AIRSHED MODEL EVALUATION OF REACTIVITY ADJUSTMENT FACTORS CALCULATED WITH THE MAXIMUM INCREMENTAL REACTIVITY SCALE FOR TRANSITIONAL-LOW-EMISSION VEHICLES
La. Mcnair et al., AIRSHED MODEL EVALUATION OF REACTIVITY ADJUSTMENT FACTORS CALCULATED WITH THE MAXIMUM INCREMENTAL REACTIVITY SCALE FOR TRANSITIONAL-LOW-EMISSION VEHICLES, Journal of the Air & Waste Management Association [1995], 44(7), 1994, pp. 900-907
The California Air Resources Board recently adopted regulations for li
ght-and medium-duty vehicles that require reductions in the ozone-form
ing potential or ''reactivity,'' rather than the mass, of nonmethane o
rganic gas (NMOG) emissions. The regulations allow sale of all alterna
tively fueled vehicles (AFVs) that meet NMOG exhaust emission standard
s equivalent in reactivity to those set for vehicles fueled with conve
ntional gasoline. Reactivity adjustment factors (RAFs), the ratio of t
he reactivity (per gram) of the AFV exhaust to that of the conventiona
lly fueled vehicle (CFV), are used to correct the stringent exhaust em
ission standards. Complete chemical speciation of the exhaust and conv
ersion of each NMOG species to an appropriate mass of ozone using the
maximum incremental reactivity (MIR) scale of Carter1 determines the R
AF. The MIR approach defines reactivity where NMOG control is the most
effective strategy in reducing ozone concentrations, and assumes it i
s not important to define reactivity at other conditions, i.e., where
NO(x) is the limiting precursor. This study used the Carnegie/Californ
ia Institute of Technology airshed model to evaluate whether the RAF-a
djusted AFV emissions result in ozone impacts equivalent to those of C
FV emissions. A matrix of two ozone episodes in the South Coast Air Ba
sin (SoCAB) of California, two base emission inventories, and exhaust
emissions from three alternative fuels that meet the first level of th
e low emission vehicle standards bounds the expected range of conditio
ns. Although very good agreement was found previously for individual N
MOG species,2 this study noted deviations of up to +/-15 percent from
the equal ozone impacts for any vehicle/fuel combination required by t
he California regulations. These deviations appear to be attributable
to differences in spatial and temporal patterns of emissions between v
ehicle fleets, rather than a problem with the MIR approach, The first
formally adopted RAF, a value of 0.41 for 85 percent methanol/15 perce
nt gasoline-fueled vehicles, includes a 1 0 percent increase based on
the airshed modeling. The correction to the RAF is different for other
fuels and may be different for air basins other than the SoCAB.