Sustainability


Environmental Product Declarations

The low environmental impacts of structural steel are vetted by third parties, are transparently disclosed in Environmental Product Declarations (EPD), and comprehensively represent steel construction products.


The structural steel industry actively supports the transparent reporting of environmental impacts associated with construction products. Many rating systems (LEED ), standards (ASHRAE), green building codes (IgCC), policy authors, and specific customers require the submission of environmental product declarations (EPDs) for products delivered to the project site.

Where can I find U.S. mill-specific EPDs?

Hot-rolled Sections

Notes:

  • The table represents the most recently published GWP data from relevant domestic structural steel locations as of December 27, 2024.
  • The intent of the table is solely to provide a quick reference summary for those trying to comply with GWP procurement policies such as Buy Clean.
  • The table is not intended to provide a basis from which policy makers could determine industry average performance. Notably, we estimate that collective LCA uncertainties affect the results in the range of 10-20%. If you are a Buy Clean policy author, see AISC’s Buy Clean Guidance for Structural Steel Products.
  • The table is not intended to make direct comparisons between producers. Life Cycle Assessment (LCA) literature (including ISO standards, the North American Steel Construction Products Product Category Rule (PCR), and each EPD in the table) makes clear that EPD comparability is limited and urges caution when comparing EPDs outside the context of a robust whole-building LCA. In order to make comparisons, differences in background datasets, age of primary data, impact assessment factors, LCA methodologies, PCR versions, and more must be considered.

Plate

Notes:

  • The table represents the most recently published GWP data from relevant domestic structural steel locations as of December 27, 2024.
  • The intent of the table is solely to provide a quick reference summary for those trying to comply with GWP procurement policies such as Buy Clean.
  • The table is not intended to provide a basis from which policy makers could determine industry average performance. Notably, we estimate that collective LCA uncertainties affect the results in the range of 10-20%. If you are a Buy Clean policy author, see AISC’s Buy Clean Guidance for Structural Steel Products.
  • The table is not intended to make direct comparisons between producers. Life Cycle Assessment (LCA) literature (including ISO standards, the North American Steel Construction Products Product Category Rule (PCR), and each EPD in the table) makes clear that EPD comparability is limited and urges caution when comparing EPDs outside the context of a robust whole-building LCA. In order to make comparisons, differences in background datasets, age of primary data, impact assessment factors, LCA methodologies, PCR versions, and more must be considered.

Hollow Structural Sections

Notes:

  • The table represents the most recently published GWP data from relevant domestic structural steel locations as of January 13, 2025.
  • The intent of the table is solely to provide a quick reference summary for those trying to comply with GWP procurement policies such as Buy Clean.
  • The table is not intended to provide a basis from which policy makers could determine industry average performance. Notably, we estimate that collective LCA uncertainties affect the results in the range of 10-20%. If you are a Buy Clean policy author, see AISC’s Buy Clean Guidance for Structural Steel Products.
  • The table is not intended to make direct comparisons between producers. Life Cycle Assessment (LCA) literature (including ISO standards, the North American Steel Construction Products Product Category Rule (PCR), and each EPD in the table) makes clear that EPD comparability is limited and urges caution when comparing EPDs outside the context of a robust whole-building LCA. In order to make comparisons, differences in background datasets, age of primary data, impact assessment factors, LCA methodologies, PCR versions, and more must be considered.

Open-Web Steel Joists

Notes:

  • The table represents the most recently published GWP data from relevant domestic structural steel locations as of December 27, 2024.
  • The intent of the table is solely to provide a quick reference summary for those trying to comply with GWP procurement policies such as Buy Clean.
  • The table is not intended to provide a basis from which policy makers could determine industry average performance. Notably, we estimate that collective LCA uncertainties affect the results in the range of 10-20%. If you are a Buy Clean policy author, see AISC’s Buy Clean Guidance for Structural Steel Products.
  • The table is not intended to make direct comparisons between producers. Life Cycle Assessment (LCA) literature (including ISO standards, the North American Steel Construction Products Product Category Rule (PCR), and each EPD in the table) makes clear that EPD comparability is limited and urges caution when comparing EPDs outside the context of a robust whole-building LCA. In order to make comparisons, differences in background datasets, age of primary data, impact assessment factors, LCA methodologies, PCR versions, and more must be considered.

Steel Deck

Notes:

  • The table represents the most recently published GWP data from relevant domestic structural steel locations as of December 27, 2024.
  • The intent of the table is solely to provide a quick reference summary for those trying to comply with GWP procurement policies such as Buy Clean.
  • The table is not intended to provide a basis from which policy makers could determine industry average performance. Notably, we estimate that collective LCA uncertainties affect the results in the range of 10-20%. If you are a Buy Clean policy author, see AISC’s Buy Clean Guidance for Structural Steel Products.
  • The table is not intended to make direct comparisons between producers. Life Cycle Assessment (LCA) literature (including ISO standards, the North American Steel Construction Products Product Category Rule (PCR), and each EPD in the table) makes clear that EPD comparability is limited and urges caution when comparing EPDs outside the context of a robust whole-building LCA. In order to make comparisons, differences in background datasets, age of primary data, impact assessment factors, LCA methodologies, PCR versions, and more must be considered.

Where can I find Industry-Wide EPDs?

AISC develops industry-wide EPDs for three products:

Industry-wide EPDs meet ISO standards to ensure they are representative of their industries. As such, they are the appropriate reference for those conducting whole building life cycle assessments (WBLCAs) of the built environment. See the background report.

Additionally, another representation of the carbon-emission intensity of domestic steel construction products is found in the report, Global Warming Potential Impacts of Domestic Steel Construction Products, authored and published by the domestic steel construction industry in support of the FHWA Low-Carbon Transportation Materials (LCTM) Grant Program.

What is an EPD?

EPDs

An Environmental Product Declaration (EPD) is a standardized document that provides detailed and third-party verified information about the environmental impact of a product throughout its lifecycle. It follows international standards and covers aspects such as raw material extraction, production, transportation, use, and end-of-life disposal or recycling. For specifiers, an EPD offers transparent data that can inform sustainable design decisions, support green building certifications like LEED or GreenGlobes, and help in selecting materials that align with environmental performance goals.

What is an LCA?

Life Cycle Assessment (LCA) is a systematic and comprehensive method used to evaluate the environmental impacts of a product, material, process, or service throughout its entire life cycle. This assessment considers all stages of a product's life, from the extraction of raw materials through to processing, manufacturing, distribution, use, and ultimately disposal or recycling.

LCA

In Life Cycle Assessment (LCA), structural material selection impacts the product stage and end-of-life stage most. Modules A1 to A3 focus on the product stage, covering the initial phases of a product's lifecycle, and modules C1 to C4 focus on end of life. These modules are essential for understanding the environmental impact of a building. Here's a breakdown of the product module:

Module A1 (Raw Material Supply): This stage includes the extraction and processing of raw materials used in the product. It covers activities like mining, harvesting, and the initial processing of these materials to make them suitable for production. For many steel construction products, the collection of scrap metal constitutes the majority of raw material supply.

Module A2 (Transport): This module deals with the transportation of raw materials to the production or manufacturing site. It includes the environmental impacts of moving these materials, considering the modes of transport (e.g., trucks, trains, ships) and the distances traveled.

Module A3 (Production or Manufacturing): This stage encompasses the production or manufacturing processes used to create the final product from raw materials. It includes all the energy, water, and other resources consumed, as well as the emissions and waste generated during production.

Together, modules A1 to A3 provide a comprehensive view of the environmental impacts associated with the initial stages of a product's lifecycle, from raw material extraction to the finished product ready for distribution. This information is crucial for identifying opportunities to reduce environmental impacts and improve sustainability in the production process.

Questions? Contact Max Puchtel, Director of Sustainability and Government Relations, at puchtel@aisc.org