| Company |
Location |
Collocated |
R&D
Controls |
R&D
HAP Emissions |
Facility-wide
HAP Emissions |
Basis
for Emission Estimates |
Source
of Information |
Comments |
| Albemarle |
Baton
Rouge, LA |
no
[2] |
scrubbers[3]
condensers
flares |
0.6
tpy HAP[4] actual (1996) |
|
Toxics
Emissions Data Inventory (TEDI) |
Facility
& State |
Albemarle
also operates a bromine terminal at this site. Located on same contiguous
property with Ethyl Corporation, which is separately owned and permitted. |
| Cerac,
Inc. |
Milwaukee,
WI |
yes |
information
unavailable |
|
Facility:
2.07 tpy HAP actual (1994)
State:
13.7 tpy HAP actual
|
State
emissions inventory information |
Facility
& State |
Speciated
HAP information provided by State.
Facility stated
that HAPs emitted include arsenic, cadmium, chromium, chlorine,
hydrogen chloride, and hydrogen sulfide.
|
| DuPont |
Deepwater,
NJ |
yes |
thermal
oxidizer
scrubbers (multi-stage packed tower, spray tower absorber)
carbon adsorber
condensers (dry ice; chilled, building, or process water)
filters |
Facility:
0.566 tpy VOC[5] actual
(a pilot plant w/ both R&D and manufacturing)
0.033 tpy (652 lb/yr) HAP actual
(a pilot plant w/ both R&D and manufacturing) |
Facility:
500 tpy VOC actual (facility, incl. mfg.)
70 to 80 tpy HAP actual
(facility, incl. mfg.)
State:
110.8 tpy (221,620
lb/y) stack
238 tpy (476,085 lb/y) fugitive
|
Emissions
inventory
Toxic Release
Inventory (TRI) emissions calcs based on chemical use
Plantsite HAP emissions from state TRI
|
Facility
& State |
|
| Polaroid |
Waltham,
MA |
yes |
afterburner
(on research test coater)
|
0.57
tpy organic solvents actual (1995)
0.79 tpy organic solvents actual (1996) |
|
Emissions
calculations |
Facility |
|
| Polaroid |
Cambridge,
MA |
no |
information
unavailable |
10.96
tpy VOC actual (1996)
5.0 tpy HAP actual
(1996)
|
|
Emissions
calculations |
Facility |
Permit
limits are 40 tpy VOC/HOC[6] and
25 tpy HAPs. |
| Solutia
|
Springfield,
MA |
yes |
industrial
hygiene controls:condensers
hoods
mist eliminators |
1.6
tpy actual VOC
(pilot plants) (1996)
<1.5 tpy actual VOC (laboratories) |
|
Emissions
estimate |
Facility |
|
| Specialty
Chemical Products |
Marinette,
WI |
yes |
condensers
(as a part of the process line)
four scrubbers (as
add-on controls)
|
|
Facility:
16 tpy total (VOC & HAP) actual (1997, est.)
State:
< 1 tpy VOC actual (1995)
zero (or below reporting levels) HAP (1995)
7.9 tpy HAP actual (unknown year) |
Facility
and State emissions inventory information |
Facility
& State |
Speciated
HAP information provided by State.
R&D and
general operations not separated. Pilot plant used for regular
operations, and R&D a very small portion of current work.
Largest emission
HAP is mixed xylenes at approximately 3 tpy (1997, est.)
Facility is
investigating difference between State and facility emissions
estimates.
|
| Union
Carbide
(chemicals)
|
Bound
Brook, NJ |
no |
information
unavailable |
9.85
tpy actual VOC (1996)
(4.93 tons R&D,
remainder from a boiler)
|
|
Lab
hood emissions factor for NJ |
Facility |
The
PTE[7] for lab hoods was 5 tpy assuming
16 hours per day operation. Permitted for pilot plants. |
| Union
Carbide |
South
Charleston, WV |
no |
information
unavailable |
4.5
tpy HAP actual (1996)
95 tpy VOC actual (1996)
|
|
State
emissions statement |
Facility |
35%
of HAP emissions fugitive;
65% of HAP pilot
plants and lab hoods.
State permit
includes speciated HAP emissions.
Good management
practices used to reduce emissions.
>100 tpy
PTE VOC for R&D
|
| Vulcan |
Wichita,
KS |
yes |
information
unavailable |
0.23
tpy (454 lb/yr) VOC actual (current) (pilot plant)
0.5 tpy (1008 lb/yr) VOC actual (future) (pilot plant)
0.22 tpy (439 lb/yr) HAP actual (current) (pilot plant)
0.44 tpy (878 lb/yr) HAP actual (future) (pilot plant) |
|
Emissions
calculations |
Facility |
Collocated
with manufacturing operations, but manufacturing operation emissions
were reported to be 1.38 tpy (2759 lb/yr) and 98% controlled. |
| Company
| Facility
| Location |
Collocated |
R&D
Controls |
R&D
HAP Emissions |
Facility-wide
HAP Emissions |
Basis
for Emission Estimates |
Source
of
Information
|
Comments |
| Department
of Defense[8] - Naval Surface Warfare
Center |
Indian
Head, MD |
Yes |
none
on most equipment; some carbon adsorbers and HEPA filters on pilot
plant buildings |
<1
tpy |
|
Material
balance, R&D emissions were assumed to be 1% of the amount used
in the pilot plants. |
Facility |
Lab
emissions were not calculated. |
| Department
of Defense - Naval Surface Warfare Center |
Carderock,
MD |
No |
none |
<1
tpy |
|
Varies,
most taken from AP-42 |
Facility |
|
| Department
of Defense - Naval Underwater Warfare Center |
Newport,
RI |
No |
afterburner
on the torpedo engine test stand |
1.2
tpy |
|
Estimated
emissions |
Facility |
|
| Department
of Defense - Naval Surface Warfare Center |
Panama
City, FL |
No |
particulate
filter on paint booth |
VOC-
0.59 tpy
nonVOC - 6.0E-5 tpy
|
|
AP-42,
material balance |
Facility |
|
| Department
of Defense - Naval Air Warfare Center |
Patuxent
River, MD |
Yes |
none
on engine test cells |
0.7658
tpy |
|
Estimated
emissions |
Facility |
|
| Department
of Defense - Naval Air Warfare Center |
China
Lake, CA |
Yes |
none |
Available
June 98 |
|
Various,
doing a comprehensive evaluation |
Facility |
|
| Department
of Defense - Naval Submarine Medical Research Laboratory |
Groton,
CT |
Yes |
none |
<
0.005 tpy (<10 lb/yr) (acetonitrile) |
|
Best
engineering judgment |
Facility |
|
| Department
of Defense - Detachment Naval Medical Research Institute Bethesda,
Brooks AFB |
TX |
No |
none |
<0.01
tpy (<20 lb/yr) (methanol, ethylene glycol) |
|
Best
engineering judgment |
Facility |
|
| Department
of Defense - Naval Facilities Engineering Services Center Port |
Hueneme,
CA |
No |
none |
<
0.03 tpy
(Many different HAPs in small amounts, largest are: Methyl Chloroform,
MEK, Methyl Chloroform, Formaldehyde, Toluene, Methanol, PCE, Xylene,
20 others) |
|
AP-42,
material balance, permit limits |
Facility |
|
| Department
of Defense - Naval Medical Research Institute |
Bethesda,
MD |
No |
information
unavailable |
1.25
tpy
Majority of HAP emissions (facility-wide) are Toluene, Ethylene
Oxide, Xylenes, Benzene, o-Xylene, Ethyl Benzene, and Formaldehyde.
(Xylene is used to fix tissue to slides.) |
2.5
tpy HAP facility-wide |
Estimating
50% from Hospital, 50% from R&D facility. |
Facility |
|
| Department
of Defense - U.S. Army Armament Research, Development & Engineering
Center |
Picatinny
Arsenal, NJ |
No |
none |
A
few pounds/year |
|
Best
engineering judgment |
Facility |
|
| Department
of Defense - Aberdeen Proving Ground |
Edgewood,
MD |
Yes |
information
unavailable |
5.3
tpy |
|
Material
balance |
Facility |
|
| Department
of Defense - Yuma Proving Ground |
Yuma,
AZ |
Yes |
none |
Hydrofluoric
Acid 2 gals/yr |
|
AP-42 |
Facility |
|
| Department
of Defense - Detroit Arsenal |
Detroit,
MI |
No |
none |
0.004
tpy
Benzene, Toluene, Xylene,
1,3 Butadiene, Formaldehyde, Acetaldehyde, Methyl Chloroform
|
|
AP-42 |
Facility |
|
| Department
of Defense - Rock Island Arsenal |
Rock
Island, IL |
Yes |
none |
0.134
tpy (267.2 lb/yr)
Petroleum Ether (not
calculated from oil testing)
|
|
AP-42 |
Facility |
|
| Department
of Defense - Soldier Systems Command |
Natick,
MA |
No |
a
few lab hoods are equipped with activated carbon filters; a few
other are equipped with "dry ice traps" (simple condensors) |
0.003
tpy
Acetonitrile, Aniline, Benzene, Benzyl Chloride, Carbon Tetrachloride,
Chloroform |
|
AP-42 |
Facility |
|
| Department
of Defense - Fort Monmouth, NJ |
NJ |
No |
none |
Methylene
Chloride, Chloroform, Xylene, Toluene |
|
AP-42 |
Facility |
|
| Department
of Defense - Edwards AFB |
CA |
Yes |
none |
3
tpy |
|
Material
balance and best engineering judgment |
Facility |
|
| Department
of Defense - Eglin AFB |
FL |
Yes |
none |
0.02
tpy |
|
Material
balance and best engineering judgment |
Facility |
|
| Department
of Defense - Brooks AFB |
TX |
No |
information
unavailable |
<
0.1 tpy |
|
Material
balance and best engineering judgment |
Facility |
|
| Department
of Defense - Arnold AFB |
TN |
Yes |
none |
0.1425
tpy |
|
Material
balance and best engineering judgment |
Facility |
|
| Department
of Defense - Kirtland AFB |
NM |
Yes |
none |
0.055
tpy |
|
Material
balance and best engineering judgment |
Facility |
|
| Department
of Defense - Holloman AFB |
NM |
Yes |
none |
<
1 tpy |
|
Material
balance and best engineering judgment |
Facility |
|
| Department
of Defense - Wright-Patterson AFB |
OH |
Yes |
none |
1.6
tpy |
|
Material
balance and best engineering judgment |
Facility |
|
| Department
of Defense - Rome Laboratory |
NY |
No |
none |
<
0.05 tpy |
|
Material
balance and best engineering judgment |
Facility |
|
| Department
of Energy - Grand Junction Project Office |
Grand
Junction, CO |
no |
scrubbers |
0.3
to 0.4 tpy HAP actual |
|
Emissions
Estimate |
Facility |
Facility
stated that actual emissions are much less than the permit level
of 11 tpy HAP (methylene chloride), and the operations at this location
are being phased out. |
| Department
of Energy[9] - Oak Ridge National
Laboratory |
Oak
Ridge, TN |
unknown |
information
unavailable |
13.3
tpy HAP actual (1994)
12.7 tpy HAP actual (1995)
11.4 tpy HAP actual (1996)
12.5 tpy HAP actual (avg.) |
|
Mass
balance using chemical procurement records and laboratory personnel
input |
Facility |
|