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About the Authors
Dr. Keith Silverman is a director and Dr. Joan Tell is a senior
project engineer in the Global Safety and the Environment Department at
Merck & Co., Inc. based in Whitehouse Station, NJ. Dr. Edward
Sargent is the managing director of EV Sargent LLC and Dr. Zeyuan Qiu is
an assistant professor in the Department of Chemistry and Environmental
Sciences at New Jersey Institute of Technology, Newark, NJ. Please
address correspondence to: Keith Silverman, Merck & Co., Inc., 2
Merck Drive, Whitehouse Station, NJ 08873; phone: +1-908-423-4102; fax:
+1-908-735-1496; e-mail: keith_silverman@merck.com.
Keith C. Silverman and Joan G. Tell
Global Safety and the Environment, Merck & Co., Inc.,
Whitehouse Station, NJ
Edward V. Sargent
EV Sargent LLC., Watchung, NJ
Zeyuan Qiu
Department of Chemistry and Environmental Sciences, New Jersey
Institute of Technology, Newark, NJ
RELATED ARTICLE: IMPLICATIONS
Air quality models are typically used to predict the fate and
transport of air emissions from industrial sources to comply with
federal and state regulatory requirements and environmental standards,
as well as to determine pollution control requirements. This study
compares two common models (ISC and AERMOD), the magnitude differences
in ambient air concentrations predicted by the models, and the
subsequent human health effects predicted using the results from the two
models.
Table 1. Source parameters used in the modeling.
Source Type Parameters Units Site 1 Site 2
Point Height m 21.4 16.5
Diameter m 0.37 0.4
Temperature [degrees]C 25 20
Exit velocity m/sec 3.8 0.4
Area Release height m 1 1
X-length m 5 5
Y-length m 12 12
Volume Release height m 9.75 9.75
Initial lateral dimension m 5.3 5.3
Initial vertical dimension m 4.5 4.5
Table 2. The parameter values for calculating the HI and LICR.
Parameter Description Value Units
Site 1
ER Methylene chloride -- 7.1 x g/sec
stack [10.sup.-2]
ER Methylene chloride -- 7.0 x g/sec
area [10.sup.-3]
ER Methylene chloride -- 8.0 x g/sec
volume [10.sup.-3]
RfC Methylene chloride 1 mg/[m.sup.3]
IUR Methylene chloride 4.7 x 1/([micro]g/[m.sup.3])
Site 2 [10.sup.-7]
ER Hydrazine -- stack 2.5 x g/sec
[10.sup.-4]
ER Methylene chloride -- 7.0 x g/sec
area [10.sup.-3]
ER Methylene chloride -- 8.0 x g/sec
volume [10.sup.-3]
RfC Hydrazine 2.0 x mg/[m.sup.3]
[10.sup.-4]
IUR Hydrazine 4.9 x 1/([micro]g/[m.sup.3])
[10.sup.-3]
RfC Methylene chloride 1 mg/[m.sup.3]
IUR Methylene chloride 4.7 x 1/([micro]g/[m.sup.3])
[10.sup.-7]
Notes: ER = emission rate.
Table 3. Maximum off-site ground-level air concentrations predicted by
the various models for both sites using a unit emission rate.
Air Dispersion Averaging ([micro]g/[m.sup.3])/(g/sec)
Model Period Site 1 Site 2
Point Sources
ISC Total period 6.2 52.0
AERMOD Total period 7.4 18.6
ISC 1 hr 571.2 4,907.2
AERMOD 1 hr 333.0 576.4
ISC-PRIME Total period 9.2 30.8
AERMOD-PRIME Total period 7.7 9.0
ISC-PRIME 1 hr 284.2 1,123.7
AERMOD-PRIME 1 hr 247.6 405.4
Area Sources
ISC Total period 369.4 67.4
AERMOD Total period 213.0 111.9
ISC 1 hr 34,147.3 11,765.5
AERMOD 1 hr 17,858.0 14,947.5
Volume Sources
ISC Total period 36.4 37.5
AERMOD Total period 43.8 19.7
ISC 1 hr 1,679.3 3,676.7
AERMOD 1 hr 1,399.8 702.8
Table 4. Predicted maximum HQ and LICR values.
Air Dispersion HQ
Model Site 1 Site 2
Point Sources
ISC 2.4 x [10.sup.-4] 1.0 x [10.sup.-1]
AERMOD 2.8 x [10.sup.-4] 3.7 x [10.sup.-2]
ISC-PRIME 3.5 x [10.sup.-4] 6.1 x [10.sup.-2]
AERMOD-PRIME 2.9 x [10.sup.-4] 1.8 x [10.sup.-2]
Area Sources
ISC 1.4 x [10.sup.-3] 2.5 x [10.sup.-4]
AERMOD 8.0 x [10.sup.-4] 4.2 x [10.sup.-4]
Volume Sources
ISC 1.6 x [10.sup.-4] 1.6 x [10.sup.-4]
AERMOD 1.9 x [10.sup.-4] 8.5 x [10.sup.-5]
Air Dispersion LICR
Model Site 1 Site 2
Point Sources
ISC 7.1 x [10.sup.-8] 2.1 x [10.sup.-5]
AERMOD 8.4 x [10.sup.-8] 7.6 x [10.sup.-6]
ISC-PRIME 1.0 x [10.sup.-7] 1.3 x [10.sup.-5]
AERMOD-PRIME 8.8 x [10.sup.-8] 3.7 x [10.sup.-6]
Area Sources
ISC 4.2 x [10.sup.-7] 7.6 x [10.sup.-8]
AERMOD 2.4 x [10.sup.-7] 1.3 x [10.sup.-7]
Volume Sources
ISC 4.7 x [10.sup.-8] 4.9 x [10.sup.-8]
AERMOD 5.7 x [10.sup.-8] 2.6 x [10.sup.-8]
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