|
Year of Inventory
|
Pollutant
|
Category
|
Methodology Change
|
|
1990
|
CO, VOC, NOx
|
Primarily nonutility point sources and 17 states worth
of area sources
|
A combination of Ozone Transport Assessment Group ( OTAG),
Grand Canyon Visibility Transport Commission Inventory (
GCVTC), and Aerometric Information Retrieval System ( AIRS)
data was added to inventory, replacing some units but primarily
just adding more units. (Ozone season daily data received
was developed into annual data).
|
|
1990
|
PM10, PM2.5, SO2
|
As above
|
State data received as above was augmented with PM and
SO2 data through an SO2 and PM to
NOx uncontrolled emission factor ratio.
|
|
1991-1995
|
All but Pb
|
Primarily nonutility point sources and 17 states worth
of area sources
|
NAPAP, AIRS data, GCVTC and Grand Canyon projections from
the 1990 inventory using Bureau of Economic Analysis ( BEA)
growth indicators.
|
|
1990
|
All but Pb
|
on-road mobile
|
1990, 1995, 1996 use state-supplied MOBILE model inputs
where applicable. See Reference 1 for a list of States supplying
model inputs.
|
|
1990
|
All but Pb
|
on-road mobile
|
Used state supplied vehicle miles traveled ( VMT) where
applicable. See Reference 1 for a list of States providing
VMT.
|
|
1985-1989
|
All but Pb
|
chemical and allied
|
Removed rule effectiveness from pre-1990 chemical and allied
product emissions.
|
|
1985-1994
|
NOx
|
utilities
|
Used NOx emission rates from Acid Rain Division
(ARD) instead of AP-42 emission factors.
|
|
1994-1998
|
NOx, SO2
|
utilities
|
Based Phase I units on CEM data from ARD, remaining units
are from DOE767 survey data (small amount of units).
|
|
1996
|
All but Pb
|
nonutility point (35 states) and area sources (14 states)
|
Added state-supplied data directly received from states
or retrieved from AIRS as part of the PEI inventory effort,
as directed by the states.
5 State submittals were select cities only.
|
|
1997-1998
|
All but Pb
|
nonutility point and area sources
|
Projected through 1998 based on the 1996 PEI enhanced database
using EGAS derived growth factors and BEA growth factors
where applicable.
|
|
1970, 1975, 1980
|
All but Pb
|
non-road sources
|
Generated national-level nonroad emission estimates based
on category-specific ratios of 1996 NONROAD model outputs
to previous year national estimates.
|
|
1985-1998
|
All but Pb
|
non-road sources
|
Ran the beta version of the NONROAD model for all counties
in U.S. for 1996. Used the NONROAD model to calculate national
emissions for the other years and then used SCC-specific
ratios for the other years relative to 1996 (year in question/1996)
to determine county-level estimates.
|
|
1985-1998
|
All but Pb
|
non-road sources
|
For commercial marine diesel, EPA’s OTAQ provided
revised national VOC, NOx, CO, and PM emission
estimates for commercial marine diesel engines. National
estimates were distributed to counties using the geographic
distribution in the existing NET.
|
|
1990-1998
|
All but Pb
|
Miscellaneous -agric. forestry
|
Revised allocation of Census of Agriculture activity data
between the 1990 and 1997 census: used agricultural surrogates
instead of economic surrogates.
|
|
1990-1998
|
PM
|
Miscellaneous -agric. crops
|
Began using tillage activity data using the Conservation
Technology Information Center, Purdue University, data,
and also changed silt value methodology from 1990 onward.
|
|
1989-1998
|
PM
|
Miscellaneous -managed burning
|
Based on USDA Forest Service inventory of PM from prescribed
burning. Public percentage of acres burned projected from
1990 using national-level growth factor developed from total
U.S. acres burned, while private portion held constant.
|
|
1990-1998
|
PM
|
Miscellaneous -construction
|
Changed the emission factor in 1990: changed from using
a former AP-42 value to using latest AP-42 findings report:
"Improvement of Specific Emission Factors" - change occurred
in Trends year 1997.
|
|
1990-1998
|
PM
|
paved roads
|
The rain correction factor in the paved road equation was
reduced by 50 percent for the years 1990 onward due to uncertainty
associated with the actual reduction in emissions due to
precipitation on paved road surfaces.
|
|
1990-1998
|
All but Pb
|
structural fires
|
For non-OTAG States, revised 1990 and 1996 emissions based
on new loading factor value. Projected all States using
EGAS regression equations, which relate State-level population
to the amount of material burned in structure fires.
|