By simple deduction, we can quickly understand what “life cycle assessment” (LCA) refers to. In basic terms, this is the determination of the importance, size, or value (“assess”) of the life cycle of practically anything produced from its origins to its end state. This end state may be a state of waste/disposed matter or a state of reuse/recycle/remanufacture/etc.
We’ll cover the specifics of a typical general life cycle assessment of any given product in a future blog post. For now, we’ll just be tackling general information on what LCA’s are and (for the most part) how LCA’s came about and developed throughout the years.
We can start by looking back to the 1960’s and 1970’s when studying the impact of consumer products to the environment started to become a big deal. Due to one product trying to best its competition in any way it can, environmental impact discussion on consumer products grew to long and sometimes fierce debates (Hocking, 1991). Take a look at some examples, as given by Guinée et al (2011), and see if they do fit in this situation:
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As far as environmental impact is concerned, further investigations and explorations revealed that a product mostly affects its environment during its production, transportation, or disposal, and not when it is being used by the consumer (Guinée et al, 2011). This finding eventually became a bigger issue, and a way for it to be addressed has to be done. This is where LCA comes in, which ISO 14040 and ISO 14044 define as the:
“…compilation and evaluation of the inputs and outputs and the potential environmental impacts of a product system throughout its life cycle”
The continual adaptation of the concept in the scientific and engineering community can be seen in the increasing number of LCA literature in Environmental Science Technology, a well-known and reputable journal dealing with, well, environmental science:

Histogram of the number of articles mentioning LCA in ES&T showing the emergence of LCA in particularly the 1990’s, starting from the first issue of ES&T in 1967 (Source: ACS Publication ES&T Web site, obtained from Guinée et al’s 2011 paper as cited below)
Clearly, scientists and engineers realized as time went by the importance of LCA’s in ultimately minimizing, if not eliminating, the hazardous environmental impacts a consumer product may cause all throughout its life cycle.
Jacquemin et al presented in a 2012 paper of theirs a handy diagram showing the general approach of industries to environmental issues during various time periods. This diagram places LCA under pollution and waste approaches that started in the 1990’s. They stated that the LCA approach is a proactive approach which eventually became a progressive one at the turn of the following decade. At this time period (the 2000’s), LCA has been said to be generalized and aided also by the development of integrated tools for environmental design and evaluation of industrial processes. This diagram is shown below:

Industrial response to environmental issues (Jacquemin et al, 2012)
A better timeline-based perspective of LCA’s development was presented by Guinée et al. In their 2011 paper, they divided the state of LCA into past (1970-2000), present (2000-2010), and future (2010-2020) stages. Listed below are the subdivisions and key points of these stages. More can be read in their paper (as listed in the References section below).
The Past of LCA (1970-2000)
1970-1990: Decades of Conception
- Environmental issues like resource and energy efficiency, pollution control, and solid waste became issues of broad public concern, and a solution to these issues has to be conceptualized and eventually implemented as soon as possible.
- The Midwest Research Institute (MRI) conducted an unpublished study quantifying the resource requirements, emission loadings, and waste flows of different Coca Cola beverage containers.
- MRI’s study was termed as a “Resource and Environmental Profile Analysis” (REPA), and this practically served as the precursor of the current LCA.
- Since the LCA was still at its early periods of conceptualization, widely diverging approaches, terminologies, and results materialized.
1990-2000: Decade of Standardization
- Started with the convergence of the Society of Environmental Toxicology and Chemistry’s (SETAC) “Code of Practice” (aimed towards the leading and coordination of LCA practitioners, users, and scientists for the continuous improvement and harmonization of of LCA frameworks, terminologies, and methodologies) and the International Organization for Standardization’s (ISO) formal task of standardization of methods and procedures via the ISO 14040 and ISO 14044.
- LCA became part of policy documents and legislation.
The Present of LCA: Decade of Elaboration (2000-2010)
- Divergence in methods became prevalent due to the need for robustness.
- Diverging approaches have been developed with respect to system boundaries and allocation methods, dynamic LCA, spatially differentiated LCA, risk-based LCA, and environmental input-output based LCA.
- Life cycle costing and social life cycle assessment approaches have been proposed and/or developed that may have consistency problems with environmental LCA in terms of system boundaries, time perspectives, calculation procedures, etc.
- There is a need for structuring the varying field of LCA approaches while taking into account more types of externalities and more mechanisms.
The Future of LCA: Decade of Life Cycle Sustainability Analysis (LCSA) [2010-2020]
- The Coordination Action for Innovation in Life Cycle Analysis for Sustainability (CALCAS) project was commissioned by the European Commission.
- CALCAS’ purpose was to structure the varying field of LCA approaches and to define research lines and programs to further LCA where necessary.
- The LCSA resulted from CALCAS.
- The framework of LCSA links life cycle sustainability questions to knowledge needed for addressing them, identifying available knowledge and related models, knowledge gaps, and defining research programs to fill these gaps.
- Three important differences with the ISO 14040: (1) the merging of inventory analysis and impact assessment into one modeling phase, (2) the broadening of the object of analysis, and (3) the broadening of the scope of indicators.
True enough, scientists and engineers have been working tirelessly to improve LCA’s so as to properly obtain their specific and overall end goals. It really is amazing to know about its beginnings and to witness how it still develops. The best we can get from all this is that if much time, effort, and ideas are being dedicated to the improvement of LCA’s, then experts really find LCA’s to be very beneficial in designing for the environment. If anything else, the history of LCA’s should serve as a motivation for us to learn more about how LCA’s are conducted. After all, if it has been established that most products affect the environment in those parts of their life cycles not directly involving the consumer, then determining and assessing what happens to the product and to the materials/processes/etc. involved in its life cycle should prove to be sensible and worthwhile.
Stay tuned to our blog for more posts on LCA’s.
References! Get your references here!
Guinée, J. B., Zamagni, A., Masoni, P. et al. Life cycle assessment: past, present, and future. Environ. Sci. Technol. 2011, 45, 90–96.
Hocking, M. B. Paper versus polystyrene: a complex choice. Science 1991, 251 (4993), 504–505.
ISO 14040 International Standard. Environmental management – Life cycle assessment – Principles and framework; International Organization for Standardization: Geneva, Switzerland, 2006.
ISO 14044 International Standard. Environmental management – Life cycle assessment – Requirements and guidelines; International Organization for Standardization: Geneva, Switzerland, 2006.
Jacquemin, L., Pontalier, P., & Sablayrolles, C. Life cycle assesment (LCA) applied to the process industry: a review. Int. J. Life Cycle Assess. 2012, 17, 1028-1041.