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A. Process name or description of each product.

B. Quantity of raw materials used and handled for each product, maximum quantity per hour, and average quantity per year.

C. Quantity of each product manufactured, maximum quantity per hour, and average quantity per year.

D. Description of annua., seasonal, monthly, weekly, and daily operating cycle including downtime for maintenance and repairs.

E. Air pollution control equipment in use (existing and proposed):

E. Air pollution control equipment in use (existing and proposed):

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G. Emission data:

1. Based on emission factors.

2. Estimate of emissions by the source. 3. Results of any stack tests conducted.

IV. SOLID WASTE DISPOSAL

A. Amount and description of solid waste generated, quantity per year.

B. Percent of total that is combustible. C. Method of disposal (on-site or offsite).

D. Description of on-site disposal method, if applicable (incineration, open burning, landfill, etc.) including maximum quantities disposed per hour and average quantities disposed per year and actual operating schedule.

1. Location of the source by a grid system (UTM or equivalent).1

2. If method of disposal is by an incinerator, include the following information:

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1. Anthracite Coal (plus type and size of unit) -tons/year or metric tons/year.

1 Emissions data for all source categories and subcategories should be summarized in the implementation plans as is in Appendix D or G.

2 Data is required on a grid basis only when diffusion modeling is utilized. For proportional model technique, data must be available on a county basis.

3 Required only when diffusion modeling is utilized.

4 Average type and size for each category. This is used as the basis for selection of average emission factor.

2. Bituminous Coal (plus type and size of unit)-tons/year or metric tons/year.

3. Distillate Oil (plus type and size of unit)-10 gal./year or 10 liters/year.

4. Residual Oil (plus type size of unit) — 10 gal./year or 10 3 liters/year.

5. Natural Gas (plus type and size of unit)-10 cu.-ft./year or 10° cu.-meters/ year.

6. Wood-tons/years or metric tons/year. 7. Other-please specify.

B. Commercial and Institutional Fuel:

1. Anthracite Coal (plus type and size of unit)-tons/year or metric tons/year.

2. Bituminous Coal (plus type and size of unit)-tons/year or metric tons/year.

3. Distillate Oil (plus type and size of unit)-103 gal./year or 103 liters/year.

4. Residual Oil (plus type and size of unit)-103 gal./year or 103 liters/year.

5. Natural Gas (plus type and size of unit)-10 cu.-ft./year or 108 cu.-meters/year. 6. Wood-tons/year or metric tons/year. 7. Other-please specify.

C. Industrial Fuel:

1. Anthracite Coal (plus type and size of unit)-tons/year or metric tons/year.

2. Bituminous coal (plus type and size of unit)-tons/year or metric tons/year.

3. Coke (plus type and size of unit) – tons/year or metric tons/year.

4. Distillate Oil (plus type and size of unit)-10 gal./year or 103 liters/year.

5. Residual Oil (plus type and size of unit)-10 gal./year or 103 liters/year.

6. Natural Gas (plus type and size of unit)-10 cu.-ft./year or 106 cu.-meters/year. 7. Wood-tons/year or metric tons/year. 8. Other-please specify.

II. PROCESS LOSSES (HYDROCARBONS ONLY) A. Surface coating operations, dry cleaning, degreasing operations, etc., unless con

sidered as point sources-appropriate basis for emission estimate.

III. SOLID WASTE DISPOSAL

A. On-site incineration (plus type of unit)-tons/year or metric tons/year.

B. Open burning-tons/year or metric tons/year.

C. Other-please specify.

IV. TRANSPORTATION

A. Gasoline-powered motor vehicles-appropriate basis for emission estimate, including hydrocarbon evaporative losses.

B. Diesel-powered motor vehicles-appropriate basis for emission estimate.

C. Off-highway fuel usage-103 gal./year or 103 liters/year.

D. Aircraft-number of flights per year per type of aircraft.

E. Railroads-103 gal. diesel oil/year or 10 liters/year.

F. Vessels-103 gal. or 103 liters of oil/year, tons or metric tons of coal/year, or tons or metric tons of wood/year.

G. Gasoline handling evaporative losses— appropriate basis for hydrocarbon emission estimate from filling tank trucks, service station tanks, and automobile tanks. H. Other-please specify

V. MISCELLANEOUS

A. Forest fires-appropriate basis for emission estimate.

B. Structural fires-appropriate basis for emission estimate.

C. Coal refuse burning-appropriate basis for emission estimate.

D. Agricultural burning—appropriate basis for emission estimate.

E. Other-please specify.

APPENDIX G-(POLLUTANT) EMISSIONS INVENTORY SUMMARY. TONS/YR. (OR METRIC TONS/YR.) (REGIONS WHERE EMISSION LIMITATIONS ARE NOT DEVELOPED)

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i Included only if interstate region.

ii Existing Emissions.

iii If not available, does not need to be submitted for Priority III regions.

iv For hydrocarbons only, would include emissions for surface coating operations, dry cleaning, degreasing operations, etc., unless considered point sources.

For hydrocarbons would include vehicle evaporative losses and losses from filling trucks, service station tanks, and automobile tanks.

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The assumptions listed below were made in
calculating the projected national urban
emissions from motor vehicles as shown in
Figures 1-3.

a. Emission factors are based on the new
Federal test procedure (1), which has an
average route speed of 18 miles per hour (29
kilometers per hour).

b. Emission control devices are assumed to
just meet present and proposed standards
when new, but deteriorate with age. Deteri-
oration factors are adapted from data given
in Reference 2.

c. Urban vehicle-mile projections adapted
from Reference 3.

d. Distribution of automobiles by age from
Reference 4.

e. Relative miles of travel for automobiles
(i.e., new cars are driven more than older
ones) from Reference 5.

Figures 1-3 can be used to approximate air
quality levels resulting from the Federal
Motor Vehicle Control Program. The follow-

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total hydrocarbon emissions will result in a
proportion reduction of measured nonmeth-
ane hydrocarbons). The equation cannot di-
rectly be applied to determine the reduction
in photochemical oxidant levels resulting
from reductions in hydrocarbon emissions.
The percent reduction in hydrocarbon emis-
sions expected from the Federal Motor Ve-
hicle Control Program can be estimated
using that portion of the equation in bracket
[ ]. By using Appendix J, it can be deter-
mined if this is sufficient to achieve the na-
tional standard for photochemical oxidants
and if stationary source and/or transpor-
tation controls are required.

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Figure 1. Hydrocarbon emission rates from urban vehicles in United States projected from 1967 base of 1.

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Figure 2. Carbon monoxide emission rates from urban vehicles in United States projected from 1967 base of 1.

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