• Base Year Inventory Methodology
  • 1 Introduction
  • 2 Petroleum Refining Facilities
    • 2.1 General Refinery Emissions
    • 2.2 Refinery Fugitive Emissions
    • 2.3 Refinery Process Vessel Depressurization
  • 3 Chemical Manufacturing Facilities
    • 3.1 Coatings & Inks
    • 3.2 Resins
    • 3.3 Pharmaceuticals & Cosmetics
    • 3.4 All Other Chemical Plants
  • 4 Other Industrial and Commercial Processes
    • 4.1 Large and Small Bakeries
    • 4.2 Cooking: Charbroiling, Deep Fat Frying, and Unspecified (Griddles)
    • 4.3 Wineries / Breweries - Fermentation
    • 4.4 Wineries / Breweries - Brandy Aging
    • 4.5 Other Food & Agricultural Processing
    • 4.6 Metallurgical, Foundry & Forging Operations; Metal Recycling & Shredding Operations
    • 4.7 Wood Products Manufacturing
    • 4.8 Cement Manufacturing & Combustion
    • 4.9 Contaminated Soil Aeration
    • 4.10 Air Stripping and Soil Vapor Extraction
    • 4.11 Asphaltic Concrete Plants
    • 4.12 Concrete Batching
    • 4.13 Glass and Related Products
    • 4.14 Stone, Sand, and Gravel
    • 4.15 Sand Blasting
    • 4.16 Semiconductor Manufacturing
    • 4.17 Flexible & Rigid Discs Manufacturing
    • 4.18 Fiberglass Manufacturing
    • 4.19 Rubber Manufacturing
    • 4.20 Plastic Products Manufacturing
    • 4.21 Oil Production Fields
    • 4.22 Gas Production Fields
    • 4.23 Other Miscellaneous Industrial/Commercial
  • 5 Waste Management
    • 5.1 Wastewater Treatment
    • 5.2 Landfills
    • 5.3 Biosolids Land Application
    • 5.4 Other Waste Management
    • 5.5 Composting
  • 6 Petroleum Products Evaporation and Leakage
    • 6.1 Storage Tanks
    • 6.2 Refinery and Marine Loading Operations
    • 6.3 Natural Gas Distribution
    • 6.4 Gasoline Bulk Plant Storage Tanks
    • 6.5 Non-Gasoline Terminals and Bulk Plants Storage
    • 6.6 Gasoline Truck Loading
    • 6.7 Gasoline Truck Transport
    • 6.8 Gasoline Filling Station Spillage
    • 6.9 Gasoline Filling Station Storage
    • 6.10 Gasoline Filling Station Fueling
    • 6.11 Gasoline Filling Station - Excess Emissions
    • 6.12 Portable Fuel Container Spillage
    • 6.13 Aircraft Fueling
    • 6.14 Ship and Boat Fueling
    • 6.15 Other Fueling
    • 6.16 Sterilizer Venting
    • 6.17 Asphalt Paving
    • 6.18 Asphalt Roofing
    • 6.19 Solvent Cleaning Operations
    • 6.20 Dry Cleaning
    • 6.21 Printing
    • 6.22 Adhesive Sealants
    • 6.23 Structures Coatings
    • 6.24 Industrial Commercial Coatings
    • 6.25 Miscellaneous Organic Evaporation
    • 6.26 Vacuum Truck at Refinery, Marine, Bulk Terminals - Petroleum Product
  • 7 Stationary Combustion of Fuels
    • 7.1 Domestic Natural Gas Combustion
    • 7.2 Domestic Fuel Combustion - LPG & Liquid Fuel
    • 7.3 Domestic Solid Fuel (Wood)
    • 7.4 Cogeneration
    • 7.5 Power Plants
    • 7.6 Power Plants: Gas/Oil Turbines
    • 7.7 Oil Refineries - External Combustion
    • 7.8 Reciprocating Engines
    • 7.9 Reciprocating Engines - Excessive Use
    • 7.10 Turbines
    • 7.11 Other External Combustion - Natural Gas
    • 7.12 Other External Combustion - All Other Fuels
  • 8 Burning of Waste Material
    • 8.1 Incineration
    • 8.2 Planned Agricultural Burning
  • 9 On-Road and Off-Road Mobile Sources
    • 9.1 Lawn and Garden Equipment
    • 9.2 Transportation Refrigeration Units
    • 9.3 Agricultural Equipment
    • 9.4 Construction, Mining, Industrial/Light Commercial, & Other Off-Road Equipment
    • 9.5 Locomotives
    • 9.6 Off Road Motorcycles & All Terrain Vehicles
    • 9.7 Ships - Mobile Marine Ship
    • 9.8 Commercial Harbor Crafts
    • 9.9 Recreational Boats
    • 9.10 Commercial Aircraft, Jet
    • 9.11 Commercial Aircraft, Piston
    • 9.12 General Aviation, Jet
    • 9.13 General Aviation, Piston
    • 9.14 Military Aircraft, Jet
    • 9.15 Military Aircraft, Piston
    • 9.16 Agricultural Aircraft
    • 9.17 On-Road Motor Vehicles
    • 9.18 Airport Ground Support Equipment
  • 10 Miscellaneous Other Sources
    • 10.1 Construction Operations
    • 10.2 Farming Operations
    • 10.3 Accidental Structural Fires
    • 10.4 Accidental Vegetation Fires
    • 10.5 Accidental Automobile Fires
    • 10.6 Paved Road Dust
    • 10.7 Unpaved Roads
    • 10.8 Animal Waste, Livestock
    • 10.9 Animal Waste, Other
    • 10.10 Municipal Sanitary Sewers
    • 10.11 Windblown Dust
    • 10.12 Cigarette and Tobacco Smoke
    • 10.13 Non-Consumer Pesticides
    • 10.14 Consumer Products
    • 10.15 Biogenic Emissions
    • 10.16 Ozone Depleting Substance Substitutes (ODSS)
    • 10.17 Natural Gas Distribution - Leakage
  • Published with bookdown

Base Year Inventory Methodology

4.13 Glass and Related Products

Category 40

4.13.1 Introduction

Category 40 accounts for point source pollutant emissions (NOx, CO, PM, PM10, PM2.5, ROG, SO2, TOG) from glass manufacturing plant plants. The main pollutant emitted by glass manufacturing plant is particulates in the form of dust. Particulates result from volatilization of materials in the melt that combine with gases and form condensates. Emissions from the forming and finishing phase depend upon the type of glass being manufactured. Emissions for glass and related product manufacturing can be categorized by three production phases: raw materials handling, glass melting and refining, and forming and finishing. The raw materials handling phase is the major fugitive dust emissions. The emissions are generated at each of the material transfer points. The emissions from forming and finishing phase are solid particles of glass and related products. (Nitrogen Oxide, NOx, emissions are the result of electric furnace operation; sulfur dioxide, SO2, emissions are the result of glass melting in furnaces.)

4.13.2 Methodology

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.

Further speciation and quality assurance of emissions are performed as a part of the inventory process. The BAAQMD staff also perform a systematic crosswalk between CEPAM’s source category classification (Emission Inventory Code - EICs) and the District’s source category classification (category identification number - cat_ids), which ensures consistency in the annual emissions reporting process (CEIDARS) to California Air Resources Board. The last part of the inventory development process includes forecasting and back casting, and aggregation into sub-sectors and sectors for documentation purposes. For those years where no data is available, emissions data are backcasted to year-1990, as well as forecasted to year-2040 using either interpolation or another mathematical approach (see Trends section). Finally, emissions trends spanning from year 1990-2040 for each category and pollutant are evaluated for anomalies that are then investigated and addressed.

Category 40 is considered a point source category and follows the above methodology for emissions estimates.

The PM2.5/PM and the PM10/PM 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, PM speciation ratios used by other regional air quality agencies, and other relevant literature. These ratios are not necessarily consistent with the latest speciation profiles developed by CARB79 or the US Environmental Protection Agency80. For this category or group of categories, PM2.5 constitutes 96% of total PM and PM10 constitutes 98% of total PM. The Air District staff routinely review speciation profiles and may update ratios as needed for improving emissions estimates.

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 CARB81 and the US Environmental Protection Agency. For this category or group of categories, ROG constitutes 70% of TOG.

4.13.3 Changes in Methodology

There are no changes to methodology for Glass and Related Products (category 40).

4.13.4 Emissions

A summary of emissions by category, county, and year are available via the associated data dashboard for this inventory publication.

4.13.5 Trends

For the historical lifespan of this category, there have been five facilities that contribute the bulk of particulate emissions. In 2016, a reduction in particulate matter emissions is seen due to two of these five facilities being shutdown. One of these facilities contributed to approximately 43% of PM emissions in the year prior, 2015. In 2018, further reduction of particulates was achieved due to the amendment of District’s Regulation 6, Rule 182. However, the Staff Report for this rule found these amendments to have little affect on this category as the remaining operations already had the required abatement of emissions implemented on site. Of the five major facilities mentioned, only one is still in operation as of this base year inventory.

(a) Historical Emissions / History

Historical emissions for point source emissions 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.

In 1963, there was at least 50% reduction of particulate emissions from equipment brought about by the District’s [Regulation 6] on visible emissions from the Ringlemann 2 standard. In 1970 there was at least an additional 25% reduction in particulates from the Ringlemann 1 standard. Projections of emissions to 2040 are assumed to be constant starting from 2020 as the trends for this category are highly dependent on the business of one facility.

(b) Future Projections / Growth

Forecasting of point source emissions is done based on calculations as shown in the equation below using recently updated growth profiles and a base year of 2020. The growth profiles for the current base year inventory have been verified and updated to represent the most likely surrogate for growing emissions for a given category up to year 2040. Forecasting for point source emissions includes impact of in-place regulations, but does not include estimation of controls that will theoretically be implemented as part of future policy emission targets or proposed regulation and legislation.

\[ \text{PE} = \text{Gr} * \text{Ci} * \text{Ei} \] \(PE\) = projected emissions of pollutant i in a past or 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

Projections of emissions to 2040 were based on ABAG’s 2009 Manufacturing Employment growth profile.

4.13.6 Uncertainties

The major pollutant of concern for this category is particulate matter and the major contributor of PM for this category can be attributed to one major facility still in operation. For this facility, the emission factors and throughputs are specific to the sources on site. For this reason, the uncertainty in this category is dictated by the margin of error in the emission factors as determined by the site operator which is unknown at this time.

4.13.7 Contact

Author: Michael Nguyen

Reviewer: Ariana Husain

Last Update: November 06, 2023

4.13.8 References & Footnotes


  1. CARB. 2022.PMSIZE https://ww2.arb.ca.gov/speciation-profiles-used-carb-modeling↩︎

  2. EPA. 2022. SPECIATE https://www.epa.gov/air-emissions-modeling/speciate↩︎

  3. CARB. 2022.ORGPROF https://ww2.arb.ca.gov/speciation-profiles-used-carb-modeling↩︎

  4. BAAQMD. 2018. Regulations 6, Rule 1 - Particulate Matter General Requirements, https://www.baaqmd.gov/~/media/dotgov/files/rules/archive-2018-regulation-6-rule-1/documents/rg0601-pdf.pdf?la=en↩︎