Sustainability Through Additive Manufacturing Operations: A Comparative Industrial Analysis with a Life Cycle Assessment Case Study of Türkiye
Abstract
1. Introduction
2. Literature Review
3. Methodology
3.1. Adaptive Choice-Based Conjoint (ACBC)
3.2. Hierarchical Bayesian Regression
3.3. Priority Observed from the Presumption of Gaussian Attitude of Alternatives (PrOPPAGA)
4. Application
Survey Design for Multiple-Case Study
5. Validation and Discussion
6. Conclusions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
Appendix A

| LCA Factors | Sub-Factors | Definitions |
|---|---|---|
| Material Efficiency | Very High | Utilization ≥ 90%, minimal scrap, optimized topology |
| High | Utilization 75–89%, low scrap, moderate optimization | |
| Moderate | Utilization 50–74%, noticeable scrap, limited optimization | |
| Low | Utilization < 50%, high scrap, poor optimization | |
| Energy Consumption | High | >10 kWh per part or equivalent high energy demand |
| Moderate | 5–10 kWh per part | |
| Low | <5 kWh per part | |
| Manufacturing Waste | High | >1 kg waste per part, low recycling |
| Moderate | 0.5–1 kg waste per part | |
| Low | 0.1–0.5 kg waste per part | |
| Very Low | <0.1 kg waste per part | |
| Transportation Impact | High | >500 km average transport distance |
| Moderate | 200–500 km | |
| Low | 50–199 km | |
| Very Low | <50 km | |
| Product Longevity | Very High | >10 years expected lifespan |
| High | 7–10 years | |
| Moderate | 3–6 years | |
| Low | <3 years | |
| End-of-Life Options | Good | Recyclability > 80%, established take-back programs |
| Moderate | Recyclability 50–79% | |
| Limited | Recyclability 20–49% | |
| Poor | Recyclability < 20% | |
| Post-Processing Needs | Extensive | >5 steps, >10 h, high cost |
| High | 3–5 steps, 5–10 h | |
| Moderate | 1–2 steps, 2–5 h | |
| Low | Minimal finishing, <2 h |
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| Publication | Research Domain | Research Design | Results |
|---|---|---|---|
| Cardoso et al. (2025) [53] | Aerospace | A comparative case study | AM gives lower environmental pollution values in comparison to conventional manufacturing |
| Favi et al. (2025) [54] | Systematic literature review, PRISMA framework | AM technologies enable eco-friendly and financially sustainable production. | |
| Falsafi et al. (2025) [55] | Automotive | PRISMA framework | Circular design must be integrated into LCA |
| Borda et al., 2024 [56] | Comparative analysis | Subtractive Manufacturing is less environmentally impacting than AM | |
| Výtisk et al., 2020 [57] | LCA is good for evaluating AM in terms of material and energy flows | ||
| Lunetto et al., 2019 [58] | Systematic review | There are risk indicators for applying LCA for AM | |
| Kokare et al., 2023 [59] | There are shortcomings in the LCA of AM | ||
| Soares et al., 2021 [60] | Medical Devices | Case study | There are social benefits of AM |
| Choudhary et al., 2023 [61] | Conceptual framework | AM provides managerial measures for the healthcare sector | |
| Mecheter et al., 2023 [62] | Industrial Equipment | Monte Carlo simulation, sensitivity analysis | The electricity utilization is eco-friendly in AM use |
| Garcia et al., 2018 [63] | Systematic review | Energy consumption is an important concern | |
| Mesecke et al., 2025 [41] | Energy | Systematic review | Hydrogen energy components can be produced by AM |
| Trolese et al., 2024 [43] | Case study | Complexity, lightweight characteristics, and high-performance are available through AM | |
| Bayat et al., 2025 [45] | Construction | Systematic review | Minimal personnel and resources, significantly reducing waste production |
| Martins et al., 2024 [46] | Exploratory case study | Complex geometrical designs are easy to handle with AM | |
| Kannan and Rajendran, 2016 [16] | Consumer Electronics | Systematic review | Rapid prototyping is available through AM |
| Pramanik et al., 2022 [50] | CAD enables direct production |
| Industry Type | Role in Company | Experience in This Field of Work | |
|---|---|---|---|
| 1 | Advanced metal production | Innovation and Product Developer | 14 years |
| 2 | Aviation industry | Technical manager | 16 years |
| 3 | Aerospace and drone parts | Factory manager | 21 years |
| 4 | Laser welding and 3D printing | Founder | 11 years |
| 5 | Laser technologies, metal machines | Sales manager | 11 years |
| 6 | Metal and machine production | Sales manager | 7 years |
| 7 | CAD software development | Industrial sales manager | 9 years |
| 8 | 3D metal printing | General manager | 12 years |
| 9 | SLM solutions | General manager | 19 years |
| 10 | Industrial machine production | Product owner | 6 years |
| 11 | 3D technology solutions | Sales specialist | 5 years |
| 12 | CAD, CAM, CAE software provider | Product owner | 3 years |
| 13 | Metal and metal powder supplier | Business development engineer | 3 years |
| 14 | Automation machines production | Sales operations administrator | 4 years |
| 15 | Manufacturing intelligence service provider | Industrial engineer | 2 years |
| 16 | Industrial machine production | Systems engineer | 2 years |
| 17 | 3D technology solutions | Product manager | 2 years |
| LCA Factors | Sub-Factors | LCA Factors | Sub-Factors |
|---|---|---|---|
| Raw Material Type [53,54,59,62] | Carbon fiber composites | Transportation Impact [9] | High |
| Metal powders | Moderate | ||
| Biocompatible metals | Low | ||
| Polymers | Very Low | ||
| Steel | Product Longevity [15] | Very high | |
| High-temperature alloys | High | ||
| Concrete mixtures | Moderate | ||
| Bio-based materials | Low | ||
| Thermoplastics | End-of-Life Options [7] | Good | |
| Polymers | Moderate | ||
| Resins | Limited | ||
| Conductive inks | Poor | ||
| Ceramics | Post-Processing Needs [28] | Extensive | |
| Material Efficiency [54,59] | Very high | High | |
| High | Moderate | ||
| Moderate | Low | ||
| Low | Environmental Certifications [7,15,60,61] | AS9100 [72] | |
| Energy Consumption [62,63] | High | ISO 14001 [73] | |
| Moderate | ISO 13485 [74] | ||
| Low | IATF 16949 [75] | ||
| Manufacturing Waste [56,58] | High | FDA compliance | |
| Moderate | CE marking | ||
| Low | LEED | ||
| Very Low | RoHS | ||
| WEEE |
| Factors | Sub-Factors | Utility Scores (%) | Factors | Sub-Factors | Utility Scores (%) |
|---|---|---|---|---|---|
| Raw Material Type | Carbon fiber composites | 10 | Transportation Impact | High | 10 |
| Metal powders | 20 | Moderate | 25 | ||
| Biocompatible metals | 8 | Low | 35 | ||
| Polymers | 12 | Very Low | 30 | ||
| Steel | 10 | Product Longevity | Very high | 30 | |
| High-temperature alloys | 8 | High | 30 | ||
| Concrete mixtures | 5 | Moderate | 25 | ||
| Bio-based materials | 7 | Low | 15 | ||
| Thermoplastics | 7 | End-of-Life Options | Good | 30 | |
| Resins | 5 | Moderate | 30 | ||
| Conductive inks | 3 | Limited | 25 | ||
| Ceramics | 5 | Poor | 15 | ||
| Material Efficiency | Very high | 30 | Post-Processing Needs | Extensive | 25 |
| High | 25 | High | 30 | ||
| Moderate | 25 | Moderate | 25 | ||
| Low | 20 | Low | 20 | ||
| Energy Consumption | High | 40 | Environmental Certifications | AS9100 [72] | 15 |
| Moderate | 35 | ISO 14001 [73] | 20 | ||
| Low | 25 | ISO 13485 [74] | 15 | ||
| Manufacturing Waste | High | 15 | IATF 16949 [75] | 10 | |
| Moderate | 30 | FDA compliance | 10 | ||
| Low | 35 | CE marking | 10 | ||
| Very Low | 20 | LEED | 8 | ||
| RoHS | 6 | ||||
| WEEE | 6 |
| LCA Factors | Aerospace | Automotive | Medical Devices | Industrial Equipment | Energy Sector | Construction | Consumer Electronics |
|---|---|---|---|---|---|---|---|
| Raw Material Type | High-performance metal powders (Titanium, Inconel), carbon fiber composites | Metal powders (Aluminum, Titanium), polymers (ABS, Nylon) | Biocompatible metals (Titanium, Cobalt-Chrome), medical-grade polymers | Tool steels, stainless steel, engineering polymers | High-temperature alloys, ceramics, polymers | Concrete mixtures, recycled polymers, bio-based materials | Thermoplastics (PLA, ABS), resins, conductive inks |
| Material Efficiency | Very high due to topology optimization and lightweighting | High; optimized designs reduce material use | Very high; patient-specific designs minimize waste | High; AM enables repair and remanufacturing | High; optimized for thermal and mechanical performance | Moderate; depends on design and material | Moderate; small parts often require supports |
| Energy Consumption | High, especially for metal AM processes like Electron Beam Melting | Moderate; varies by part complexity and material | High due to precision and sterilization needs | Moderate to high, depending on part size | Moderate; varies by application | Moderate; large-scale printers vary | Moderate; varies by printer and batch size |
| Manufacturing Waste | Low; near-net-shape production minimizes scrap | Low; AM reduces tooling and scrap | Very low; customized production avoids excess | Moderate; depends on support structures | Moderate; depends on complexity | Moderate; AM reduces formwork waste | Moderate; failed prints and supports contribute |
| Transportation Impact | Reduced via localized production of critical parts | Lower due to localized spare part production | Reduced by producing near hospitals or clinics | Reduced via on-site or regional production | Reduced via rapid part replacement | Reduced via on-site printing | Reduced via localized production |
| Product Longevity | Very high; parts are durable and optimized for performance | High; durable components with extended life | Very high; implants and tools are long-lasting | High; AM parts extend equipment life | High; AM improves efficiency and durability | High; structural components are durable | Low to moderate; rapid obsolescence |
| End-of-Life Options | Moderate; recycling of high-grade alloys is possible | Good; metals are recyclable, polymers less so | Limited; disposal protocols vary by material | Moderate; metals recyclable, polymers less so | Moderate; recycling possible for metals | Limited; recycling of printed concrete is complex | Poor; mixed materials complicate recycling |
| Post-Processing Needs | Extensive (heat treatment, surface finishing, inspection) | Moderate (machining, painting, assembly) | High (polishing, sterilization, testing) | Moderate (heat treatment, machining) | Moderate (coating, testing) | Low to moderate (finishing, curing) | Moderate (cleaning, curing, assembly) |
| Environmental Certifications | Strong compliance (AS9100 [72], ISO 14001 [73]) | ISO 14001 [73], IATF 16949 [75] | ISO 13485 [74], FDA compliance | ISO 14001 [73], CE marking | ISO 14001 [73], industry-specific standards | LEED, ISO 14001 [73] | RoHS, WEEE, ISO 14001 [73] |
| Raw Material Type | Material Efficiency | Energy Consumption | Manufacturing Waste | Transportation Impact | Product Longevity | End-of-Life Options | Post-Processing Needs | Environmental Certifications | |
|---|---|---|---|---|---|---|---|---|---|
| Aerospace | 9 | 9 | 8 | 8 | 7 | 9 | 7 | 8 | 9 |
| Automotive | 8 | 9 | 7 | 8 | 7 | 8 | 7 | 6 | 8 |
| Medical Devices | 9 | 9 | 8 | 9 | 8 | 9 | 5 | 8 | 9 |
| Industrial Equipment | 8 | 8 | 7 | 7 | 6 | 8 | 6 | 7 | 8 |
| Energy Sector | 8 | 8 | 7 | 7 | 6 | 8 | 6 | 7 | 8 |
| Construction | 7 | 7 | 6 | 6 | 6 | 7 | 5 | 6 | 7 |
| Consumer Electronics | 6 | 6 | 6 | 5 | 7 | 4 | 3 | 5 | 7 |
| Raw Material Type | Material Efficiency | Energy Consumption | Manufacturing Waste | Transportation Impact | Product Longevity | End-of-Life Options | Post-Processing Needs | Environmental Certifications | Final Weight | Final Rank | |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Aerospace | 0.88 | 0.83 | 0.09 | 0.25 | 0.34 | 0.82 | 0.87 | 0.11 | 0.91 | 0.56 | 4 |
| Automotive | 0.56 | 0.83 | 0.50 | 0.25 | 0.34 | 0.61 | 0.87 | 0.76 | 0.50 | 0.58 | 1 |
| Medical Devices | 0.88 | 0.83 | 0.09 | 0.07 | 0.03 | 0.82 | 0.33 | 0.11 | 0.91 | 0.45 | 6 |
| Industrial Equipment | 0.56 | 0.50 | 0.50 | 0.55 | 0.85 | 0.61 | 0.63 | 0.39 | 0.50 | 0.56 | 2 |
| Energy Sector | 0.56 | 0.50 | 0.50 | 0.55 | 0.85 | 0.61 | 0.63 | 0.39 | 0.50 | 0.56 | 2 |
| Construction | 0.19 | 0.17 | 0.91 | 0.82 | 0.85 | 0.36 | 0.33 | 0.76 | 0.09 | 0.50 | 5 |
| Consumer Electronics | 0.03 | 0.03 | 0.91 | 0.96 | 0.34 | 0.01 | 0.02 | 0.95 | 0.09 | 0.37 | 7 |
| PrOPPAGA | AHP-Gaussian | MOORA | COPRAS | MOOSRA | MABAC | WASPAS | VIKOR | |
|---|---|---|---|---|---|---|---|---|
| Aerospace | 4 | 2 | 2 | 1 | 2 | 2 | 2 | 1 |
| Automotive | 1 | 1 | 1 | 2 | 7 | 1 | 3 | 2 |
| Medical Devices | 6 | 6 | 6 | 6 | 1 | 6 | 1 | 3 |
| Industrial Equipment | 2 | 3 | 3 | 3 | 5 | 3 | 5 | 4 |
| Energy Sector | 2 | 3 | 3 | 3 | 5 | 3 | 4 | 4 |
| Construction | 5 | 5 | 5 | 5 | 3 | 5 | 6 | 6 |
| Consumer Electronics | 7 | 7 | 7 | 7 | 3 | 7 | 7 | 7 |
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Karadayi-Usta, S. Sustainability Through Additive Manufacturing Operations: A Comparative Industrial Analysis with a Life Cycle Assessment Case Study of Türkiye. Logistics 2026, 10, 7. https://doi.org/10.3390/logistics10010007
Karadayi-Usta S. Sustainability Through Additive Manufacturing Operations: A Comparative Industrial Analysis with a Life Cycle Assessment Case Study of Türkiye. Logistics. 2026; 10(1):7. https://doi.org/10.3390/logistics10010007
Chicago/Turabian StyleKaradayi-Usta, Saliha. 2026. "Sustainability Through Additive Manufacturing Operations: A Comparative Industrial Analysis with a Life Cycle Assessment Case Study of Türkiye" Logistics 10, no. 1: 7. https://doi.org/10.3390/logistics10010007
APA StyleKaradayi-Usta, S. (2026). Sustainability Through Additive Manufacturing Operations: A Comparative Industrial Analysis with a Life Cycle Assessment Case Study of Türkiye. Logistics, 10(1), 7. https://doi.org/10.3390/logistics10010007
