9.1 Lawn and Garden Equipment

Categories 1647, 1648, 1649, 1650, and 1651

9.1.1 Introduction

Categories 1647, 1648, 1649, 1650, and 1651 account for emissions (NOx, CO, PM, PM10, PM2.5, ROG, SO2, and TOG) from lawn, garden and other general utility equipment, powered by two and four stroke gasoline engines of less than 20 horsepower and diesel engines. Two-stroke engines have several attributes that are advantageous for applications such as leaf blowers. The two-stroke engines are lightweight and operate in multi-position, allowing for great flexibility in equipment applications. Typical two-stroke engines feed fuel/oil mixture into combustion chamber. A major disadvantage of two-stroke engines is high exhaust emissions. The major pollutants from a two-stroke engines are: oil-base particulates, reactive organics (a mixture of burned and unburned hydrocarbons), and carbon monoxide. Lawn, garden and other diesel equipment includes products such as walk behind mowers, garden tractors, hedge and lawn trimmers and leaf blowers. General utility equipment includes chain saws, generators, compressors, pumps, welding machines, grinders and shredders.

9.1.2 Methodology

The Lawn and Garden Equipment emissions are derived by California Air Resources Board (CARB) inventory staff. This significant emissions dataset, sorted by county, is published every few years and is a product of the State Implementation Plan (SIP) emissions document formally known as the California Emissions Projection Analysis Model (CEPAM) inventory. BAAQMD staff export the emissions data directly from CEPAM into the District’s Base Year inventory package. This calculation approach and collection of categories are internally termed as “CARB Source Categories”.

This base year inventory uses the 2016 CEPAMv1.05341 to estimate emissions from “CARB Source Categories”. This version of the CEPAM derives emissions from a 2012 base year inventory and contains backcasts and forecasts from year-2000 to year-2035. All applicable regulatory and technological controls are assumed to be built into the CEPAM dataset during CARB staff’s inventory computation work. After the emissions data are exported, the inventory for CARB Source categories is taken through a quality assurance (QA) process.

9.1.3 Changes in Methodology

Emissions data were obtained from the CARB’s 2016 CEPAMv1.051. In comparison, the emissions in the previous inventory methodology involved area source categories derived from the CARB’s OFFROAD2007 model.

9.1.4 Emissions

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

9.1.6 Uncertainties

The estimated Lawn and Garden Equipment emissions for Solano and Sonoma counties under District’s jurisdiction may contribute to an increased uncertainty of the Bay Area Off Road emissions.

9.1.7 Contact

Author: Michael Nguyen

Reviewer: Ariana Husain

Last Update: November 06, 2023

9.1.8 References & Footnotes


  1. CARB. 2016. California Emissions Projection Analysis Model (CEPAM) inventory, https://www.arb.ca.gov/app/emsinv/2016ozsip/2016ozsip/fcemssumcat_2016o3sip105.php↩︎

  2. CARB. 1995. California Exhaust Emission Standards and Test Procedures For 1995 and Later: Small Off-Road Engines. https://ww2.arb.ca.gov/sites/default/files/barcu/regact/sore/test_fin.pdf?_ga=2.97100055.962285900.1646782104-423543219.1584725377↩︎

  3. CA. 2021. CA Assembly Bill No. 1346, https://leginfo.legislature.ca.gov/faces/billNavClient.xhtml?bill_id=202120220AB1346↩︎