6.13 Aircraft Fueling
Categories 79, 80, and 1906
6.13.1 Introduction
Categories 79, 80, and 1906 account for organic emissions (TOG and ROG) that occur during the refueling (including spillage) of general aviation, commercial, and military aircraft with aviation gasoline or jet fuel.
There are two systems used by airports for the refueling of aircraft: over-the-wing and single point pressure. Over-the-wing fueling is like service station fueling of automobiles but without a vapor recovery system. Single point pressure systems use pressure and a closed connection to refuel aircraft. The gasoline vapors in the aircraft tank are vented into the atmosphere through vents on the wings. Other sources of emissions covered by these categories are those from the working and breathing losses that occur during underground storage tank refueling.
6.13.2 Methodology
Point Sources
Point Sources are operations that emit air pollution into the atmosphere at a fixed location within a facility, for which the Air District has issued a permit to operate, e.g., refinery cooling towers. These could also be a collection of similar equipment / sources located across multiple facilities, e.g., reciprocating engines.
During the permit to operate (PTO) issuance process, the BAAQMD collects information from the operating facility and/or determines from published literature, e.g., EPA’s AP-42, characteristics of a source including maximum throughput, emission factors for emitted pollutants, and control factors associated with downstream abatement devices. These characteristics are then stored for future use in the BAAQMD’s internal database. Facilities that hold a permit to operate are required to renew this permit periodically (this period varies based on facility and source type). Upon renewal, the facilities are requested to provide any updates to source characteristics as well as the source throughput for the last 12 months. This throughput, in combination with the emission factors and controls factors stored in the internal database, are used to estimate annual emissions at the source level. These source level emissions are then sorted and aggregated into categories.
Category 80 is a point source category and follows the above methodology for emissions estimates. Category 80 accounts for emissions from refueling of jet engine aircraft with Jet-A fuel.
Area Sources
Categories 79 and 1906 are considered an area source category since they cover facilities / emission sources that are not directly permitted by the District, and hence not systematically cataloged. Emissions for area source categories are determined using the formula:
Current Year Emissions = Base Year Emission X Growth Profile, and,
Base Year Emission = Throughput X Control Factor X Emission Factor
where,
- throughput or activity data for applicable base year(s) is determined using a top-down approach (e.g. state-, national-level data);
- emission factor is derived from general literature, specific literature and reports, and/or source testing results provided by Air District staff;
- control factor (if applicable) is determined by District and state rules and regulations in effect;
- and, historical backcasting and forecasting of emissions is based on growth profiles as outlined in the Trends section of this chapter
More details on throughput, county distribution, emission factors and controls is provided in the following subsections.
(a) Activity Data / Throughput
For area source categories 79 and 1906, the amounts of aviation gasoline and Jet-A fuel usage at San Jose International Airport (SJC) and Oakland International Airport (OAK) were obtained from the airport Monthly Activity Reports. For some airports fuel usage information was not readily available. The fuel usage at these airports was determined by apportioning the Oakland Airport fuel usage amounts with the relative number of aircraft operations at these airports.
(b) County Distribution / Fractions
Emissions were distributed into the nine counties based on aircraft operations activity at airports in each Bay Area county.
(c) Emission Factors
The uncontrolled emission factors of gasoline service station are used for aviation gasoline refueling with over-the-wing system. The emission factors are chosen based on the Environmental Protection Agency (EPA) document AP-42 and engineering judgment201. Total organic (TOG) emission factors used for categories 79 and 1906 are 21.2 and 0.78 (lbs/1000 gallons), respectively.
Point source emission factors are specific to device and facility as noted in the Methodology section above.
(d) Control Factors
The Air District adopted Regulation 8, Rule 7 in 1992 for pressure-vacuum valve requirement for gasoline dispensing facilities. The Regulation 8, Rule 7 required 95 percent control of fugitive gasoline emissions with an estimated control effectiveness of 9 percent. This control effectiveness provided a net emission reduction of 8.55% during a period of one year (1992-1993).
(e) Speciation
The ROG/TOG ratios applied to this category or this group of related categories are based on an Air District internal speciation profile. Multiple data sources have been used for developing speciation profiles, such as Air District-approved source tests, TOG speciation ratios used by other regional air quality agencies, and relevant literature including latest speciation profiles developed by CARB202 and the US Environmental Protection Agency203.
For category 79, ROG constitutes 95% of TOG.
For category 1906, ROG constitutes 83% of TOG.
For category 80, ROG constitutes 100% of TOG.
Further assessment and improvement of ROG/ TOG speciation profiles has been planned in future inventory updates.
(f) Sample Calculations
The following example shows Category 79 TOG emission calculation for year 2015 for 27,000,000 gallons of aviation gasoline dispensed:
TOG Emissions (tons / day) = Throughput (thousand gallons/year) x Emission Factor (lbs/1000 gallons) x Growth Factor x Control Factor x (ton/ lbs) x (year/days)
TOG Emissions = (27,000) x (21.2) x (1.0) x (0.915) x (1/2000) x (1/365) = 0.717 (tons/ day)
6.13.3 Changes in Methodology
No changes to methodology were made in this version of the base year emissions inventory.
6.13.4 Emissions
A summary of emissions by category, county, and year are available via the associated data dashboard for this inventory publication.
6.13.5 Trends
Emissions trends tend to follow the aircraft activity in terms of number of aircraft operations that take place at the Bay Area airports and revenue passenger miles.
(a) Historical Emissions / History
For category 79, historical emission trends were based on the aircraft operations trends at San Jose International Airport. These categories were created to account for the organic emissions at filling stations during aircraft refueling of aviation gasoline and Jet-A fuel during 1987 Base Year emission inventory.
Historical emissions for point source emissions (categories 80) are derived from source-specific throughputs provided by the permitted facility, compiled/reported emission factors, and regulation-based control factors. This information is archived in the BAAQMD’s internal database which is queried to retrieve the data for historical and current years. Interpolation techniques to account for missing data are used when necessary, this is the case for years 1991-1992.
(b) Future Projections / Growth
For all categories, future projections to year 2040 are based on estimates of aircraft operations at the Bay Area airports and revenue passenger miles as predicted by the Federal Aviation Administration (FAA)204. For point source category 80, forecasting is applied after year 2020. For area source categories 79 and 1906, forecasting is applied after year 2015.
Forecasting for all categories follows the general procedure outlined below:
\[ \text{PE} = \text{Gr} * \text{Ci} * \text{Ei} \]
\(PE\) = projected emissions of pollutant i in a future year
\(Gr\) = growth rate by economic profile of industry or population
\(Ci\) = control factor of pollutant i based on adopted rules and regulations
\(Ei\) = base year emissions of pollutant i
6.13.6 Uncertainties
Uncertainties associated with the emission estimates from aircraft refueling can occur due to malfunctioning of emission control equipment such as the pressure-vacuum valves at the fuel dispensing facilities. Malfunctioning equipment will not efficiently capture evaporated gasoline and can lead to an increase in fugitive TOG emissions.
6.13.7 Contact
Author: Sukarn Claire
Reviewer: Ariana Husain
Last Update: November 06, 2023
6.13.8 References & Footnotes
USEPA. Document AP-42. Compilation of Air Pollutant Emissions Factors. https://www.epa.gov/air-emissions-factors-and-quantification/ap-42-compilation-air-emissions-factors↩︎
ORGPROF. CARB. 2022. https://ww2.arb.ca.gov/speciation-profiles-used-carb-modeling↩︎
SPECIATE. USEPA. 2022. https://www.epa.gov/air-emissions-modeling/speciate↩︎
The Federal Aviation Administration (FAA). [accessed 2022 July 14]. https://www.faa.gov/data_research/aviation/taf/↩︎