Life Cycle Assessment
This article focuses on Life Cycle Assessment (LCA), which is a method used to evaluate the environmental impact of a product, process or activity over its entire life cycle. The goal of LCA is to identify and quantify the potential environmental impacts of a product or service, from the extraction of raw materials, through the manufacturing and use phases, to final disposal. The LCA process provides a comprehensive and scientifically robust analysis of the environmental impact of a product, taking into account its entire life cycle.
In the context of project, program, and portfolio management, LCA can be used to evaluate the sustainability of projects and to identify opportunities for improvement. For example, a project manager may use LCA to assess the environmental impact of different project options and to prioritize projects that have the lowest environmental impact. Additionally, a portfolio manager may use LCA to assess the environmental impact of different investment options and to prioritize investments in companies that are actively engaging in sustainability.
LCA can also provide valuable information for stakeholders, including investors, customers, and policymakers, who are interested in understanding the environmental impact of the products and services they use and invest in, and help them make more informed decisions.
In conclusion, LCA can be a valuable tool for project, program, and portfolio management, as it provides a comprehensive and scientifically robust analysis of the environmental impact of projects and enables managers to identify opportunities for improvement and make informed decisions. As sustainability becomes increasingly important to investors and customers, LCA will play an increasingly important role in project, program, and portfolio management, helping companies and investors to achieve their sustainability goals and drive positive change in the world.
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History of LCA
Origins
The idea of LCA was conceived in the 1960s, when environmental degradation and limitations of raw materials and energy resources sparked interest in finding ways to cumulatively account for energy use and to project future resource supplies and use. This practice sees its roots in studies carried out uncoordinately in the US and Northern Europe regarding packagings, with a focus on energy use and a few emissions. At first, studies were primarly done for companies for internal use, usually without informing styakeholders, since interest in sustainability was very limited to few at that time. One example is an internal study initiated in 1969 for The Coca-Cola Company that laid the foundation for the current methods of life cycle inventory analysis in the United States. This study quantified the raw materials, fuels, and environmental loadings from the manufacturing processes for various beverage containers, in order to compare their impact on the environment and their depletion of natural resources. The aim was to identify the container with the lowest release to the environment and the least impact on natural resource supply. After a stall in the 1970s, it was just during the 1980s and 1990s, when international collaboration and coordination in the scientific community started to take place and universities engaged in working on method development, that the application of LCA spreaded across industry and governments, resulting in an increasing range of products and systems included into LCA studies. The term Life Cycle Assessment was itself coined in 1990 and, since then, this practice has seen a constant increase in both range of methodologies and applications.[1] [2]
Development and Standardisation
Starting from the early 1990s, the global Society for Environmental Toxicology and Chemistry (SETAC) organised multiple workshops with the aim of developing a common "Technical Framework for LCA". The series culminated in the development of a Code of Practice for LCA, the first official guidelines for LCA in 1993.
Towards the end of the decade, leading researchers of the SETAC working group on life cycle impact assessment initiated a collaboration with the United Nations Environmental Program (UNEP) to expand the global dissemination of good LCA practices beyond the primary activity centers of Europe, North America, and Japan. The partnership was aimed at ensuring the continued development of such practices on a global scale, and it culminated in 2002 in the launch of the UNEP/SETAC Life Cycle Initiative. This initiative brought a wide scientific consensus on LCA.
Consequently to the publication of the first Code of Practice, a formal standardization process was initiated by the International Organization of Standardization (ISO) to develop a global standard for LCA. Over a period of seven years, the development of standards led to the adoption and release of four different standards. These standards pertained to the LCA principles and framework (ISO 14040), goal and scope definition (ISO 14041), life cycle impact assessment (ISO 14042), and life cycle interpretation (ISO 14043). The ISO standards were found to have limitations in their applied methodology and consultation process, leading to potential ambiguities. As a result, the UNEP/SETAC Life Cycle Initiative was launched to evaluate alternative practices and provide scientifically grounded recommendations. This need for improved consistency and reproducibility of LCA results also led the European Commission to initiate the development of the International Life Cycle Data System (ILCD) in the mid-2000s. The ILCD system includes a database of life cycle inventory data and methodological guidelines aimed at ensuring greater consistency and comparability of LCA results across different studies and practitioners. Cite error: Invalid <ref> tag;
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Steps to perform an LCA
In the following paragraphs are listed the steps that have to be carried out in order to perform a well structured LCA study. These are, as well, the most important parts that must be included in an LCA report that can be considered detailed and professional.
Goal and Scope definition
Inventory analysis
Impact assessment
Interpretation
LCA tools and databases
Strenghts and limitations
Rather than saying that LCA calculates actual environmental impacts, it is more accurate to say that it calculates impact potentials.[3]
References
- ↑ Life Cycle Assessment:Theory and Practice, chapter 3 (Michael Z. Hauschild, Ralph K. Rosenbaum, Stig Irving Olsen) https://link.springer.com/book/10.1007/978-3-319-56475-3
- ↑ M.L. Brusseau, Chapter 32 - Sustainable Development and Other Solutions to Pollution and Global Change,Editor(s): Mark L. Brusseau, Ian L. Pepper, Charles P. Gerba, Environmental and Pollution Science (Third Edition),Academic Press,2019,Pages 585-603,ISBN 9780128147191,https://doi.org/10.1016/B978-0-12-814719-1.00032-X. (https://www.sciencedirect.com/science/article/pii/B978012814719100032X)
- ↑ Life Cycle Assessment:Theory and Practice, chapter 2.3 (Michael Z. Hauschild, Ralph K. Rosenbaum, Stig Irving Olsen) https://link.springer.com/book/10.1007/978-3-319-56475-3
- Project Management: A guide to the Project Management Body of Knowledge (PMBOK guide), 7th Edition (2021) https://findit.dtu.dk/en/catalog/2702860479
- Project Management: ISO 21502 (2021 Edition) https://findit.dtu.dk/en/catalog/2690497944
- Program Management: ISO 21503 (2017 Edition) https://findit.dtu.dk/en/catalog/2441783644
- Portfolio Management: ISO 21504 (2015 Edition) https://findit.dtu.dk/en/catalog/2441783648
