92.132—Calculations.

(a) Duty-cycle emissions. This section describes the calculation of duty-cycle emissions, in terms of grams per brake horsepower hour (g/bhp-hr). The calculation involves the weighted summing of the product of the throttle notch mass emission rates and dividing by the weighted sum of the brake horsepower. The final reported duty-cycle emission test results are calculated as follows:

(1) (i) Eidc =(Σ(Mij )(Fj ))/(Σ(BHPj )(Fj ))

Where:

Eidc=Duty-cycle weighted, brake-specific mass emission rate of pollutant i (i.e., HC, CO, NOX or PM and, if appropriate, THCE or NMHC) in grams per brake horsepower-hour;

Mij=the mass emission rate pollutant i for mode j;

Fj=the applicable weighting factor listed in Table B132-1 for mode j;

BHPj=the measured brake horsepower for mode j.

(ii) Table B132-1 follows:

Table B132-1—Weighting Factors for Calculating Emission Rates

Throttle notch setting	Test mode	Locomotive not equipped with multiple idle notches		Locomotive equipped with multiple idle notches
Throttle notch setting	Test mode	Line-haul	Switch	Line-haul	Switch
Low Idle	1a	NA	NA	0.190	0.299
Normal Idle	1	0.380	0.598	0.190	0.299
Dynamic Brake	2	0.125	0.000	0.125	0.000
Notch 1	3	0.065	0.124	0.065	0.124
Notch 2	4	0.065	0.123	0.065	0.123
Notch 3	5	0.052	0.058	0.052	0.058
Notch 4	6	0.044	0.036	0.044	0.036
Notch 5	7	0.038	0.036	0.038	0.036
Notch 6	8	0.039	0.015	0.039	0.015
Notch 7	9	0.030	0.002	0.030	0.002
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Notch 8	10	0.162	0.008	0.162	0.008

(2) Example: For the line-haul cycle, for locomotives equipped with normal and low idle, and with dynamic brake, the brake-specific emission rate for HC would be calculated as:

Code of Federal Regulations

EHCdc=[(MHCla) (0.190) (MHC1) (0.190) (MHC2) (0.125) (MHC3) (0.065) (MHC4) (0.065) (MHC5) (0.052) (MHC6) (0.044) (MHC7) (0.038) (MHC8) (0.039) (MHC9) (0.030) (MHC10) (0.162)]/[(BHP1a) (0.190) (BHP1) (0.190) (BHP2) (0.125) (BHP3) (0.065) (BHP4) (0.065) (BHP5) (0.052) (BHP6) (0.044) (BHP7) (0.038) (BHP8) (0.039) (BHP9) (0.030) (BHP10) (0.162)]

(3) In each mode, brake horsepower output is the power that the engine delivers as output (normally at the flywheel), as defined in § 92.2.

(i) For locomotive testing (or engine testing using a locomotive alternator/generator instead of a dynamometer), brake horsepower is calculated as:

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BHP=HPout/Aeff HPacc

Where:

HPout=Measured horsepower output of the alternator/generator.

Aeff=Efficiency of the alternator/generator.

HPacc=Accessory horsepower.

(ii) For engine dynamometer testing, brake horsepower is determined from the engine speed and torque.

(4) For locomotive equipped with features that shut the engine off after prolonged periods of idle, the measured mass emission rate Mi1 (and Mi1a as applicable) shall be multiplied by a factor equal to one minus the estimated fraction reduction in idling time that will result in use from the shutdown feature. Application of this adjustment is subject to the Administrator's approval.

(b) Throttle notch emissions. This paragraph (b) describes the calculation of throttle notch emissions for all operating modes, including: idle (normal and low, as applicable); dynamic brake; and traction power points. The throttle notch (operating mode) emission test results, final reported values and values used in paragraph (a)(1) of this section are calculated as follows:

(1) Brake specific emissions (Eij) in grams per brake horsepower-hour of each species i (i.e., HC, CO, NOX or PM and, if appropriate, THCE or NMHC) for each mode j:

(i) EHC mode =HC grams/BHP-hr=MHC mode /Measured BHP in mode.

Where:

MHC mode=Mass HC emissions (grams per hour) for each test mode.

(ii) ETHCE mode =THCE grams/BHP-hr=MTHCE mode /Measured BHP in mode.

Where:

MTHCE mode (Total hydrocarbon equivalent mass emissions (grams per hour) for each test mode):

=MHCj Σ (Mij) (MWCp)/MWCi

Mij=the mass emission rate oxygenated pollutant i for mode j.

MWCi=the molecular weight of pollutant i divided by the number of carbon atoms per molecule of pollutant i.

MWCp=the molecular weight of a typical petroleum fuel component divided by the number of carbon atoms per molecule of a typical petroleum fuel component=13.8756.

(iii) ENMHC mode =NMHC grams/BHP-hr=MNMHC mode /Measured BHP in mode.

Where:

MNMHC mode=Mass NMHC emissions (grams per hour) for each test mode.

(iv) ECO mode =CO grams/BHP-hr=MCO mode /Measured BHP in mode.

Where:

MCO mode=Mass CO emissions (grams per hour) for each test mode.

(v) ENOx mode =NOX grams/BHP-hr=MNOx mode /Measured BHP in mode.

Where:

MNOx mode=Mass NOX emissions (grams per hour) for each test mode.

(vi) EPM mode =PM grams/BHP-hr=MPM mode /Measured BHP in mode.

Where:

MPM mode=Mass PM emissions (grams per hour) for each test mode.

(vii) EAL mode =Aldehydes grams/BHP-hr=MAL mode /Measured BHP in mode.

Where:

MAL mode=Total aldehyde mass emissions (grams per hour) for each test mode.

(2) Mass Emissions—Raw exhaust measurements. For raw exhaust measurements mass emissions (grams per hour) of each species for each mode:

(i) General equations. (A) The mass emission rate, MX mode (g/hr), of each pollutant (HC, NOX. CO2, CO, CH4 CH3 OH, CH3 CH2 OH, CH2 O, CH3 CH2 O) for each operating mode for raw measurements is determined based on one of the following equations:

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MX mode=(DX/106)(DVol)(MWX/Vm)

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MX mode=(WX/106)(WVol)(MWX/Vm)

Where:

X designates the pollutant (e.g., HC), DX is the concentration of pollutant X (ppm or ppmC) on a dry basis, MWX is the molecular weight of the pollutant (g/mol), DVol is the total exhaust flow rate (ft3/hr) on a dry basis, WX is the concentration of pollutant X (ppm or ppmC) on a wet basis, WVol is the total exhaust flow rate (ft3/hr) on a wet basis, Vm is the volume of one mole of gas at standard temperature and pressure (ft3/mol).

(B) All measured volumes and volumetric flow rates must be corrected to standard temperature and pressure prior to calculations.

(ii) The following abbreviations and equations apply to this paragraph (b)(2):

α=Atomic hydrogen/carbon ratio of the fuel.

β=Atomic oxygen/carbon ratio of the fuel.

CMWf=Molecular weight of the fuel per carbon atom, or carbon molecular weight (g/moleC)=(12.011 1.008α 16.000β).

DCO=CO concentration in exhaust, ppm (dry).

DCO2=CO2 concentration in exhaust, percent (dry).

DHC=HC carbon concentration in exhaust, ppm C (dry).

DNOX=NOX concentration in exhaust, in ppm (dry).

DVol=Total exhaust flow rate (ft3/hr) on a dry basis; or

=(Vm)(Wf)/((CMWf) (DHC/106 DCO/106 DCO2/100)).

K=Water gas equilibrium constant=3.5.

Kw=Wet to dry correction factor.

MF=Mass flow-rate of fuel used in the engine in lb/hr=Wf/453.59.

MWC=Atomic weight of carbon=12.011.

MWCO=Molecular weight of CO=28.011.

MWH=Atomic weight of hydrogen=1.008.

MWNO2=Molecular weight of nitrogen dioxide (NO2)=46.008.

MWO=Molecular weight of atomic oxygen=16.000.

T=Temperature of inlet air ( °F).

Vm=Volume of one mole of gas at standard temperature and pressure (ft3/mole).

Wf=Mass flow-rate of fuel used in the engine, in grams/hr=(453.59)×(Mf lbs/hr).

WCO2=CO2 concentration in exhaust, percent (wet).

WHC=HC concentration in exhaust, ppm C (wet).

WVol=Total exhaust flow rate (ft3/hr) on a wet basis; or

=(Vm)(Wf)/((CMWf)(WHC/106 WCO/106 WCO2/100)).

(iii) Calculation of individual pollutant masses. Calculations for mass emission are shown here in multiple forms. One set of equations is used when sample is analyzed dry (equations where the concentrations are expressed as DX), and the other set is used when the sample is analyzed wet (equations where the concentrations are expressed as WX). When samples are analyzed for some constituents dry and for some constituents wet, the wet concentrations must be converted to dry concentrations, and the equations for dry concentrations used. Also, the equations for HC, NMHC, CO, and NOX have multiple forms that are algebraically equivalent: An explicit form that requires intermediate calculation of Vm and DVol or WVol; and an implicit form that uses only the concentrations (e.g., DCO) and the mass flow rate of the fuel. For these calculations, either form may be used.

(A) Hydrocarbons and nonmethane hydrocarbons.

(1) Hydrocarbons. (i) For petroleum-fueled engines:

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MHC mode

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=(DHC)CMWf(DVol)(106)/Vm

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=((DHC/106)(Wf)/((DCO/106) (DCO2/100) (DHC/106) (ΣDX/106)))

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MHC mode

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=(WHC)CMWf(WVol)(106)/Vm

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=((WHC/106)(Wf)/((WCO/106) (WCO2/100) (WHC/106) (Σ(WX/106)))

(ii) For alcohol-fueled engines:

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DHC=FID HC−Σ(rx)(DX)

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WHC=FID HC−Σ(rx)(WX)

Where:

FID HC=Concentration of “hydrocarbon” plus other organics such as methanol in exhaust as measured by the FID, ppm carbon equivalent.

rx=FID response to oxygenated species×(methanol, ethanol, or acetaldehyde).

DX=Concentration of oxygenated species×(methanol, ethanol, or acetaldehyde) in exhaust as determined from the dry exhaust sample, ppm carbon (e.g., DCH3OH, 2(DCH3CH2OH)).

WX=Concentration of oxygenated species×(methanol, ethanol, or acetaldehyde) in exhaust as determined from the wet exhaust sample, ppm carbon.

ΣDX=The sum of concentrations DX for all oxygenated species.

ΣWX=The sum of concentrations WX for all oxygenated species.

(2) Nonmethane hydrocarbons:

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MNMHC mode=(DNMHC)CMWf(DVol) (106)/Vm

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=((DNMHC/106)(Wf)/((DCO/106) (DCO2/100) (DHC/106)))

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MNMHC mode=(WNMHC)CMWf(WVol) (106)/Vm

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=((WNMHC/106)(Wf)/((WCO/106) (WCO2/100) (WHC/106)))

Where:

DNMHC=FID HC−(rCH4)(DCH4)

WNMHC=FID HC−(rCH4)(WCH4)

FID HC=Concentration of “hydrocarbon” plus other organics such as methane in exhaust as measured by the FID, ppm carbon equivalent.

rCH4=FID response to methane.

DCH4=Concentration of methane in exhaust as determined from the dry exhaust sample, ppm.

WCH4=Concentration of methane in exhaust as determined from the wet exhaust sample, ppm.

(B) Carbon monoxide:

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MCO mode=(DCO)MWCO(DVol)/106/Vm

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=((MWCO(DCO/106)(Wf)/((CMWf)(DCO/106) (DCO2/100) DHC/106) (ΣDX/106)))

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MCO mode=(WCO)MWCO(DVol)(106)/Vm

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((MWCO(WCO/106)(Wf)/((CMWf)(WCO/106) (WCO2/100) WHC/106) (ΣWX/106)))

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MNOx mode=(DNOX)MWNO2(DVol)(106)/Vm

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=((MWNO2(DNOX/106)(Wf)/((CMWf)(DCO/106) (DCO2/100) (DHC/106) (ΣDX/106)))

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MNOx mode=(WNOX)MWNO2(DVol)(106)/Vm

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=((MWNO2(WNOX/106)(Wf)/((CMWf)(WCO/106) (WCO2/100) (WHC/106) (ΣWX/106)))

(D) Methanol:

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MCH3OH mode=(DCH3OH/106)32.042(DVol)/Vm

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MCH3OH mode=(WCH3OH/106)32.042(WVol)/Vm

Where:

DCH3OH=(Vm)(106)[(C1×AV1) (C2×AV2)]/DVolMS.

WCH3OH=(Vm)(106)[(C1×AV1) (C2×AV2)]/WVolMS.

Ci=concentration of methanol in impinger i (1 or 2) in mol/ml.

AVi=Volume of absorbing reagent in impinger i (1 or 2) in ml.

DVolMS=Volume (standard ft3) of exhaust sample drawn through methanol impingers (dry).

WVolMS=Volume (standard ft3) of exhaust sample drawn through methanol impingers (wet).

(E) Ethanol:

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MCH3CH2OH mode=(DCH3CH2OH/106)23.035(DVol)/Vm

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MCH3CH2OH mode = (WCH3CH2OH/106)23.035(WVol)/Vm

Where:

DCH3CH2OH=(Vm)(106)[(C1×AV1)

(C2×AV2)]/DVolES.

WCH3CH2OH=(Vm)(106)[(C1×AV1) (C2×AV2)]/WVolES.

Ci=concentration of ethanol in impinger i (1 or 2) in mol/ml.

AVi=Volume of absorbing reagent in impinger i (1 or 2) in ml.

DVolES=Volume (standard ft3) of exhaust sample drawn through ethanol impingers (dry).

WVolES=Volume (standard ft3) of exhaust sample drawn through ethanol impingers (wet).

(F) Formaldehyde:

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MCH2O mode=(DCH2O/106)30.026(DVol)/Vm

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MCH2O mode=(WCH2O/106)30.026(WVol)/Vm

(1) If aldehydes are measured using impingers:

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DCH2O=(Vm)(106)[(C1×AV1) (C2×AV2)]/DVolFS

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WCH2O=(Vm)(106)[(C1×AV1) (C2×AV2)]/WVolFS

(2) If aldehydes are measured using cartridges:

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DCH2O=(Vm)(106)(CR×AVR)/DVolFS

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WCH2O=(Vm)(106)(CR×AVR)/WVolFS

(3) The following definitions apply to this paragraph (b)(2)(iii)(F):

AVi=Volume of absorbing reagent in impinger i (1 or 2) in ml.

AVR=Volume of absorbing reagent use to rinse the cartridge in ml.

Ci=concentration of formaldehyde in impinger i (1 or 2) in mol/ml.

CR=concentration of formaldehyde in solvent rinse in mol/ml.

DVolFS=Volume (standard ft3) of exhaust sample drawn through formaldehyde sampling system (dry).

WVolFS=Volume (standard ft3) of exhaust sample drawn through formaldehyde sampling system (wet).

(G) Acetaldehyde:

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MCH3CHO mode=(DCH3CHO/106)27.027(DVol)/Vm

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MCH3CHO mode=(WCH3CHO/106)27.027(WVol)/Vm

(1) If aldehydes are measured using impingers:

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DCH3CHO=(Vm)(106)[(C1×AV1) (C2× AV2)]/DVolAS

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WCH3CHO=(Vm)(106)[(C1×AV1) C2× AV2)]/WVolAS

(2) If aldehydes are measured using cartridges:

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DCH3CHO=(Vm)(106)(CR×AVR)/DVolAS

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WCH3CHO=(Vm)(106)(CR×AVR)/WVolAS

(3) The following definitions apply to this paragraph (b)(2)(iii)(G):

AVi=Volume of absorbing reagent in impinger i (1 or 2) in ml.

AVR=Volume of absorbing reagent use to rinse the cartridge in ml.

Ci=concentration of acetaldehyde in impinger i (1 or 2) in mol/ml.

CR=concentration of acetaldehyde in solvent rinse in mol/ml.

DVolAS=Volume (standard ft3) of exhaust sample drawn through acetaldehyde sampling system (dry).

WVolAS=Volume (standard ft3) of exhaust sample drawn through acetaldehyde sampling system (wet).

(iv) Conversion of wet concentrations to dry concentrations. Wet concentrations are converted to dry concentrations using the following equation:

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DX=KW WX

Where:

WX is the concentration of species X on a wet basis.

DX is the concentration of species X on a dry basis.

KW is a conversion factor=WVol/DVol=1 DH2O.

(A) Iterative calculation of conversion factor. The conversion factor KW is calculated from the fractional volume of water in the exhaust on a dry basis (DH2O=volume of water in exhaust/dry volume of exhaust). Precise calculation of the conversion factor KW must be done by iteration, since it requires the dry concentration of HC, but HC emissions are measured wet.

(1) The conversion factor is calculated by first assuming DHC=WHC to calculate DVol:

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DVol=(Vm)(Wf)/((CMWf)(DHC/106 DCO/106 DCO2/100))

(2) This estimate is then used in the following equations to calculate DVolair, then DH2O, then KW, which allows DHC to be determined more accurately from WHC:

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[Please see PDF for image: ER16AP98.009 ]

Where:

Y=Water volume concentration in intake air, volume fraction (dry).

DVolair=Air intake flow rate (ft3/hr) on a dry basis, measured, or calculated as:

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[Please see PDF for image: ER16AP98.010 ]

(3) The calculations are repeated using this estimate of DHC. If the new estimate for KW is not within one percent of the previous estimate, the iteration is repeated until the difference in KW between iterations is less than one percent.

(B) Alternate calculation of DH2O (approximation). The following approximation may be used for DH2O instead of the calculation in paragraph (b)(2)(iv)(A) of this section:

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[Please see PDF for image: ER16AP98.011 ]

Where:

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[Please see PDF for image: ER16AP98.012 ]

Y=Water volume concentration in intake air, volume fraction (dry).

(3) Mass Emissions—Dilute exhaust measurements. For dilute exhaust measurements mass emissions (grams per hour) of each species for each mode:

(i) General equations. The mass emission rate, Mx mode (g/hr) of each pollutant (HC, NOX. CO2, CO, CH4 CH3OH, CH3CH2OH, CH2O, CH3CH2O) for each operating mode for bag measurements and diesel continuously heated sampling system measurements is determined from the following equation:

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Mx mode=(Vmix)(Densityx)(Xconc)/(Vf)

Where:

x designates the pollutant (e.g., HC), Vmix is the total diluted exhaust volumetric flow rate (ft3/hr), Densityx is the specified density of the pollutant in the gas phase (g/ft3), Xconc is the fractional concentration of pollutant x (i.e., ppm/106, ppmC/106, or %/100), and Vf is the fraction of the raw exhaust that is diluted for analysis.

(ii) The following abbreviations and equations apply to paragraphs (b)(3)(i) through (b)(3)(iii)(J) of this section:

(A) DF=Dilution factor, which is the volumetric ratio of the dilution air to the raw exhaust sample for total dilution, calculated as:

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[Please see PDF for image: ER16AP98.013 ]

Where:

WCO2=Carbon dioxide concentration of the raw exhaust sample, in percent (wet).

WCO2e=Carbon dioxide concentration of the dilute exhaust sample, in percent (wet).

WCO2d=Carbon dioxide concentration of the dilution air, in percent (wet).

(B) Vmix =Diluted exhaust volumetric flow rate in cubic feet per hour corrected to standard conditions (528°R, and 760 mm Hg).

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=((CO2conc/102) (COconc/106) (HCconc/106))(Vmix)(CMWf)/Vm/Mf

(iii) Calculation of individual pollutants.

(A) MHC mode =Hydrocarbon emissions, in grams per hour by mode, are calculated using the following equations:

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MHC mode=(Vmix)(DensityHC)(HCconc/106)/Vf

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HCconc=HCe−(HCd)(1−(1/DF))

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HCe=FID HCe−Ξ(rx)(Xe)

Where:

DensityHC=Density of hydrocarbons=16.42 g/ft3 (0.5800 kg/m3) for #l petroleum diesel fuel, 16.27 g/ft3 (0.5746 kg/m3) for #2 diesel, and 16.33 g/ft3 (0.5767 kg/m3) for other fuels, assuming an average carbon to hydrogen ratio of 1:1.93 for #1 petroleum diesel fuel, 1:1.80 for #2 petroleum diesel fuel, and 1:1.85 for hydrocarbons in other fuels at standard conditions.

HCconc=Hydrocarbon concentration of the dilute exhaust sample corrected for background, in ppm carbon equivalent (i.e., equivalent propane×3).

HCe=Hydrocarbon concentration of the dilute exhaust bag sample, or for diesel continuous heated sampling systems, average hydrocarbon concentration of the dilute exhaust sample as determined from the integrated HC traces, in ppm carbon equivalent. For petroleum-fueled engines, HCe is the FID measurement. For methanol-fueled and ethanol-fueled engines:

FID HCe=Concentration of hydrocarbon plus methanol, ethanol and acetaldehyde in dilute exhaust as measured by the FID, ppm carbon equivalent.

rx=FID response to oxygenated species x (methanol, ethanol or acetaldehyde).

Xe=Concentration of species x (methanol, ethanol or acetaldehyde) in dilute exhaust as determined from the dilute exhaust sample, ppm carbon.

HCd=Hydrocarbon concentration of the dilution air as measured, in ppm carbon equivalent.

(B) MNOx mode = Oxides of nitrogen emissions, in grams per hour by mode, are calculated using the following equations:

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MNOx mode=(Vmix) (DensityNO2) (NOxconc/10 6) /Vf

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NOxconc=(NOxe−NOxd(1−(1/DF)))

Where:

DensityNO2=Density of oxides of nitrogen is 54.16 g/ft3 (1.913 kg/m3), assuming they are in the form of nitrogen dioxide, at standard conditions.

NOxconc=Oxides of nitrogen concentration of the dilute exhaust sample corrected for background, in ppm.

NOxe=Oxides of nitrogen concentration of the dilute exhaust bag sample as measured, in ppm.

NOxd=Oxides of nitrogen concentration of the dilution air as measured, in ppm.

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MCO2 mode=(Vmix) (Density CO2) (CO2conc/102) /Vf

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CO2conc=CO2.−CO2.(1−(1/DF))

Where:

Density CO2=Density of carbon dioxide is 51.81 g/ft3 (1.830 kg/m3), at standard conditions.

CO2conc=Carbon dioxide concentration of the dilute exhaust sample corrected for background, in percent.

CO2.=Carbon dioxide concentration of the dilute exhaust bag sample, in percent.

CO2.=Carbon dioxide concentration of the dilution air as measured, in percent.

(D) (1) MCO mode =Carbon monoxide emissions, in grams per hour by mode, are calculated using the following equations:

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MCO mode=(Vmix)(DensityCO)(COconc/106)/Vf

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COconc=COe−COd(1−(1/DF))

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COd=(1−0.000323R)COdm

Where:

DensityCO=Density of carbon monoxide is 32.97 g/ft3 (1.164 kg/m3), at standard conditions.

COconc=Carbon monoxide concentration of the dilute exhaust sample corrected for background, water vapor, and CO2 extraction, ppm.

COe=Carbon monoxide concentration of the dilute exhaust sample volume corrected for water vapor and carbon dioxide extraction, in ppm.

COe=(1−(0.01 0.005/α)CO2.−0.000323RH)COem, where α is the hydrogen to carbon ratio as measured for the fuel used.

COem=Carbon monoxide concentration of the dilute exhaust sample as measured, in ppm.

RH = Relative humidity of the dilution air, percent.

COd=Carbon monoxide concentration of the dilution air corrected for water vapor extraction, in ppm.

COdm=Carbon monoxide concentration of the dilution air sample as measured, in ppm.

(2) If a CO instrument that meets the criteria specified in 40 CFR part 1065, subpart C, is used without a sample dryer according to 40 CFR 1065.145, COem must be substituted directly for COe and COdm must be substituted directly for COd.

(E) MCH4 mode =Methane emissions corrected for background, in gram per hour by mode, are calculated using the following equations:

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MCH4 mode=(Vmix) (DensityCH4) (CH4conc/106) /Vf

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CH4conc=CCH4e−CCH4d(1−(1/DF))

Where:

DensityCH4=Density of methane is 18.89 g/ft3 at 68 °F (20 °C) and 760 mm Hg (101.3kPa) pressure.

CH4conc=Methane concentration of the dilute exhaust corrected for background, in ppm.

CCH4e=Methane concentration in the dilute exhaust, in ppm.

CCH4d=Methane concentration in the dilution air, in ppm.

(F) MCH3OH mode =Methanol emissions corrected for background, in gram per hour by mode, are calculated using the following equations:

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MCH3OH mode=(Vmix)(DensityCH3OH) (CH3OHconc/106)/Vf

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CH3OHconc=CCH3OHe−CCH3OHd(1−(1/DF))

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CCH3OHe=((3.817)(10−2)(TEM)(((CS1)(AVS1)) (CS2) (AVS2)))/((PB)(VEM))

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CCH3OHd=((3.817)(10−2)(TDM)(((CD1) (AVD1)) (CD2) (AVD2)))/((PB)(VDM))

Where:

DensityCH3OH=Density of methanol is 37.71 g/ft3 (1.332 kg/m3), at 68 °F (20 °C) and 760 mm Hg (101.3kPa) pressure.

CH3OHconc=Methanol concentration of the dilute exhaust corrected for background, in ppm.

CCH3OHe=Methanol concentration in the dilute exhaust, in ppm.

CCH3OHd=Methanol concentration in the dilution air, in ppm.

TEM=Temperature of methanol sample withdrawn from dilute exhaust, °R.

TDM=Temperature of methanol sample withdrawn from dilution air, °R.

PB=Barometric pressure during test, mm Hg.

VEM=Volume of methanol sample withdrawn from dilute exhaust, ft 3.

VDM=Volume of methanol sample withdrawn from dilution air, ft 3.

CS=GC concentration of aqueous sample drawn from dilute exhaust, µg/ml.

CD=GC concentration of aqueous sample drawn from dilution air, µg/ml.

AVS=Volume of absorbing reagent (deionized water) in impinger through which methanol sample from dilute exhaust is drawn, ml.

AVD=Volume of absorbing reagent (deionized water) in impinger through which methanol sample from dilution air is drawn, ml.

1=first impinger.

2=second impinger.

(G) MC2H5OH mode =Ethanol emissions corrected for background, in gram per hour by mode, are calculated using the following equations:

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