LCA is a systematic process that evaluates how products or activities impact the environment at each stage of their life cycle, from raw material extraction to disposal. As stated in ISO 14040:2006, life cycle assessment is "the compilation and evaluation of the inputs, outputs, and the potential environmental impacts of a product system throughout its life cycle." The methodology considers all stages of a product's life, including resource acquisition, production, transportation, use, and disposal at the end, to assess environmental effects such as energy consumption, releases into the air, water, and land, and resource depletion. LCA provides useful information on how well products and processes perform environmentally in order to lessen negative environmental effects. Making decisions and allocating resources are aided by this information. Additionally, LCA can help identify areas that need improvement and guide the development of environmentally friendly products and processes.
A LCA framework is shown in Fig. 1, along with an explanation of its main elements and how they function together. The framework is divided into three primary sections: Impact Assessment, Inventory Analysis, and Goal and Scope Definition. Every stage contributes to the Interpretation stage, which evaluates the findings. The framework's goal is to provide direction for decision-making across a range of domains, such as marketing, public policy, strategic planning, and product creation and enhancement. This methodical methodology guarantees a thorough assessment of the environmental effects of a product over the course of its life cycle.
3.1 Goal and scope
By describing its goal, an LCA's purpose and objectives can be understood in detail. According to ISO 14040:2006, the purpose statement should outline the study's intended application, target audience, and expected outcomes. As per Azapagic et al. (2004), a well-defined objective ensures that the LCA considers relevant issues and provides valuable insights for decision-making. Setting reasonable expectations, focusing resources on areas that have the most impact, and prioritizing evaluation efforts are all aided by it. The goal of LCA must be clearly defined in order to provide an accurate assessment of the environmental implications. If it is not obvious which components are being analyzed and why, the results of an LCA may not be applicable or may not address the specific concerns of stakeholders. Determining the purpose and scope of an LCA is the first step in carrying out an LCA, according to ISO 14040:2006, to ensure that the assessments that come after are pertinent and goal oriented. Having a clear goal makes it easier to make judgments and carry out comparative investigations. When LCA objectives align with stakeholder interests and expectations, evaluating different products or processes becomes easier and informed decisions may be made more easily. For example, a study by Zamagni et al. (2012) demonstrates how precisely defining the goal of LCA makes it possible to make pertinent comparisons between different packaging materials based on environmental performance parameters. Beyond just addressing environmental issues, LCA also considers sustainability. LCA, which incorporates social, economic, and environmental elements to provide a more comprehensive examination of processes and products, can support sustainable decision-making. This all-encompassing approach is supported by frameworks such as the Social Life Cycle Assessment (SLCA) and the Triple Bottom Line analysis. Sala et al. (2020).
The range of life cycle phases raw material extraction, production, use, and disposal, that are considered in life cycle assessments is defined by system boundaries. The selection of these boundaries is important since it influences the reliability and thoroughness of the assessment Laurent et al. (2020). A thorough understanding of system boundaries ensures that all significant environmental impacts are taken into account, providing a thorough perspective on the sustainability of products and processes. According to Rebitzer et al. (2004) in the "Journal of Cleaner Production", defining system boundaries is essential to conducting a comprehensive effect evaluation. LCA incorporates all relevant life cycle stages to ensure that no significant environmental impact is overlooked. Using this comprehensive method, stakeholders can prioritize treatments and detect hotspots over the course of the entire life cycle. The phenomenon of burden shifting, or the transfer of environmental impacts from one stage of the life cycle to another, can be lessened with the use of clearly defined system boundaries. Rebitzer et al. (2004) highlight the risks associated with omitting specific stages of a research in their study. When the entire life cycle isn't taken into consideration, underestimating the environmental impact of processes and goods can lead to unwise decisions. System boundaries are crucial for meaningfully comparing various products or processes. Consistent system limits are necessary for relevant and trustworthy comparison evaluations, claim Zamagni et al. (2013). Maintaining consistency in the study's scope enables stakeholders to evaluate options' environmental performance and reach educated conclusions. Transparent system boundaries improve the validity of life cycle evaluations by providing interested stakeholders with a better grasp of the theory and methodology employed in the study.
According to Heilungs et al. (2002) in their book "The Computational Structure of Life Cycle Assessment," clearly defined limits increase the transparency of LCA results, facilitating peer review and validation. This transparency builds stakeholder confidence and makes decision-making processes more resilient. For the purpose of evaluating a few chosen goods, the system boundaries for this study were drawn from Cradle to Gate.
The functional unit in LCA refers to the quantifiable measure of a system's or product's performance. It serves as the standard for assessing environmental impacts and makes it easier to compare different solutions in an intelligent manner. According to Arzoumanidis et al. (2020), selecting a good functional unit is crucial since it determines the scope and parameters of the research, which has an impact on the accuracy and dependability of LCA outcomes. One of the primary benefits of the functional unit is its ability to facilitate the comparison of different processes or products. According to Guinée et al. (2002) in the Handbook on Life Cycle Assessment: Operational Guide to the ISO Standards, the functional unit provides a standard framework for comparing choices, allowing stakeholders to analyze environmental performance objectively. Making educated decisions is made easier and more sustainable options can be found with the help of this comparison method. The functional unit is crucial in establishing the characteristics and extent of the LCA research. According to Hauschild et al. (2015), the functional unit chosen determines whether environmental impacts and life cycle stages are included in the analysis. By identifying the intended use of the system or product, stakeholders can tailor the LCA to specific environmental concerns and goals. Transparent documentation from the functional unit enhances the uniformity and transparency of LCA studies. As stated in ISO 14040 (2006), "Environmental management – Life cycle assessment – Principles and framework," a clear definition of the functional unit aids stakeholders in understanding the basis of the study and assessing its reliability. Peer review and validation are facilitated by open communication within the functional unit, which increases confidence in the precision of LCA results.
3.2 Life cycle inventory analysis (LCI)
Creating an inventory of all the inputs (materials, energy, etc.) and outputs (waste, emissions, etc.) related to each stage of a product's life cycle, from the extraction of raw materials to its disposal at the end of its useful life, is the task of a life cycle inventory (LCI) study. As stated in Bjørn et al. (2018), this quantitative method offers a foundation for assessing environmental consequences and identifying opportunities for change throughout the life cycle.
LCI study provides a comprehensive inventory of the resources consumed and emissions associated with a process or product as a baseline review. In the study, Weidema et al (2019) discovered that the use of LCI data aids stakeholders in understanding the environmental implications of different life cycle stages and in prioritizing areas for intervention. Decision-making and policy related to sustainability are aided by the entire picture of resource flows and environmental repercussions provided by LCI analysis. LCI analysis facilitates the identification of hotspots, or life cycle stages with significant environmental implications. LCI data, according to Cu Margni, M. and Curran, M.A (2012), assist stakeholders in identifying environmentally hazardous or inefficient places so that their efforts can be focused on mitigating their consequences. By quantifying inputs and outputs at every level, life cycle impact (LCI) analysis provides valuable insights into the reasons behind environmental deterioration and optimization potential. When LCI data is openly reported, environmental assessments become more transparent and accountable. According to ISO 14044 (2006), which states this in the standard "Environmental management, Life cycle assessment – Requirements and guidelines," accurate and consistent reporting of LCI data helps stakeholders understand the basis for environmental assessments and evaluate their reliability.
3.3 Life cycle impact assessment (LCIA)
An essential tool in the pursuit of sustainable development is the Life Cycle Impact Assessment (LCIA), which offers a comprehensive examination of the effects products or processes have on the environment, society, and economy throughout the duration of their entire life cycles. Sustainability is becoming more and more important in a society where it is becoming a global imperative. LCIA ensures that the environmental and social impact of processes and products is fully understood by considering every stage of the life cycle of the product. This approach, endorsed by reputable publications such as the ISO 14040 standard (ISO, 2006), prevents the overlooking of significant importance of LCIA. Figure 2, referred from the study conducted by Verones et al. (2020) illustrates the connections between areas of protection (such human health, the quality of terrestrial, freshwater, and marine ecosystems, and natural resources) and impact categories (including climate change, ozone depletion, and water stress). Because environmental impacts are interrelated and need a comprehensive approach in environmental assessments, each impact category has an impact on one or more areas of protection.
The effectiveness of LCIA depends on careful model selection that strikes a balance between relevance, data accessibility, and complexity. To guarantee reliable evaluations, Zamagni et al. (2013) emphasize how crucial it is to match LCIA models with the information and tools at hand. Practical and data-driven, models should capture pertinent environmental and social indicators. Certain environmental impacts at mid-point in cause-and-effect chains are quantified by midpoint indicators, such GWP. For example, the GWP quantifies the length of time that greenhouse gas emissions could potentially contribute to global warming. The use of midway indicators, such as GWP, to shed light on particular environmental impacts and facilitate the development of tailored mitigation plans is emphasized by Laratte et al. (2014).
In impact assessment, the choice of suitable models is crucial since it affects the precision and dependability of the outcomes. Model selection should be based on how well they capture the intricate relationships that exist between environmental factors and human activity. Finkbeiner et al. (2010) have emphasized that model selection should take into account factors including uncertainty, data availability, and scales in both space and time. Every effect category has an endpoint impact or a midpoint impact. The term "midpoint impact" describes the consequences that arise within a product's life cycle. These are quantifiable effects that can be traced back to the initial emissions, but they are not directly connected to the chain's final affects Hauschild et al. (2015).
The goal of endpoint impact assessment is to appraise the ultimate results, or endpoints, of environmental consequences, such as alterations in human health, biodiversity, or ecosystem services. A thorough grasp of the effects of human activity is provided by this holistic approach, which also makes well-informed decision-making easier. Endpoint indicators provide information on a systems' or products' overall environmental performance, as de Haes et al. (2002) pointed out. It is frequently necessary to integrate various models for endpoint effect assessment in order to fully capture the complexity of environmental systems. For instance, the evaluation of effects on biodiversity and ecosystem health is made possible by the combination of ecosystem service models and LCA. The necessity of interdisciplinary cooperation and model integration is emphasized by research by Hertwich et al. (2015) in order to increase the reliability of endpoint impact evaluations.
Table 2 provides examples of Life Cycle Inventory (LCI) data and describes the various environmental consequences at both the midpoint and endpoint levels. Carbon dioxide and chlorofluorocarbons are two examples of LCI data that are used to evaluate global warming and ozone depletion at the midway level. Local and regional assessments of acidification and eutrophication are conducted using sulfur oxides and phosphates, respectively, as case studies. When evaluated locally, ozone production and terrestrial toxicity are related to hazardous substances that impact rodents and non-methane hydrocarbons. Endpoint categories that incorporate total emissions and resource utilization, ranging from global to local, include human health and resource depletion. Based on waste volumes and land alterations, land use impacts can be evaluated globally and locally, at both the midpoint and endpoint levels.
Table 2
Life cycle impact categories (The U.S. Environmental Protection Agency, 2006).
Impact Category | Mid-/Endpoint | Scale | Examples of LCI Data |
Global Warming | Midpoint | Global | Carbon Dioxide (CO2), Nitrous Oxide (N2O) Methane (CH4), Chlorofluorocarbons (CFCs) Hydrochlorofluorocarbons (HCFCs), Methyl Bromide (CH3Br) |
Ozone Depletion | Midpoint | Global | Chlorofluorocarbons (CFCs), Hydrochlorofluorocarbons (HCFCs), Halons Methyl Bromide (CH3Br) |
Acidification | Midpoint | Regional , Local | Sulfur Oxides (Sox), Nitrogen Oxides (NOx) Hydrochloric Acid(HCl), Hydrofluoric Acid (HF) Ammonia (NH4) |
Eutrophication | Midpoint | Local | Phosphate (PO4), Nitrogen Oxide (NO), Nitrogen Dioxide,(NO2), Nitrates, Ammonia (NH4) |
Ozone formation | Midpoint | Local | Non-methane hydrocarbon (NMHC) |
Terrestrial Toxicity | Midpoint | Local | Toxic chemicals with a reported lethal concentration to rodents |
Aquatic Toxicity | Midpoint | Local | Toxic chemicals with a reported lethal concentration to fish |
Human Health | Endpoint | Global, Regional , Local | Total releases to air, water, and soil. |
Resource Depletion | Endpoint | Global, Regional , Local | Quantity of minerals used, Quantity of fossil fuels used, Water footprint |
Land Use | Midpoint/ Endpoint | Global, Regional , Local | Quantity disposed of in a landfill or other land modifications |
Table 3 lists different environmental models along with the impact categories they address, including acidification, global warming, ozone depletion, and toxicity. A multitude of topics are covered by models such as CML2002, Eco-indicator 99, EDIP 2003, EPS 200, Impact 2002+, and ReCiPe, which include acidification, global warming, ozone depletion, and human toxicity.
Table 3
Impact category and associated models Margni et al. (2012).
Model | | | | | | | | | | | |
CED | | | | | | | | | ✔ | | |
CML2002 | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | |
Eco-indicator 99 | ✔ | ✔ | ✔ | ✔ | | ✔ | | ✔ | ✔ | | ✔ |
EDIP 2003/EDIP978 | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | |
EPS 200 | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | |
Impact 2002+ | ✔ | ✔ | ✔ | | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | |
IPCC | ✔ | | | | | | | | | | |
LIME | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | |
LUCAS | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | |
MEEuP | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | |
ReCiPe | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ |
Swiss Ecoscarcity | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | |
TRACI | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | ✔ | |
USEtox | | | | | | | ✔ | ✔ | ✔ | | |
The selection of impact categories, category indicators, and characterization models is the first stage in LCA as per ISO standards (Fig. 3; ISO 14040, 2006). Classification entails dividing the inventory data into impact groups according to the endpoints and environmental mechanisms they represent. The inventory data is categorized in this step based on pertinent environmental stresses, including resource depletion, acidification, eutrophication, greenhouse gas emissions, and ozone depletion. To maintain comparability and consistency across various LCIA studies, ISO 14044 stresses the significance of employing a consistent and rigorously scientific classification scheme. Quantifying the possible environmental effects of the inventory data within each impact category is a necessary step in the characterization process. In order to enable comparison and aggregation across several effect categories, this phase converts the inventory data into commonly used units of measurement, such as kilograms of CO2 equivalents or kilograms of sulfur dioxide equivalents. When characterizing the environmental impacts associated with each inventory item, ISO 14044 advises using scientific methodologies such as cause-effect models, fate and transport models, and others. Table 4 illustrates the damage pathways from the study conducted by Huijbregts et al., (2017) for a range of environmental issues across multiple protection domains. Only the climate change category is mentioned here, rest of the table is put in appexdix.. Increased sickness and natural catastrophes are two ways that climate change affects human health. It also has an impact on freshwater and terrestrial ecosystems by causing the extinction of species (IPCC 2013; Joos et al. 2013; De Schryver et al. 2009). Skin cancer and cataracts are caused by stratospheric ozone depletion (WMO 2011; Hayashi et al. 2006), whilst ionizing radiation is linked to an increase in cancer and genetic disorders (Frischknecht et al. 2000; De Schryver et al. 2011). By generating respiratory and cardiovascular disorders, particulate matter and photochemical ozone production are harmful to human health (Van Zelm et al. 2016). According to Roy et al. (2014) and Helmes et al. (2012), freshwater eutrophication and terrestrial acidification cause the extinction of aquatic and plant species. Chemical exposure causes toxicity, which affects both human health and different ecosystems (Van Zelm et al. 2009). Ecosystems that consume more water become malnourished and produce less (Pfister et al. 2009). Due to habitat modification brought on by land use, species are lost (De Baan et al. 2013; Curran et al. 2014). Because of the extraction of minerals and fossil fuels, resource scarcity drives up costs (Vieira et al. 2016).
Table 4
Damage pathways in ReCipe 2016 (Huijbregts et al., 2017).
Environmental problem | Area of protection | Damage pathways | References |
Climate change | Human health | Years of life lost and disability brought on by an increase in malaria, diarrhea, hunger, and natural disasters as a result of a rise in the average world temperature | IPCC 2013; Joos et al. 2013; De Schryver et al. 2009 |
Ecosystems (terrestrial) | Loss of species as a result of shifting biome distributions brought on by rising global temperatures | IPCC 2013; Joos et al. 2013 |
Ecosystems (freshwater) | Loss of fish species as a result of reduced river discharge | Hanafiah et al. 2011 |
Quantitative measurements known as category indicators are employed to depict the environmental impacts associated with each impact category. These indicators offer a way to standardize the expression of the impacts' extent and relevance. The adoption of scientifically and policy-relevant indicators that encapsulate the principal environmental issues linked to every impact category is encouraged by ISO 14044. Global warming potential (GWP), acidification potential (AP), eutrophication potential (EP), and human toxicity potential (HTP) are examples of common category indicators. In order to make comparisons across various effect categories easier, normalization entails scaling the category indicators to a standard reference scale. This phase enables a more relevant comparison of environmental impacts by taking into account changes in the category indicators' magnitude and units of measurement. To promote uniformity in the interpretation of the results and standardize the category indicators, ISO 14044 advises using normalization factors such global or regional averages. By weighting, the various impact categories are given varying degrees of relevance or significance according to stakeholder preferences, policy aims, or other factors. By taking this action, decision-makers can sort environmental issues into priority lists and concentrate their efforts on resolving the most pressing issues. Recognizing the subjective character of weighting, ISO 14044 suggests open, participatory methods to guarantee the validity and trustworthiness of the weighting procedure. The LCIA procedure is shown in Fig. 3 as referred from ISO 14040, 2006, with emphasis on both required and optional components. The selection of impact categories, category indicators, and characterization models are required components. The results of the Life Cycle Inventory (LCI) are then assigned through classification. This results in the characterisation, or category indicator results, being calculated. After that, the LCIA profile is created using the category indicator results. Grouping, weighting, and normalization, which determines the significance of outcomes in relation to reference data—are optional components that might improve the assessment. This methodical procedure guarantees a comprehensive assessment of a process's or product's environmental effects.
3.4 Interpretation
Finding important environmental problems and hotspots across the life cycle is the first step in evaluating LCA results. In order to help identify pertinent elements, publications like Guinée et al. (2011) provide a thorough overview of the environmental challenges addressed by LCAs. The standard method supporting the determination of relevant factors is also described on ISO 14044 (2006) guideline presented in Fig. 3. The significance of making sure that all pertinent inputs and outputs are taken into account at every point of the life cycle is emphasized by ISO standards. Research works such as Jørgensen et al. (2010) offer approaches for evaluating completeness and assisting practitioners with data gathering and validation. Sensitivity analysis is a useful tool for assessing how important parameters and assumptions affect LCA outcomes. Studies like Hauschild et al. (2018) provide information about influence of sensitivity analysis in life cycle assessment results. It is essential to guarantee internal consistency in the LCA study. To improve the trustworthiness of outcomes, ISO standards and literature, such as Martin et al. (2018) offer recommendations on confirming consistency throughout the assessment process's many stages. As referred from ISO 14044, 2006 Fig. 4 illustrates the Life Cycle Assessment (LCA) framework, highlighting the three primary elements that comprise it: impact assessment, inventory analysis, and aim and scope determination. These elements contribute to the interpretation stage, which is where important problems are found and assessed using a variety of techniques. Finally, the framework forms conclusions, constraints, and suggestions. The LCA's results have direct bearing on marketing, public policy, strategic planning, and product development.
3.5 Understanding customer perspective (Sentiment Analysis)
Moreover, as the internship is addressing two pillars of sustainable development (environmental and social) for social development, sentiment analysis is essential for understanding customer perspective. Through the examination of reviews, social media comments, and other digital feedback, the case company can obtain profound insights into the opinions and emotional responses of its customers through sentiment analysis.
Sentiment analysis is a branch of natural language processing (NLP) that examines textual data to ascertain the writer's sentiment. This might be classified as neutral, negative, or positive feelings. More sophisticated methods can also identify the degree to which particular sensations, like joy, rage, or contempt, are present. Sentiment analysis offers important insights into consumer perceptions and may be used to a wide range of data sources, such as social media posts, online reviews, and survey results Thao et al. (2023).
3.5.1 Application of sentiment analysis
Rich data on consumer experiences can be found in reviews on food delivery apps and e-commerce sites. Examining these reviews enables one to pinpoint frequent compliments and grievances regarding aspects like flavor, texture, packaging, and nutritional worth. Salehan et al. (2016) illustrate how sentiment mining can be used to forecast the effectiveness of online customer reviews, underscoring its importance for bettering products.
Social media sites such as Facebook, Instagram, and Twitter are useful for sentiment research in real time. Finding trends and public opinion can be achieved by monitoring hashtags and remarks pertaining to plant based RTE foods. Chen and Zhang (2022) demonstrated the possibility of social media sentiment analysis for food goods by investigating popular perceptions of alternative meat in China using social media data and transfer learning.
Survey responses that are structured can be examined to identify areas for development and to learn more about particular facets of customer satisfaction. Using sentiment analysis, Thao et al. (2023) investigated consumer perceptions of vegetarian cuisine, offering insights into consumer expectations and preferences.
3.5.2 Sentiment analysis methodology
The approach of sentiment analysis consists of multiple essential procedures intended to identify, evaluate, and extrapolate subjective information from textual data. Thao et al. (2023) state that the procedure usually starts with data collection, which involves gathering textual data from a variety of sources, including social media, online reviews, and survey replies. After that, the data is preprocessed using techniques like tokenization, stemming, lemmatization, and stop word removal in order to eliminate noise and unnecessary information. After the data has been cleaned, it is analyzed using machine learning techniques (where models are trained on labeled datasets to classify text into sentiment categories) or lexicon-based approaches (which rely on predefined dictionaries of words loaded with sentiment). In order to increase accuracy, advanced techniques may also use hybrid approaches that combine machine learning with lexicon-based techniques.Lastly, the data is visualized and analyzed to offer useful insights into the attitudes and opinions of the consumer. In order to effectively capture the complexities of consumer sentiments on plant-based and vegetarian diets, Thao et al. (2023) states that robust analytical methodologies and thorough context evaluation are necessary for effective sentiment analysis.
3.6 Analysis of data
The databases and methodologies chosen for the study's LCA are validated in Table 5. It enumerates three primary techniques, each linked to certain databases and references: ReCiPe 2016, EcoInvent v3.6, and GaBi. ReCiPe 2016, which makes use of the Agri-footprint database, is the best appropriate for this study because of its thorough effect evaluation that includes midway and endpoint indicators. While GaBi offers a wide range of datasets for environmental impact assessments, EcoInvent v3.6 delivers comprehensive LCA data for a variety of processes. The study comes to the conclusion that the best approach for carrying out the LCA is to use the ReCiPe 2016 Midpoint (H) technique in conjunction with the Agri-footprint database. These techniques were put into practice using SimaPro LCA software, which ensures a comprehensive and verified life cycle assessment
Table 5
Method and database selection
Method | Description | Database | Reference |
ReCiPe 2016 | Comprehensive impact assessment method offering midpoint (e.g., GWP) and endpoint indicators. | Agrifootprint | Huijbregts et al (2016) |
Ecoinvent v3.6 | Widely used LCA database containing extensive data for various processes, including GWP factors. | Ecoinvent | Wernet et al (2016) |
GaBi | A comprehensive LCA software and database that provides extensive datasets for environmental impact assessments. | GaBi | Curran et al. (2013) |