A Review of the Key Findings from the Special Issue on “Life Cycle Sustainability Analysis of Resource Recovery from Waste Management Systems in the Context of Circular Models of the Economy and the Bioeconomy”
1. Introduction
- Virgin materials being extracted beyond their replenishment capacities;
- Post-use commodities often being landfilled or treated in incineration plants, which has the consequence of valuable and scarce natural resources being extracted anew and the original resources being lost for the manufacturing of new products;
- Unsafe, unsustainable waste management practices leading to hazardous substances being emitted into the air, water and soil, and generating alarming environmental pollution conditions;
- Product manufacturing and distribution being responsible for extensive energy use and emissions of greenhouse gases and other pollutants, thus leading to climate change and heavily damaging human health, resources and ecosystem quality.
2. Scope of This Special Issue
3. Article Collection Overview
3.1. Technical Assessments (Cluster 1 Articles)
3.2. Single Sustainability Dimension Assessments (Cluster 2 Articles)
3.3. Combined Sustainability Dimension Assessments (Cluster 3 Articles)
3.4. Other Empirical Studies (Cluster 4 Articles)
4. Final Remarks from the LCA-Article Review
5. Conclusions
6. List of the Contributions to This SI
- Bashiri, B., Cropotova, J., Kvangarsnes, K., Gavrilova, O., Vilu, R., 2024. Environmental and Economic Life Cycle Assessment of Enzymatic Hydrolysis-Based Fish Protein and Oil Extraction. Resources 13(5), 61.
- Bravo, L.M.R., Cosio Borda, R.F., Quispe, L.A.M., Rodríguez, J.A.P., Ober, J., Khan, N.A., 2024. The Role of Internet and Social Interactions in Advancing Waste Sorting Behaviors in Rural Communities. Resources 13(4), 57.
- Brigida, V., Golik, V.I., Voitovich, E.V., Kukartsev, V.V., Gozbenko, V.E., Konyukhov, V.Y., Oparina, T.A., 2024. Technogenic Reservoirs Resources of Mine Methane When Implementing the Circular Waste Management Concept. Resources 13(2), 33.
- Fontaine, L., Legros, R., Frayret, J.-M., 2024. Sustainability and Environmental Performance in Selective Collection of Residual Materials: Impact of Modulating Citizen Participation Through Policy and Incentive Implementation. Resources 13(11), 151.
- Ketkale, H., Simske, S., 2023. A LifeCycle Analysis and Economic Cost Analysis of Corrugated Cardboard Box Reuse and Recycling in the United States. Resources 12(2), 22.
- Levickaya, K., Alfimova, N., Nikulin, I., Kozhukhova, N., Buryanov, A., 2024. The Use of Phosphogypsum as a Source of Raw Materials for Gypsum-Based Materials. Resources 13(5), 69.
- Provenzano, M., Pacchera, F., Silvestri, C., Ruggieri, A., 2024. From Vineyard to Value: A Circular Economy Approach to Viticulture Waste. Resources 13(12), 172.
- Rebolledo-Leiva, R., Estévez, S., Hernández, D., Feijoo, G., Moreira, M.T., González-García, S., 2024. Apple Pomace Integrated Biorefinery for Biofuels Production: A Techno-Economic and Environmental Sustainability Analysis. Resources 13(11), 156.
- Sobaih, A.E.E., Elnasr, A.E.A., 2024. From Your Plate to Our Bin: Tackling Food Waste in Saudi Family Restaurants. Resources 13(10), 134.
- Vinci, G., Gobbi, L., Porcaro, D., Pinzi, S., Carmona-Cabello, M., Ruggeri, M., 2024. Environmental Evaluation of Chemical Plastic Waste Recycling: A Life Cycle Assessment Approach. Resources 13(12), 176.
- Wojnarowska, M., Muradin, M., Paiano, A., Ingrao, C., 2025. Recycled Glass Bottles for Craft-Beer Packaging: How to Make Them Sustainable? An Environmental Impact Assessment from the Combined Accounting of Cullet Content and Transport Distance. Resources 14(2), 23.
Acknowledgments
Conflicts of Interest
References
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Article Number | Authors’ Team | Research Focus | Assessment Methodology Applied |
---|---|---|---|
1 | Bashiri et al. | Extraction of protein ingredients from fish processing residues | Combined ELCA-LCC |
2 | Bravo et al. | Investigating how social dynamics and digital connectivity are influencing residents’ willingness to adopt waste sorting in rural areas. | A combined social theory and econometric modelling, supported by results from participants’ surveys. |
3 | Brigida et al. | Technogenic reservoir resources of mine methane to support circular waste management implementations | Reconstruction of the response space for the dynamics of methane release from frontal and lateral projections. |
4 | Fontaine et al. | Exploring the effects of municipal strategies on household waste management behaviours and sustainability performances | Agent-based modelling |
5 | Ketkale and Simske | Corrugated Carbon Box (CCB) life cycle with different disposal scenarios (i.e., reusing, recycling, and landfilling). | ELCA, combined with economic tools like willingness-to-pay versus marginal cost curves and benefit–cost analysis. |
6 | Levickaya et al. | Recycling of phosphogypsum, derived from the synthesis of orthophosphoric acid from phosphorite rock. | Product characterisation and testing |
7 | Provenzano et al. | Vinification residue valorisation | Systematic literature review |
8 | Rebolledo-Leiva et al. | Apple pomace/vinasse integrated biorefinery for production of biofuels and bio-nutrients. | Techno-economic analysis (TEA) and ELCA |
9 | Sobaih and Elnasr | Tackling problems related to food waste management in Saudi Arabia, with special regard to family restaurants | Surveys for data collection and analysis |
10 | Vinci et al. | Plastic waste recycling through pyrolysis for oil production. | ELCA |
11 | Wojnarowska et al. | Exploring glass bottle recycling, with the combined accounting of cullet content and transport distance | ELCA |
Cluster | Belonging Articles | |
---|---|---|
Number | Description | |
1 | Assessments of technical aspects, which are related to more holistic LCSAs, are included here. | Brigida et al.; Levickaya et al. |
2 | This cluster includes assessments that have considered one single sustainability dimension. | Vinci et al.; Wojnarowska et al. |
3 | Combined assessments of at least two sustainability dimensions and other related ones. | Rebolledo-Leiva et al.; Ketkale and Simske; Bashiri et al. |
4 | Other empirical studies (e.g., surveys, social theory, econometric modelling, data analysis and agent-based modelling) for evaluation of the sustainability-relevant issues of waste recovery systems | Sobaih and Elnasr; Bravo et al.; Fontaine et al. |
Reference | Object of the Study | Study Area | Study Scale | Type of LCA Conducted | FU | SB | Type of Data Used | Secondary Databases | Software Used | Allocation | Substitutional Approach for Environmental Credit Accounting | IAM | MIs | Other Energy, Environmental, Economic Indicators Used | Endpoint | Main Findings from the Study |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Vinci et al. | Environmental assessment of chemical plastic waste recycling (CPWR) | Italy—Spain | Laboratory | Full LCA | 1 L pyrolysis oil | Cradle-to-gate (from plastic waste acquisition to oil production) | Primary data obtained through site visits and surveys, combined with secondary data | Ecoinvent v3.11 | SimaPro v9.6 | None | Yes, the authors used this approach to model the environmental gains coming from using pyrolytic oil as a diesel substitute | ReCiPe (I) 2016 Midpoint [22] | All those considered by the IAM | No | No | CPWR enables reducing global warming by −3849 kg CO2 eq per ton of plastic processed, ionising radiation by −22.4 kBq Co-60 eq/1000 kg, terrestrial toxicity by −58.9 kg 1.4-DCB/1000 kg, land use by −174 m2 a crop eq/1000 kg, and fossil resource consumption by −1807.5 kg oil eq/1000 kg |
Wojnarowska et al. | Recycled glass bottle production complemented with the combined accounting of cullet content and transport distance | Poland | Industrial supply chain | Streamlined LCA | 1 kg glass bottles | Cradle-to-gate (from glass cullet acquisition to bottle production) | Only secondary data from Polish reports and statistics and other databases were used in this study. | Ecoinvent v3.7 | SimaPro v9.6 | None | No | EF 3.0 [23] | All those considered by the IAM | CED | Yes. The assessment was extended to the normalisation step | Using the maximum possible cullet content (90%) results in the lowest environmental impact, even when transport distances increase up to 250 km. |
Reference | Object of the Study | Study Area | Study Scale | Type of LCA Conducted | FU | SB | Type of Data Used | Secondary Database | Software Used | Allocation | Substitutional Approach for Environmental Credit Accounting | IAM | MIs | Other energy, Environmental, Economic Indicators Used | Endpoint | Main Findings from the Study |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Bashiri et al. | Economic/environmental sustainability assessment of enzymatic hydrolysis for extraction of protein compounds and oils from Atlantic fish processing residues | Norway | Laboratory | Combined LCC-ELCA | 1 g FPH | Cradle-to-gate (fish residue acquisition and preparation to the combined production of FPH and fish oils through enzymatic hydrolysis) | Primary data from laboratory experiments, combined with secondary data | Ecoinvent v3.8 | OpenLCA | Economic allocation between FPH and fish oil | No | Recipe (H) Midpoint | All those considered by the IAM | Breakdown of economic costs | No | ELCA results
Labour and electricity are mostly responsible for cost of producing 1 g of FPH. |
Rebolledo-Leiva et al. | Techno-economic and environmental assessment of apple pomace biorefinery. A scenario analysis was performed on the vinasse comparing their valorisation into biogas (for recirculation within the biorefinery for energy purposes) with composting and lagooning | Chile | Biorefinery plant design | Technical analysis combined with a discounted cash flow analysis and an ELCA | A multifunctional approach was used in this study for bioethanol:
| Cradle-to-gate (apple pomace generation from cultivated apple processing, bioethanol production, and vinasse treatment) | Process design data, combined with background data from previously published literature and databases | Ecoinvent v3.8 | Superpro designer v11 SimaPro v9.4 | Economic allocation performed in the upstream part of the system, between apple juice and pomace. In the core part, all burdens were allocated to bioethanol | No | ReCiPe 2016 (H) [22] | All those considered by the IAM | Optimum Plant Capacity (OPC), Minimum Feedstock Requirements (MFR), Cumulative Energy Demand, Discounted Payback Period (DPP) | No | Different biorefinery phases contribute differently to the environmental impact of the whole system:
The carbon footprint was 1.13 kg CO2 eq∙kg−1 when biogas production was integrated to reduce the energy demand of the biorefinery. If the vinasse management strategy is lagoon and compost, the footprint increases to about four. Overall, the eco-efficiency analysis showed that the scenario of co-production of bioethanol and biogas was the best alternative, although the economic dimension was a significant limitation due to high investment costs. |
Ketkale and Simske | ELCA and economic cost analysis applied to CCB life cycle. The assessment was extended to testing different end-of-life (EoL) scenarios for post-use CCBs | United States of America | Industrial supply chain | Carbon-focussed and economic analysis | 1 kg of a typical CCB | Cradle-to-grave (CCB manufacturing, use, and end-of-life) | Only background data were used from previously published reports and statistics combined with databases. | Ecoinvent v3.7 Environmental footprint v2.0 ELCD v3.2 Exiobase v3.4 and others | OpenLCA v2.1.3 | No | No | AR5—IPCC (2013) [24] | GWP100 |
| No | Carbon footprint assessment The reuse of the CCB would also result in a saving of 1.54 kgCO2-eq for the second use since the effort to produce a new CCB would be saved. Economic analysis The general conclusion from the cost–benefit analysis is that, assuming 100,000 uses, the 50,000 CCBs that would be reused would generate USD 83,103 in net profit, with a 1.44 cost–benefit ratio. Businesses can break even at no profit by reducing new crate costs to USD 1.17, selling return crates at USD 3.66, and increasing motivational costs to USD 3.46. Exceeding these limits will have a negative impact on the profitability of the reuse cycle. The marginal cost curve shows the difference between the marginal value and the cost of motivating the population. |
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Ingrao, C.; Bezama, A.; Paiano, A.; Hildebrandt, J.; Arcidiacono, C. A Review of the Key Findings from the Special Issue on “Life Cycle Sustainability Analysis of Resource Recovery from Waste Management Systems in the Context of Circular Models of the Economy and the Bioeconomy”. Resources 2025, 14, 44. https://doi.org/10.3390/resources14030044
Ingrao C, Bezama A, Paiano A, Hildebrandt J, Arcidiacono C. A Review of the Key Findings from the Special Issue on “Life Cycle Sustainability Analysis of Resource Recovery from Waste Management Systems in the Context of Circular Models of the Economy and the Bioeconomy”. Resources. 2025; 14(3):44. https://doi.org/10.3390/resources14030044
Chicago/Turabian StyleIngrao, Carlo, Alberto Bezama, Annarita Paiano, Jakob Hildebrandt, and Claudia Arcidiacono. 2025. "A Review of the Key Findings from the Special Issue on “Life Cycle Sustainability Analysis of Resource Recovery from Waste Management Systems in the Context of Circular Models of the Economy and the Bioeconomy”" Resources 14, no. 3: 44. https://doi.org/10.3390/resources14030044
APA StyleIngrao, C., Bezama, A., Paiano, A., Hildebrandt, J., & Arcidiacono, C. (2025). A Review of the Key Findings from the Special Issue on “Life Cycle Sustainability Analysis of Resource Recovery from Waste Management Systems in the Context of Circular Models of the Economy and the Bioeconomy”. Resources, 14(3), 44. https://doi.org/10.3390/resources14030044