    in
                                    •*
                                    CM
                                  O    O     O    O    00


                                                     in    CM
                               O    CM

                               in    m

                               ?    co
                                                     in
                                  o     oo    in    o
                                  ,»-i     4-    o    i-i
                                  o     •*    co    *••
                                  *     -t    r--    o
             O    r-l
                   03
                   co
                   co
                        ,0
                         00
                         CM
                         CM
                  C
                  O
                  m
                  in
                        oo    in
o    co    in
      CM    O"
      •4-    CM
      r-    co
      s0    *O
                  o    co
                  in    oo
                  a    >-i
                  O    CM
                  co    -O
a    o    o


in
                                                                                                            o    o    o    o
                                                                          o    o    o    o
 (0


 i


 0)
00
CM
CM
                                               s
CO    ->
CM    in
o    co
r-    in
•o
                   o

                   r*
                   O
                        r-     oo    o

                        o     i-
oo    o    o
CO    >C
-H    O
                                                                                    CO
                                                                                    CO
in
CO
o.
                                                                                                            o    o    o    o
                               o
                               CM
                               -O
                               O
                               CM
^-    O    O    O    O    O


O
O
CM
 (0
 H
 •O
 CO
                                   co
                         O    CM    O>
                               "*    •<•
                               CM    "I

                               •O
                  CM
                  CM
                  CM
            r-
            co
      J
      in
                                                                                                            o    o    o    o
                                                                 o    r-    o<

                                                                       o    P
                                                                       ^K   i »C
                                                  o-
                                                  in
                                                  CM
                                                              •o
                                                              co
                                                                                                            o    o    o    o
                                   o   lo    o    o    >o
                             tii
                             ui
                             Cf.
                             UL
                                                                 ;O    O    10




                                                                       CM
                                                                                    OOO
                                                                             I      I
                                                                                                            o    lo    o    o
                                                                                    o    o    c    o    o    o
                                                                        L-16

-------








CM
£
1— 1
s

C/3
<3
§5
CO
&J
2
PL|
§

jg
^
,J
1— 1

p
w
1
w
^^

^i**^

1
J
r-l
JO
CO
H










h















































?
X
«u


B
n
-i
3
3
N

M
0




0



O


o




o

o


o


0


o


o



o



3


3


ft
M
^
^
1
^
H
0
0

»

9



9


O




O

9


-t
*
\
M
*t
9


9


9



9



9


9

9


9


^
^
ft
^

/>
^
0

o


0




o

o


N
N
9-
4)
ft
O


0


o



o



3


9

9


9


9




N
ft
ft

O


O




o

ta.
•o
9-
»•
M
Ift
B
0


o


o



o



3


3

9


9


9




o


o

9


O


O




N <^
•4 jlft
*
A
ro
ft
l>
M

O
$
*


9

O


O


o


o


o



o



ft)

ift
N
O
Ift
Ift
O




o

0


o


o


o


o



o



9


O

9


9


O




o



Ift
•4
ft
Ift

O




o

o


o


0


0


ft
k»
N
N

O



5
9
B
0

O


O


O




o



o


0




o

o


o


o


o


3

1
N
Ift
1
3
N
9


9

9


9


O




O



O


no
^
^
ft

o
M
ft

0


O


o
<0
3
*
Ift
3
•O
m

3
CO

o



9


9

9


9


9




9



O


O




O

o


o


o


o


o



0



3


3

3


O


3




O



>
fl
3
Ift
O
ft
M
N

*
D
Ift

w
yw
«
ft
9


O


9


0



O



                 9   3
                       o  o
                       o  o
                       o  o
                       9  O
                       O  O
                       O  O
L-17

-------








CM
r^
c^
l-<

g
n
CO
H
g
H
3

>*
§
S
Pi
PH
55
O

C_|
A
[>
N_i
t-1"
. T
h- 1
i i
<
P
H
O
3
w
>

tH
M
fH
in
fH
h-
«*•
fH


IM
N

fH
o



o


o


f-
0
00


fH
fH
•O
•o

4.
^
in
N
CO
N
«fr
in
o
fH


O


o



o-
$
•fr
o.
o
CO
o

CM
in


o


o



CM
fH
CO
in
in
CO
3
o




o

o


0


8
ft


0


n
tH
fH

*
|<)
•0
N

*
^*
CO
PO

o
00
N
CO
in
•»•
CO
CO
CO


g!
CO
in


CO
ID

5
fH
m
iw
0
in
fH
00
fH
CM
CO
fH
0
CO
IM
fH
•O
fH

fH
^
s
fH
§
fH
fH
CO
fH
IM
^
IM
CO
CO
C*
IM



*»
M
5
fH
•O
co
§
fH
£
M
**0

M
5
IM
O

f»
CM


O

%
t\

o
co
N
•O
g
M
CM

^
oo
o

o-
fH
o
o
0
fH
<*•
N

IM
CO
00
o
o>
•o
CM
O
N
0^
CO
fH
fH
CO
in
co
*
fH

CO
fH
f-
5
CM
in
fH
fH
0


CM
•O

0




O

o


o


o



CM
CO
00
IM
CO

*

1




I
o
fH
*
I
fH

r-

-------
VERAGE DAILY VMT ON MINOR ARTERIALS IN 1972
 —1
in -c
r- oo
sO ro
nj in
IN
in (si
r- •»
in ro
in -o
in ro
i O
.-4 CO
CM CO
ro *0
(SI ?
sO O
0 0
oo in
ro o
"*
O ro
O -*
r-t

0 0





(SJ *f>
r-J ro
ro r\l
«• ^
(V O
c
p—
ro
•* C
o
in
o
in
0
o>

C
r-j


O-
^>
(Ni

^
O
ro
~*
c


O 0
•O **
m oo
*t o
o *
~* cc
in o>
r^ INJ
m o.
•+ m
CO r-4
Is- in
00 O
o* 
r-4 (SI
rr>, f-
in r-
o- in
0- (SI
m o
ro in
-J- ro
cc O
•4- in
•-< ro
ro ro
(SJ i-l
CO CO
o ^o
ro -^
CO


r\j ro
-* ~t
•O LTl
"^ -O
O ro
oj
r>
r-
c o


-t
ro
f-
•O
00
 o
ro
in
-« .0
O ~>
f- in
co O
Q\ ^
C (SI
m ro
in •o
•-> IM
in ro
IH in
(M -4
ro in
ro Is-
r-l O
ro o
m »-
ro -O
(M -,
co in
-4 O
^ 0.
•*J U^
•r^ t\i
-> •*
LPl O
m



0 C
-0
ro
-t
O O
»->4
>}•
cu
o c


O O O O t r-4
f- >o in o
in (•- 4- -t
o r> o f- o o
<-« oo in cc.
ro rg * r-i
ro h- ro »o
N -H isi a c o
tM in o o
cc ro m a
r> (*• ^ t^
r-4 r-4
ro ro .4- o O oo
ro ro ro m
m f- co rsj
(SI INJ
ro o r*- •"•< O ^~
ro in -o t~ in in
ro -o in 03 *o
ro in in (si
(M
cc rg oo •-! o o
ON i£t ^^ fO ^
CT< r- co ro
-* r-
'-'
o in o o o o
in
in
•-1


(vj CO C O O C
r- h-
m r\j
r—4
0 O O O O O



c o o o o o


L-19

-------
CN


ON
I—I



5


CO


o
H
o
o

§
H
>-<

ri
<3
n


o
in


in
— i
o
en

co
0
r~

o



o



o

o

-o
CM
in
00
•fr
en

•fr
in
en
i-i
in
oc
•O
CM
in
o»
o
en

•o
in
f»
in

CM

^4
.H

m

in
en

5
fw
oo

O



o



c



o

o

^
f)
ot
r-

lA
•M
fM
en
fM
m
o

M
p»
CM
CM

fM
in
^
o
CM
cn
i-i
evi
•O
»•*
•fr

in
**3
r*«
(M

£
•o
en

en
CM
en

en
^
en

^.
f>


o

O

^
CM
O
O



O



en
O
o
IA
1-4
1A
•^
N
f>

O
CM
fM
m
f-4
^
ff)
fl
t_|
^
(SJ
^
•fr
00

••H
in
r-l
«v(

03
•O
en
CM

in
in
I-4
O



o

00
•0

m
in
-
o



o



•fr
fe»

0^
a
r-

f>
f>
1-
•*

0
fM

fM

CM
O
in
o
"•*
CM
0
CM
en
eg
0
(M
O
o
f-
o

•fr
o



m

0

<0
»4
•0
in
-o
fM
•0
O



?
in
lf\

r4
|-
^4
CM
r4
f-
m
00
en
^3
r-

^
CO
CM
•O
>4
m
in

c*
•-H
•C
^
•M
st
(M
^
•*

rg
oo
in
•fl
en
0



^.
^
r-
en
•fr

O

CM
ffl
•fr
O
r*
•4
m
00
00
^
N
O
•fr
eo
r-
oo
fn
(M
CM

r-
en
fM
^.
•A
in
CM
fM
m
in
o
in
r4
-fr
co
co
en
•*
CM
in
CM
*
o



o



0

0

in
«^
o
r4
•0
o
m
"*
m
r»
•fr
r4
in
•fr
•o
in
N
en
fM
03
CM
o
fM
••4
— 1
^
0

en
f>
r~
o
o

5
f/i
^
"^
o
o
en
en
c



o



00
00
*4
00
•o
(M
•O
«^
•O
IM
f>
^4
fl
f>
<^
IA
CM
«^
in


00
o
in

fM
•0
^
•^
•fr
(O
CM
O
r-

^.
t-
1H
CM

0
in
1-4
CM

O



O



C



o

•o

0
•fr
(M
r^
•o
(M

00
00
fM

CM
•0
O

O
CM


9^
n»
in
in
"*
•o
en
O
O
"^
o
CO
03
sO

O
oc
o


en
o
in
"*
o



o



in
m
fM
*
r»
f*.
N
in

^

•o
>fr
at

CM
fM
CM

f>


O
in
en
•o

f-4
m
0


a
in
o*
*4

a
r~
»4
f«l

0.
a.


0



0



_
in
*

in
oo
«4
•fr

fM

—
m


•fr
**
o




o




OS
o



CM
O
O
••4

5
en
rj

o



c



0



o

o

0


in



(M

CM

s
fM
in
CM



tn
CM



^
CM



O




C



O



o



o



o

o

o


o



o



0

o




o




o




o




0



o



o



c



                   _)
                   o
                                                                             o   o   o   o
                                                   L-20

-------
                           O    O   O   O   O    O
                                                          ON    .-4
                                                                    OOr-OfHOOO
                                                                              in         co
                           O    O    O   O   O    O    -H
                                                          m
co   o   o   rg    o    o    O
rg        in   >4-
 O
 H
 O
 w
 53

 §
 O
§
H
O



§
>*

rf
<;
P

w
Q
§
m


 i


 cu
 03

H


rg
ON
p-

o



•t
rA



o



o




o




ON
NO
o
*"*
m
NO


rg
-O
fH
f-4

^
C
CO
CO
c



o




O



o



PA
o
*t


^.
ON
fH

m
fH
in
r\j

»-(
ON
ON
rg

^
c


r--
o
-t

o
en
in
in

o



o



o




O



^
ON
rg

in
^
rg


p.
0>


__,
in
oo
PA

o
oo
PA
PA
f-4
m
-t

f-4
p-

•"*

m
NO



>o
M
fH
*
CO
Nt

~
*
ON
fH


O



o



•o
PA
O


rg
rg
f-4
*4
in
•o
Nt
r-

o
0
^
f-4
**
r.
in
o
o
fH
O
in
Nt

p-




0



^
rg


C




o



NO
,^-
O*
rj
a
o
in
p»

I-
o>

^
^
in
rg
in

ON
S^
^>
fC\
*
j.
Qs
rg
in
^
O>
m

o
in
-O
>f

-O
(Tl
m
(M
0-
xj-
Lfl

O




O



N
NO
rg

^
^
tA
\e\

00
fw
4^
f"
ON
O>
r-
p-

c-i
00
n
p~
^
o
o^
fH
co
M

0<

^
in
rg
NO
1-1
rg
o
CO

^
0
fw
in
in

NO
in
m
fH
rg
PA
rf\
rg
fH
^
ON
in
ON

0
P-
rg
2
«t
03
O
C
rg
o
NO
m
CO

&-
on
ON
Nt
C



-c
tn
(N~l
r-
rg
0>
ON
00
00
CO
f-4
ON
in
oo
rg
ph.
fH
rg
^
fH
p*.
fH
O
in
p»
rg
rg
in
p-
>o
0
Nt
in
co
in
^
in
P-
fH
rg
in
rg
fH
fH
rg
o
rg
fH
"^
C
fH
m
m
p-
c
m
in

f>
CP)
oc

fH
ON
ff\
•O
rA
PA
fH
pk
fH
fH
P-
fH
^
0^
PA
O
oo
rg
fH
ff\
PA
in
rg
0
rg
-t
2
-o
O
fH
pg
IM
0
CO
P.
PA
1-1
in
CO
CO
in
CO
fH
ON
fH
p.
t""1
P-
fH


PA
ON
fH

O>
rg
in
in
*
rg
NO
00

^
NO
rg
rg
CO
co
CO
fH
rg
O
rg
ON
NO
fH
in
ON
Nt
in
0"
ff\
GO
NO
i— I
ir\

f^
h-
i—*
UN
fr
(*}
m
o



0




o



ON
NO
O>

m
o
CO
00

rt
PA
O>
in
PA

NO
"*
ON
t>
in
co
o
ON
rg
-t
-1
rg
CO
fH
Nt

0-
rg
fH

O



o




o



NO
^
rg

rA
in

•t

in
Nt
00

^
fH
09
p»

^
PA
O

rg
O
NO
-t
rg
NO
oc
1

l
>t
NO


ffl
P-
rg

CM
o
fH

O


^.

PA O
in
NO

r- o
p»
pH

ON O
^
ON


•* O
00
rg
PA
rg rg
•H rg
in o
ON in

CO O
rg
•t
in
'"'
O> 0
NO >H
ON NO
NO
PA ON
in PA
rg £

CO ON
PN| rg
PA
fH

0 0



O 0



0 0




o o



o o



0 0




0 0



0 0




o o




O 0



O O-
in


0 -t
on
rg
fH

O O



o o



0 0


                     o
                     LU

                     O
                           O    C    ft    *^   O   O    O
                                     O^    f>
                                     m    co
                                                            L-21

-------
OJ
                           oooooooooooooooo
                           OOOOOOOOOOOOOOOO
                           oooooooooooooooo
                           oooooooooooooooo
                           oooooooooooooooo
M


W
                           OOOOQOOOOOOGOOOO
                           OOOOOOlAOO-*COOOOO
                                                          •o              o
                                                          in              m
3
M

-------
OOOOOOCO^-^rOcOOOOO
                                             •*    O    0    9*
                                                                        ro    -O
                                                                        t>oo
                                                                   (ft   r*
                                                                   co   o»
(N
CTv
,-1
23
H

CO
M
w
H
§

0"O(si
ro co .$• o
*-• *• ro tsi
ro a ci ro in
ro Is* •— 4 oo r>
m
ooostcoinoo
c. ><• ro *o in
sO ^ in rA r*-
in in r\i o
<-> « ro


OOOCOG-tO-
in -o
^ ^
(SI -t
•"*
O^OOOCO^CO
ro ro -c
ro >t f>
ro *$• (si
^4 i-4

Off-OOOO—irM
ro O- ro
CO ^H ^•
^ f\i ro
r-t *-4

O»-tcC'C o^>r>
03 C •*
C — ro
-H I-- o
OC OOOOJ-G
O* CO
in in
(SI
oocoooco
V

CO
1-4

CT
in
(SI
in
«— t

c



o



0



O 0


0 O



* 0
a
-t
m


o o
*-4
O
r-


(Sl o
o
(SI
CF
""
o o






o o




0 o
sj-
(f\
rH

CM O
n
(NJ
*C


r^ o
>-4
•^
(SI
o o



C 0



o o o o


o o o o



o o o o




Is- CO O O
0s r>
ro (si
-o ro


O* 0^ O O
O> ro
in r-i
in ro
*H «-(
(SI >}• O O
«J- !f\
4- 0
-o



ro o o o
r^
r^
CJ

0^-400
-O (SI O
~O -1


O 0 C O





0 0 C C



o o c o



o o o o



                                L-?.3

-------
IB
EH











































































U)
UJ
cr:
u_


00
r-
00
0-
ro
in
•o
00
i-i
O




o





o





o





•o
o
c
ro
(M
1—4
o





o





fsj
-4-
ro



^
in
ro
C\J
o
c




o




o







o



o
p^
^.
,$•
**
—
in
-o
0s
*"'
0





o





c





ro
O
*o
rsi
•O
<-<
O





o





(V
•r
rs!
ro
>O
—>
C




o




c.




o







0



o




0
0

o
l-l
ro
•C
-o
!>•
ro

in
in
in
in
1—4

0





^.
in
o
ro
(M

rsi
rsi
•C
•t-
oo
ro
cy\
>0
ro
ro
on
O
*c
r-l
C





c





o




c




o




c







o



o




o




o





r>
•o
00
(M
ro
I-H
co
in
^
-0
0
1—4
in
CO
o
rsj
r~
«!•
i-i
rsi
-O
o
1—4
1-4
ro
CO
r-

in
r-i
o-
rsi
ro
o-


C




O




O




C







a

*
^
^0
•O
1^
in
in
ro
O

o
rsi
^.
ro
m
-O
in
^o
c
^>
-o
fv.
ro
rsi
r>
o
o

(•»

^.
r-
1-4
ro
*— 4
(M
cn
ro
ro
ro
in
f— 4
(M
r>
f— i
C
rsi
a
ro
ro
c
r>j
O





>o
o
-*•
a-
^

rsi
xt
o
*-4
0
•*
(M
f^-
-t
o
rf"p
m
ro
CO
rsi




O



O




1^
•o
0

o
0





o
o
r«»
r1*
ro

o





(M
r--
m
in
rsi
in
c
N
f*.
ro
in
ro
CO
ro
O
•£>
•C
rsj
r>
cn
1—4
f-
r>-
ro
ro
r^.
^>
^_
ro
0
f-4
Qs
f^.
2
^
CO
ff*
•—4
rsi
O







o



o




•o
CM

ff\
i-l
O





ro
r\i
«^
^
r--

r-
r+
0
r-
ro
ro
^
^
0
t>
•0
•t
o





o





ro
IM
ro
in
o

f-
_H
a
^>
-o
•ft
r>
m
»^
m
c




o







o



o




03
00
O
O
00
<0
^
^f
(M
1-4
1-4
00
^
r-
ro
i— i
•*•
00
r-
^
fw
oo
•-1
^
^
f-
^
ro
«t
^
ro
r*-
-J-
a-
rsi
O-
ro
in
cc
O
IM
-0
-o
CD
1—4
*f
rsi
^.
1—4
CC
^
IM
ro
CO
vO
c
^
c




o







0



o




o




ro
•O
O
in
in

o
in
in
£
ro
O





O





ro
•0
-o
JD
in
(M
C





O





_|
I— 1
O
r>
m
sC
1—4
1— 1
^*
01
O




o







o



o




o




^
^
in
o*
^^
(M
O





O





0





-t
1-4
ro
in
1-4
l-l
O





o





CM
-t
O*1
cc
ro
c




o




c







o



0




o




in
^4
o*
•*•


^
fi
fO
00

-0
ro
^~
•"
^
rsi
0-
in
IM
i— i
^3
I— 4
O
—• 1
CO

0
*o
xC
s^1
rsj
O




o




o







o



o




o




^
^
^
rsi
r»

o





o





o





0





f-
vf
00
l-l
OJ

rs)
O
l-H
CC


o




o




o




0





                                       L-24

-------
                         OOOOOOOOOOOOOOOOO
                         oooooooooooooooo
o
o
o
CM
                         oooooocooooooooo
                         oooooooooooooooo
w
tH

w
«
H

a
oooooooooooooooo
                         ooooooocoooooooo
Pd
P5
PM
ooooococoooooooo
                         ooooooooc    ooooooo
                         oooooooiooooooooo
                                                           •o
a
w
                         oooooooooooooooo
                         ooocoooooooooooc
                         ococcoooocoocooc
                         OCOCOOOCO—iCOOOCO
                              M                                      r-
                              <-t                                      -fl
                         oc    oooooocccooooo
                         ococooooooecoooc
                    (X
                    a.

                    X
                                                        L-25

-------
CO
erf
w
H
M

Crf

PH

w
 I


rJ
                 or
                 •a
                 a:
                 a


o


o



0
co
M5

m
o


o





c





o





0




o




ro
C
CO
ro
CM
C




o




o




o




o


CM
CO
CO
CM

CO
r-

P^.
CO
CO
co
0
CO
CM

u.
in


^.
FH
in
0
FH

FH
Ch
in
in
s4-

FH
IX.
CM
0
ro
r-
o

00
CO
f—
m
FH
ro
0
co
^>
*+•
r^
CM
^
f^
o
•O

O




cn
00
O


O


O



^
in
CO
0
CO
o
in
-o
0





c
CM
CM
•^
FH

CM
^
«—4
r\j
f^

-fr
cc
f--
*o
fO
in
i*.
•o
t— t
CO
M->
er
CO
cr
••*
•O
I— •
CO
FH
•*
_,
r- 4
*^-
CM
CO
o




0




o


o



o




CM
r-
o
co
o
in
CO
co


*o
FH
o
CO
FH

CO
in
CM
*$•
•O

co
in
o
•o
co
^.
r-
CM
0-
en
(0
-O
sO
>o
(M
j.
>^
CM
CO
•fr
^
sO
FH
CO
CO
c




c




o


o



0




o


t>
CO
»*•
fit
vO

-o
o
X
r-


(^
CO
0

•o

CM
o
a
CM
O-
C
C

!>.
0-
CM
^
CO
c

sj-
t^
a.
sj-
ro
^
ro
sT
ff\
•*
C




C




o


o



o




o


o
NO
in
co


CO
•*•
^p
a


CM
•a

m
^

co
o

CM
CM
-O
CM
in
r^
2
(_)
rj
r-
cr
in
CO
ai
CO

t>
c
ro
(M
0
r-
o




0




o


^
FH
in
o
rt
^.
CO
co
CO

^
f^
CO
o
CM
CM
r-
m
o
CO
r~
CM
^>
CO
in
2
^
>!•
m
^j-
CO
CO
{O
CO
l^~
F-l
c




0




c


o
CO
-o
co
CM
CO
•o
in
in
—
t^
tj»
fO
r-
o
CM
•*
CO
o
CM
fM
CM

>0
co
-O
FH
CO
CM
CO
^>
l>-
ro
0
in
CO
CM

00
•*
CM
f^
in
a
-l-
sO
~c
ON
CO
rt
J.
C sj
-n
c
**
r
o-
fH
^
**
^
CJs
r-4
i—4

in
m
0


a
o
s
«0
•o
CO
in
cc
•o

5
o
r--
CO
CO
CO
in
CM
o

co
•-1
co
1-4
in
CM
O
C^
CO
*o
*o
o
IM
>t
co
in
in
0
r-
0
CO
IT.
FH
tn
o
cn
CO
FH
*
0
cn
o\
CO
^
^
in
rH
CM
•"•
IM
in
CO
-c
CM
c




O


CO
in
1
CO
in
^
00
in
.fr
o
i
CO
CO
co
o
FH
FH
CM
f-

f-
^>
CM
CM
•O
in
^
o
co
**
O
FH
o
CO
o
tr>
0
f-

CM
^
(^«
co
^4-
CM
j.
sj1
O
ro
1-1
r-
(0
IT1
J5

O




O




o


__,
•o
o
-o
CO
o
r-
in
FH
o
in
2
CO
t-H
0
^
*Q
O
**•

CM
0
co
t-
o
•-1
CO
CO
FH
CM
l>-

^.
^
c

•4-
CM
in
r-j

c




c




o


CO
CO
in
«o
CO
co
t>
o>
"*
CM
ro
(>-
O
(>•
FH
o\
CO

0
CO
t~
-o
a

o
FH
C
CM
FH
-<
,«.
co
N
^
co
CO
CM
O
FH
*"
CO
in
CO
•ft
o
_,
c
•A
(M

C




C




o




o


vC
•o
o

in
f^
o

CO
^.
o
CO
o
CO
^
CO
m
FH
CO

-c
f>
^
CM
O
•*
•O
CO
^
o\
CM

0
CM

v£)
•o
o
CO
^4-
CO
o
0
•n
in
r^4
F-l
CO
-o
CO
FH
CM
C




o




o




in
CO
g
(M
^
-O
FH
in
^
CM

in
>M
in
c>
O
oo
FH
co
o
FH
o
FH

CO
-t
•^1
CM
CO

in
in
in
CO
FH

CO
O
r-
CM
*t
^
in
>^
co
in
•c
in
m
»4-
in
CM
FH
CM
vO

c




o




o




in

-o

CM

O
\4-
o
FH


in
•Q
FH
CO


CM
^
•^
FH


,4.
CM
CM
C
•f
O
CM
-0
st

CM
CM
O
in
•0
o




o




o




o




o


o



o




o


o





o





c





^.
^
r-
CM
CM
O




-0
CO
CO
cr
FH
o




o




c




o


                                              L-26

-------
                        o    o
                                                          rOOOOOOOOO
O
o
o
CNI
w
>>

w
w
H
tf
O
13
§
>*

ri
 -0
0s Ch
r- co
(M CO
•4- -<
r- o
O

in
(SI
•t r-
F- CO

(SI
o

0


o



o




o




rH
(SI
ro
ro

•t
^>
co
0
*~*
m
•4
oo
(SJ

-o
cn
ro
(SJ

-O

CO
CO
1-1
0




CO
IM
or
(SI
o
cr



^
1-4
in
ro
oo
ro

O
in
r-

,_
f>»
ISJ
in

f-4
>^
CO


^
in
0
in

in
*-
r-
r-
•£>
v-l
•~*
4
ro
C


C



o


-t
-t
ro
^p
t^
in
o


•c
rj>
O
^
^
m
a
m

^
ro
in
r>
(SI
ro
o
(SI
ps.
ro
*
f^.
a
a.
a.
O
•0
CO
in
ro
0




o




^.
ro
-O
st

0



r-j
r-
cn


0



O


o



(SI
in
^

-0
^
^o
>J3
ro

O
(SI
ro
f-«

^
CO
-o
(SI
(SI
„,
0

-o
•4-
1SI
o
1— 1
r-
ro
m
CO
in
ro

o




r-
r~
CO
ro

0



C




o



o


o>
CO
•o

CO
ro
fMt
O
CM
(SI
co
in
CO

co
<*•
>o
(SI
in
00
00
o
•O
rH
1— 1
•O
r-
in
r-
*
-0
r~
O
ro
cr>
o
h-
>j-
«n
'-
,_,
>O
1— i
a.

c



c




O



O


O



CM
CO
o

"*
r-
i— i
r-
03
"~l
00
c
in
•4-
(SI
CO
^
f>
in
rt
^
r-
•4
i— i
r-
»
cn
>^-
^O

o




^
PI
00
m
r-
o



o




o



o


r-
f».
CO

ro
pH


^
•^
CO
1^

o




,».
co
f-t
(SJ
ro
ON
-O
ON
r-
•^
CO
•o
•— t


p-
•o
(NJ
QN
1~4
C



c




0



o


^
CO
pk.
00
co
00

-o
fvj
—
p-l
ro


-o
•o
o
fjN
1-
-0
-0
•o
^>
CM
^
in
(SI
(SJ

in
*o
00


sO
!—4
ON


-O
ro
m
ro

o



o




0



o


CO
^
a
CO
CO

o.
CO

a
ro



rsi

in
(SI

^
ON
CO
f-4
(M
^
ro
CM
ou

(SJ
0
(M


O




O




C



o




o



O


0



C




0




0




o




•4
ro
rM
ro

in
*j-
ro
-4

si-
(\i
in


o




o



o


                   DC:
                   <
                   lW-1

                   X
                                                       •L-27

-------
OoOOO>O«O<4>*49>4'OOOOOO
                             -«    o    o    in    a>
                                   m    o    m    —4
                                         IN
O    ^    (*l    CC     ^
      f-4    O    rg     MS
      oo    m
ooooo-oinooo
                             o    o
                             co    r-
                             f\    IA
^»^COOOOO*fViO*Oi^OOlNOOOO
IN          H    m    >o    o
•4-          o         -i    <

H
E

3

U)
g
H
U
W
J
iJ
0
o
a
5

^_t

>
1
i-j
t— i
<^
Q
w
C3
1
w

O
0

03
-*

-C
r-l
4*1
•O
•*
C





r-
c


m
•o
Q\


si-
f-4
f^

O



•o
rvj
in
o>

o
5
in


•4-
in
o
00

,$.
CO
0^
o
f-4

in
o
-o
CO
in
^
^>
0
CO
f-4

»4
r-


s*-
xj"
r~


o



o



o

o

o



m
CO
o

CO
-o
o
rg
f-4

in
•o
o
-4-

0
0s
^
vO
rg

•>
£
h-

f^
•o


t-4
IN
•O
03
"-1
n
f^.
o
,^
-t

C)
CO
-t
rj

>4;
in
CO

gs
f-4
•0



Q*
C*
f-
f-

j.
a


in
•0


fH
|Y>
in
B.
ro

•O
»o
ro
i>
»t

(TJ
r*^
m
t?i
m
-t
m
in
f-4
in

.n
in
•£
t£
"-
^
•O
^~
fk..
-H
a
ro
^j-
in
ro

f»»
•*
f-
0""
40364

o
•o
in

IN
in
»*

^
CO
f-4

o-
o-
•o

•*•

o
^>
in
in
ro
f-i
CO
-o
O


0
o
rg
in
in
.n
•0
CTj
CM
•4-

a

IT
m
0
£
-o
o
f-
m

IN
O
•O
ff\

*M
^-
f-4
0

c
co
Kl
0s
•0

sO
p^
fw
in
•*
•o
m
ro
4N
-t

f^
-4
00
•*
in
^j-
P^
fs.
^
J.
o
o>

o



o

IN
»
00

m
IN
r-
•H

CO
•O
f-
in

r-
•4-

00


co
•4-
*
in
in
0-
•t
00
^
•^

in
0
m
m
o
»H
•O
n

^
o^
t^i
**
^
•c
f-l
•4-
O

•0
in

o
fO
m
fO

00
00
•O
o
•N

O-
00
1—4



f^
>t
en
r-

o
IN

O
f-4

Kl
O
in

O




^
0
f— 4

m
r-


0

•H

m
o
00
0
(*l

t^4
f— 4
oo

•o
oo
,-4
4^.
rt

in
«— 4
r-H
vO
4T>
IN

^
O
^4-

tr\
CC
M?
—
O




o



o



c

o

c



o
fSJ
-0

0-
a
i^.
a


a
i*)
•4-
O*

»0
o
f»»
l>


m
o-
•o

m
^
f<^
*^
•"
0



o



o

                                    L-28

-------
C8

H
0



0


o
in
m
1-1
o



in
o
in

CM

fH


0




o




•o
o
co
o
to

o
•4"

IM
m
l-
fi

c



c



o



o


0



o


o



o



CM
f«.
^

•O

*o


^.
0x
^3
f^.

O
rd
•0
-c
fH
o
in
.4-
CM
CM
(M
m
fo
»— i
o
o
-4-
*

O



C



^.



C'


o



o


•o



o
IX
0.
fH
•o
4-
fH

m
•a
•H


i»-

CM
^

in
4-

m
fH
0
0
*
•H
sC

s$-
fH

|
CO
f-
fH

CM
r--
m

en
fO
i^-
O
fH
CO
I/I
0
o
fH
J3
r-
ir
O



o


0



o



o
•fr
fH
IM
fH
.fr
fO
CM

4.
[*•
{\|
tf>

IT
,^-
(J*
00

CM
^
*$•
N

f*~.
O^
CO
1— 1
^
•4-
(M


C



(M
ro
-t

O



c


o



t
*t

(M
••4
f>m

lf\
^
r*j
•4

in

fH
O
o
in

o
o
o
0
'-'
CO
in
m
•o
in
i>-
CO
OJ
fH
fH
-C
•0
fH
(M
in
O^
,$•

o
CM
co
^
-t

fM
CO
•^
fO
00
CM
CM

0
^
CM
0

CM
0

r-
o

|H
l/te
fH
00

-t
fH
0
r-

c
o
o
CM
CC
fH
in
o
^
CD
in
ro
^
c



^
f^
in
ir
c


0



t
f«»
•*"
CM
c*>
^f
o
—
o
in
-o
•o
o

00
fH
O
•o
^^1
CM
CM
C
m
o
•o
CM
O
*^-
ffl
CO
CM
CO
in
fH
m
in
r-
in
CO
^
m

>o
IT
fH
r-
in
fH
fH
O
rH
(*"1
CO
CO
o
s4-
0
c


0



r-
00
^

0
CM
in
m
IM
fH
fH
""
-O
ro
fH
-
^
CO
co
•o
•^
^
-J-
in
in
"*
CM
O
CM
in
CM
CO
00
03
co
t-
f>
in
o
CO
CO
fO
o
f>
^
-t
CO
o
IM
rH
-0
o-
CJ
in
^
CM
CO
CO
o


o



<0
^
^
^
in
Qs
fH
in
o
o
CM
fH
o>
l/h
in
fH
sO
IH
O
0
•"*
in
o
f^
o
CM
j.
CO

o
fH
-t
CO
CM
f>
m
^~
fM
O
fH
CO
CO
o^
(O
fH
r~
o
(M
-O
O



c



0


IM
co
^
""*
K
fH

0

f^.

0
o
o
fH
fH
o
in
fH
fH
00
CM
f>
^3
fH
CM
in
in
fH
fH
O
in
>o
CO
CO
f>
CM
0
in

•c
fH
•>•
CM
^
(f\
i-H
C.b

^.
r^
o

c



o



c


o
o
o
-0
•o
o
•*
o



03
in
o
|H
in
W5
CM
0
CM
in
in
M5
fH
IN
fH
CM
fw

CO
00
in
o
CM
^
^
00
CO
in
03
C
0
CM
fH
rci
00
fO
fH
CO
•c
CO
in
fH
O



c



o


CO
•o
r-
in
Mt
fl
-O
^
>*•
CM
-O
•a
fH
fM
O
0
CO
fH
fH
a.
o
Qs
1^
CM
h-
i>»
O
fH
fH
CC
m
in
CM
fH
—
!>.
O
in
CM
fH
a
fM
CM
in
a
in
•o
fH
0



o



o



c


^
CM
O
O
0


O



o



o



in
co
CO
CM

0
Q*
0*
^•4


fM
O



O



O



0


-t
f>
f>
fH
CO
CO
fl
in
^
o

in
CO

r-
03
^
CM
O


a



rH
o-

fw

fH
fH
in
-0

o



o




o




c



o



o



0


o



o


o



0



o



o




o




c




o



o
fH
CO


r>

I-
CO

o



c



o



o


               _
               11
               o
                                       L-29

-------
                         COCOOCOOOOOGOOOO
                         ocoooooooooocooo
                         OOOOOOOOCOOOOOOO
o
o
o
CM
cooooooooooooooo
w
                         ocoooooooooooooo
H
                         ooccoococoococooo
                                                         o
                         ooooocf^ccrtccoooc
                                                         CO              -<
                                                         in              ^
                                                                         fM
                     oo    1*1
                     ^H    o
                     c    •-<
                                                                    -o
                                                                    ro
o
w
OOOOOOO'-'-OOOOOCCC
                                     -o    -t
                                     O    M
                                     cr    in
                         oooococooocccccc
                                                              -I    L-\
                                                              rn    c
                         ococooocooooocoo
                         OCCCC    CCCCCCCCCCC
                          occccococ.   oocccce
                          crcocccccocecccc
                    Q

                    T
                                                            L-30

-------







0
o
0
CM
3
w
>l
H

S

CO
$
h-i

ri
M4
H
3

c*i
o
^
§

H
>

><
nJ
H

iTi
fH
-t
CO
c
1*1
(SI
>0
o
-0


o
v4/
(—4
CO


^
f-
ro
O
-*•
(SI
m
rj

1^
,$•
in
t^
f«<


^
•o
r-

~t

£
u*
»— i
»— i
m
Js
IT

•— 1

C




O




c

rs
0

o



(SI
•O
in
-0
m
0

0




0





r-
<*i
(SI
(SI
-o
in


-t
•0
(SI
o>



r-
o
CO
(—4

O



cc
^
in
t-
fv

o
r-

f^
r <
C i
ir
r^
r^
r .
C
C
r-;
O

O



>0
c^
in
4*4
(SI
00
m
*H
*
IM
in


C
to
O
-C


CO
IM
o-
0
00
00
in
(SI

CO
c
-o
(SI



0)
in
o-


f-
sO
r^i

0
f*J
^J.
-A


,.}.
r.i
.— <
^^i

C




^
f\
in
o

c



^
CO
1^-
r^
(SI
^
0
rt
^~
(SI


o
>J-
l"^
-o
«_4

r-
•J-

•4-
•0
oc
r-
m
t—4

0
CO
CO
•40
ro


C
c
1-4


c



i—4
0
IT

>-'

J-
t


m
c
r-
^

m
o^
v£
O

o



•4
•0

^
(SI
0

0




(SI
f-
m
r-4
f^

c



c



t-
^>
(SI
cr-



ro
in
vQ
rj

c
c
(0
**
m
o
f^
rj


(^
rj
h-


m
(SI
^^
^~

c


o

o



r--
IM
0
f>
m
^
00
(0
o




o>
ro
en
fsj
-*

r
(SI
m
o
(SI
m
•o
-0
in


«i
o
0
CO
f-4

•C
*c
o
2
(SI
o
-t
(SI

i)
^-
•^
m
f*j
1— 4

0
in
in
in

o-
(-4
'S'
rj
^
a
^
o
n

c
,-H
f--
J5

rr>
f^-
ir
c
(-
a
^i
c
o

a-
f^
o
*^
in
^
in
(SI

0
O
in
<*i
0
o

r-j
s£l
f>-
0
r-

(*i
^
>o
5
m
(SI
in
-r

0
&•
o.
^*
o


n
o
vO
fsj
O
i^H
4J—4
C,
O
c.
0
0-
o
c

in

,^
r-
rO
C
-cf
(S,
st
C
rj
"
,,,
r"1
xf
00
(SI
•O
in
o^
(SI
o




o

o




(SI
•4"
0
in
rs!

-0
«*•
or

•4-
rsi
o

,-,
O-
^
.4
sf


o-
^
•o
(*1

r-
o
en
f^;
•*
O-
m
sf

r.j

f<-
o
n't
r^

c




o


0
CO
in
INI
in
in
r-
INI
^.
*O
00
CO

o

c




—
(S,
^
M
l^

rn
O"
r<^
5
c
0-
cc>
(*\
^

m
o-
^4-
in
(SI


«-4
in
M
vO

on
0
-0
(V
~o
*
o
o

t J

c




o




o


in
(SI
0
o>
(SI
oo
«0

1*1
-0

o
1-4
-*
o

o




0
m
a
m
^>

*H
0


CO
in
M

_
r-
fr^
f^.
(SI


fT)
in
m



-o
r-
4-^
r-

o





r .
n
r
-t

c




c


o
(»!
•0

in
a-


0




m
o
^
^
oo
•*•


^
o
(-4
O*
sO

0



o
c
in

CM
o
4^
h-
r-j


O




in
cr
^>
o

o
in
NO
Li


in
0"
rj


C




O


00
o
INI
^
-O
ao

in
in
(SI
IN
(SI
in
00
0




in
r-
.4*
h-
f^

o



(>
(SI
rr\
0
(SI

fr
in
03




r-
Cl
rj
m

o^-
rj
C
C
i—4
O





o




c




c


rO
•N
CO

^>
*
^
o^
•0
m

o

oo
f^
m
rH


00
f«-
IM
CO
1*4

(Nl
0
fSI
fSl
vC
0
f-
c
FH

o






n
£



CO
-3-
(^
C
"••
CO
(SI
o
o


c




o




c


o

o
•o
•a

•o
in
o
4-4

o

IM
in
4—4
f H

(SI
r-4
ON
a
^

4
fSI
o
(SI
^
c


0






c




£
^»
n

o





c




o




o


o

0



0




0

o




0





o



o



c






c




c



o





o




0




c


L-31

-------
LO
r~-
CTv
Q
I-l
Pi
O


§
H
Pi
M
>
g
Pn
w
a
s
I
§
o

f=4
O

w

§
M
CO
CO
5g
    53
    p
^^
H^
ffi  O
w  ^
>
@
H
O  CO
W  H
*-3  H

Q  g
Pi  P
PL,  ^_/
 CO
N«^



 I




    IT1
                                                                                            VD
                                                             CM
                              com
                                        oo
                                                             O   r^
                                                             CM   CM
                                                                  .ro
                                                             oooocy>cM
-------
O
oo
a!
§
H
Q
g
w
a
s
u

Pn
o
CO

I
00
CO
H {M
   
H
CJ CO
W H
^ M
Q g
Pd P
PH ^^
 CO
H
                    CO
                    
-------
m
oo
01
O

o
oi
H
w
H


O


W

3
I


§
CJ
1
oo
en
t-t
K O
W M
H
U CO
W H
"-J M
Q &
 o
N^X

r^-


rJ

 (a
t-l


 crj
H
m
i-i
i-4
CO
i-i
CM
I-l
1-1
t-l
o
r-i
01
O)
a
00
0
o
r-
VD
in
-
CO
CM
1-4
0 O
p3 c*
0 0
CO CM
CM i-l
CO r~~
in O1v^O
inininoiOcoinoiooi OCMI — i
CO CM i-l i-4 CM r-l
r-ir-iLn~d-cocMcM
-------
ON
9
(A
O
Q


W







O



CO
o
§
lit
o

CO


1
CO
00
M
   Q
§
PM
 I



 OJ
Cfl

H
   CO

   EH
   M
m
r-i
r-i
CO
r-i
CM
r-l
r-4
r-4
O
r-l
u
1
p! 00
r-l
O r-
U
-
m
•*
CO
CM
r-l
O O
eg £
O 0
O CM
r-4
CO 00
 CO
st
CO O
t-l
vD CM
CO
OO t-~
t-{
CM ON
i-l CjNOOr^*r-4CO
CM CM r-4
^r-IOO-J'i-^CMI^.CM-cfOr-ICM-cl-O
OcMi— icoi— ico>— imi — oooor-^m
r-l CM <)" CM r-l r-l i-l
ONCMCM^-^DCMinO
cocoOoovOr^cor^-OinoocM
t-ICMi-l^fincOCO-d-CM
mOcocMoo^£)coi—i
r-l r-4 r-l
r^.vOCM\Oin^'cocMi— i
r-l r-l r-l 1-4 r-4
                                                  L-35

-------
o
OO
§
H
W
O
En
§
Pn
O
en

I
    Q
    co
O

PM


  •
/-x
 0)
^^*


 I



 
-------
co
0
oi
O

§
W
g
§
§
p
Pn
O

CO


1
CO
CO
H
    O
Pd
H
O  CO

W  H

"-3  H

O  2


p I  s.^
rJ



 (1)
 CO

H
               t-l

               Ol
               o
              o
                      00
                      vO
                      CO
                      CM
                   0  0

                  Pi  C
                               000
                               CO
                              OO
                                                               r^^l —   i— ICMOOlTlCMO

                                                               COCNlr-li-lr-li-ICOi-l
                               CM
                                                                    co
                                    U">   <(•    i—linCTiOCOOCT\COvQCMi—I   <(•    O
                               co   
-------
m
O


§
H
Pi
W
O

o

oo
X
O
H
l-l
00

I
oo
00
I-H
   CM
   M
   O
W
EH
CJ oo
W H
n H
o z
Pi n5
p . ^^/
r-
 i






S-l
0)
,0
c
i-H
o
CJ

m
rH
rH
CO
rH
CM
rH
rH
rH
O
rH
-
OO
-
vO
m
-
CO
CM
rH
o o
fv! rj
O 0 0 O
~d- i-l rH rH
in -3- CM CM
rH rH
CO O CM O
CM CM rH
CM VO rH r-.
rH CO d" ^O vD ^O
O m r^ co
O 
O
rH
CM
O
CM
m
CO
00
OS
CM

CM
vo m
rH CM
i-H rH
ON 
-------
o
00
ON
O




§
w
g
CO
w
H
H
00

1
CO
CO
M
   o
   o
H
U CO
H H
 0)
1-1
J-i
(1)
C
r-l
O
o





in
r-4
•O-
i-i
CO
1-1
CM
i-H
r-4
t-l
o
1-1
CTN
oo
-
0
in
-
CO
CM
i-l
go
rA a
i— 1
t-l i— 1
i-l T-l CO CM i-l CM i-l
cOr-i-oc^vocMO
cMcMi—i cy> crv r^- <)•<]• i— i
co **o i— i CT* xj" oo CM in oo co **Q T~~i r*^> ^D oo co
i— i ~ct" o^ r— i *sO in r^« *^ t^i ^0 CM
i— i i-i
cMcococMcMOooo<|-Oinincr>rocoO
O i—l i— 1 i— 1 i— 1 i— 1 i— 1
co i— i in ^j~ ^^ ^0 oo i~~i c^ in *^* *cj* co in CM co
i—4 i— 1 CM Cj CT* i™~l CO O^ 00 CO ^t" *vl" CM
i-l CM CM i-l CM i-l
r-li-lCMCM^CO^CMCM
\o cr\ r^* o ^o r^ vo CM i— i CM CM *^ co in r— i in
i— 1 CM vO CO 00 00 i— 1 00 O CO *-d" **O ^d" f~l
r-4 CM CO CM i-l i-l r-4
i-l i-l i— 1 CM i-l
1-1 T-t I-l

-------
m
oo
ON
§
H
W
H

O

CO

1
g
o

§
H
M
§
M
CO
CO
H
 Q

 H
   co
 CD
r-l
m
r-l
r-l
CO
r-4
CM
r-l
r-l
r-l
0
r-l
ON
00
r-l
0
o
m
 O CO ON CM CM
CM CO C^ OO r— 1 CM r— 1 OO
r-i co 
-------
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

-------
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

-------
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

-------
                                  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)

-------