Submitted:
19 May 2025
Posted:
20 May 2025
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Abstract

Keywords:
1. Introduction
2. Literature Review
3. Preliminaries
3.1. General Type-2 Fuzzy Sets
3.2. Interval Type-2 Fuzzy Sets
3.3. Arithmetic Operations in Type-2 Fuzzy Sets
3.4. Interval Type-2 Fuzzy VIKOR Method (IT2 F-VIKOR)
-
Transformation of Upper and Lower Membership Functions into Type-1 Fuzzy Sets: Here, to obtain a Type-1 fuzzy set, the average of the upper and lower membership functions is calculated.Here; represents the value of the upper membership function, and represents the value of the lower membership function.As a result of this process, our type-2 fuzzy set is transformed into a type-1 fuzzy set.
- Defuzzification: Here, the Weighted Average (Centroid) Method is applied to defuzzify the type-1 fuzzy set: This significantly simplifies the computation required to find the center of a two-dimensional shape, thus enhancing the efficiency of the defuzzification process [13].
3.5. DEMATEL Method (The Decision Making Trial and Evaluation Laboratory Method)
3.6. QFD Model

4. A Combined Selection Method for Green Supplier Selection
4.1. Stage I: Identification of Customer, Green Supplier Selection Requirements, and Alternatives
4.2. Stage II: Weighting of Customer and Green Supplier Selection Criteria
4.3. Stage III: Weighting of Suppliers According to Each Green Supplier Selection Criterion
4.4. Stage IV: Ranking Alternatives Using the IT2 F-VIKOR Method
5. Application of the Proposed Method
5.1. Ranking of Alternatives Using IT2 VIKOR
6. Analysis of Result
7. Conclusion and Discussion
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
AI Declaration Statement
Abbreviations
| MCDM | Multi-Criteria Decision-Making |
| IT2 F-VIKOR | Interval Type-2 Fuzzy VIKOR |
| QFD | Quality Function Deployment |
| DEMATEL | Decision-Making Trial and Evaluation Laboratory |
| LR | Long range |
| FCT | Fast charging time |
| S | Safety |
| EFR | Environmental friendliness and recyclability |
| LC | Low cost |
| CF | Carbon Footprint (CO₂ Emissions) |
| WMRR | Waste Management and Recycling Rate |
| TCMU | Use of Toxic and Critical Materials |
| GEU | Use of Green Energy |
| EELI | Energy Efficiency and Lifetime Impact |
References
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| Author / Authors | Applied Method | Application Area |
| [8] | ORESTE method | Automotive-Battery Supplier Selection |
| [9] | Fuzzy QFD- Multiple regression Method | Automotive - Hybrid electric vehicles |
| [6] | Type-2 Fuzzy TOPSIS, Type-2 Fuzzy Hamming | Energy-Battery industry |
| [10] | Classical VIKOR- Fuzzy VIKOR | Transportation-Energy-Sensors |
| [11] | Fuzzy DEMATEL- LPWBN | Automotive - Electric vehicle - Battery supplier selection |
| [12] | DEMATEL-ISM | Automotive - Electric vehicle selection |
| Customer Requirements (Customer Demands) (CRs) | Explanation |
| Long range (LR) | It is the maximum distance that an electric vehicle can travel on a single full charge. |
| Fast charging time (FCT) | It refers to the time required for the battery to reach a specific charge level. |
| Safety (S) | It refers to the level of protection the vehicle and battery provide to the user against physical hazards. |
| Environmental friendliness and recyclability (EFR) | It refers to the minimal environmental impact of the battery's production, use, and disposal processes, as well as the inclusion of recyclable materials. |
| Low cost (LC) | It refers to the minimal impact of the battery on the vehicle's price or ensuring that its total cost remains at an acceptable level. |
| Green Supplier Selection Criteria | Explanation |
| Carbon Footprint (CO₂ Emissions) (CF) | It refers to the total greenhouse gas emissions (especially CO₂) generated throughout the process from raw material extraction to production, transportation, and usage of the battery. Low emissions are crucial for reducing environmental impacts. |
| Waste Management and Recycling Rate (WMRR) | It refers to how much of the battery can be recycled when its lifespan ends and how environmentally friendly this process is. A high recycling rate reduces resource waste and environmental pollution. |
| Use of Toxic and Critical Materials (TCMU) | It refers to the amount and type of materials used in the battery that are harmful to the environment and human health (e.g., cobalt, lead, fluoride electrolytes) or are at risk in terms of sourcing. Reducing the use of such materials is important both environmentally and ethically. |
| Use of Green Energy (GEU) | It refers to whether renewable energy sources (such as solar, wind, etc.) are used in the battery production processes. The use of green energy significantly reduces the environmental impact of the production process. |
| Energy Efficiency and Lifetime Impact (EELI) | It refers to how efficiently the battery provides energy and the total environmental impact throughout its entire life cycle. Long-lasting and highly efficient batteries reduce resource usage and waste generation |
| Abbreviation of the Alternatives | Battery Type / Criteria | Carbon Footprint (CO2 Emissions) | Recycling and Waste Management | Use of Toxic / Critical Materials | Use of Green Energy | Energy Efficiency and Lifetime Impact |
| A1 | NMC (Li-ion) |
High Intensive mining and processing process |
Medium It has existing infrastructure but is costly |
High Contains Cobalt and Nickel |
Low-Medium Typically produced using fossil energy |
Medium-High Good range but limited cycle life |
| A2 | LFP (LiFePO₄) |
Medium Simpler structure, production with lower energy |
High Easy and safe recycling |
Low Does not contain critical materials |
Medium-High Production is increasing with solar energy |
High Long cycle life and stable performance |
| A3 | Solid-State |
Medium-High Its production is complex; however, there is potential for cost reduction |
Medium As an emerging system, it encompasses both advantages and disadvantages |
Low-Medium It may vary depending on the material selection |
High (Objective) It is planned to increase the use of clean energy in production in the future. |
Very High Very long lifespan and high energy density |
| A4 | Li-S (Lithium Sulfur) |
Medium Lightweight material but inefficient production |
Low Sulfur-based structure poses challenges in recycling |
Low Does not contain critical materials |
Low In R&D-focused production, conventional energy is typically used |
Medium High capacity but short lifespan |
| A5 | Sodium-Ion |
Low Abundant resources, low-temperature production |
High Easy recycling due to its simple structure |
Low Does not contain toxic materials |
High Low temperature and production are easy with green energy |
Medium Low energy density, but durable structures are possible |
| CRs | LR | FCT | S | EFR | LC |
| LR | 0 | 1 | 2 | 2 | 3 |
| FCT | 2 | 0 | 1 | 1 | 3 |
| S | 3 | 2 | 0 | 1 | 2 |
| EFR | 3 | 3 | 3 | 0 | 3 |
| LC | 1 | 1 | 1 | 2 | 0 |
| CRs | LR | FCT | S | EFR | LC |
| LR | 0.0000 | 0.0833 | 0.1667 | 0.1667 | 0.2500 |
| FCT | 0.1667 | 0.0000 | 0.0833 | 0.0833 | 0.2500 |
| S | 0.2500 | 0.1667 | 0.0000 | 0.0833 | 0.1667 |
| EFR | 0.2500 | 0.2500 | 0.2500 | 0.0000 | 0.2500 |
| LC | 0.0833 | 0.0833 | 0.0833 | 0.1667 | 0.0000 |
| CRs | LR | FCT | S | EFR | LC |
| LR | 0.2810 | 0.3055 | 0.3752* | 0.3619 | 0.5497* |
| FCT | 0.3732* | 0.1844 | 0.2693 | 0.2668 | 0.5010* |
| S | 0.4791* | 0.3575 | 0.2233 | 0.2926 | 0.4862* |
| EFR | 0.6029* | 0.5221* | 0.5279* | 0.3038 | 0.6952* |
| LC | 0.2782 | 0.2409 | 0.2436 | 0.2941 | 0.2439 |
| CRs | Dk (Influencing) | Rk (Influenced) |
| LR | 1.8733 | 2.0144 |
| FCT | 1.5947 | 1.6104 |
| S | 1.8387 | 1.6393 |
| EFR | 2.6519 | 1.5192 |
| LC | 1.3007 | 2.4760 |
| CRs | D + R | D - R | Group |
| LR | 3.8877 | -0.1411 | Conclusion |
| FCT | 3.2051 | -0.0157 | Conclusion |
| S | 3.4780 | 0.1994 | Reason |
| EFR | 4.1711 | 1.1327 | Reason |
| LC | 3.7767 | -1.1753 | Conclusion |
| CRs | LR | FCT | S | EFR | LC |
| Ağırlıklar | 0.2099 | 0.1731 | 0.1878 | 0.2252 | 0.2039 |
| HOW’s (CRs) | WHAT’s (Green Supplier Selection Criteria) | Weights of CRs | |||||
| CF | WMRR | TCMU | GEU | EELI | |||
| LR | 3 | 1 | 1 | 1 | 9 | 0.2099 | |
| FCT | 1 | 1 | 1 | 1 | 6 | 0.1731 | |
| S | 3 | 3 | 9 | 1 | 6 | 0.1878 | |
| EFR | 9 | 9 | 3 | 6 | 6 | 0.2252 | |
| LC | 3 | 3 | 6 | 3 | 3 | 0.2039 | |
| Absolute Importance Values | 4.0047 | 3.2093 | 3.9722 | 2.5337 | 6.0174 | ||
| Normalized Criterion Weights | 0.2029 | 0.1626 | 0.2013 | 0.1284 | 0.3049 | ||
| Alternatives | Criteria | ||||
|
CF (Minimize) (0-10) |
WMRR (Maximize) (0-10) |
TCMU (Minimize) (0-10) |
GEU (Maximize) (0-10) |
EELI (Maximize) (0-10) |
|
| A1 | (2, 3.5, 5;1,1) (2.5, 3.5, 4.5;0.8, 0.8) |
(4, 5.5, 7;1,1) (4.4, 5.5, 6.6;0.8, 0.8) |
(1, 2.5, 4;1,1) (1.3, 2.5, 3.7;0.8, 0.8) |
(4, 5, 6;1,1) (4.2, 5, 5.8;0.8, 0.8) |
(5, 6, 7;1,1) (5.2, 6, 6.8;0.8, 0.8) |
| A2 | (5, 6.5, 8;1,1) (5.4, 6.5, 7.6;0.8, 0.8) |
(7, 8.5, 10;1,1) (7.3, 9, 9.7;0.8, 0.8) |
(8, 9, 10;1,1) (8.4, 9, 9.6;0.8, 0.8) |
(5, 7, 8;1,1) (5.6, 7, 7.4;0.8, 0.8) |
(7, 9, 10;1,1) (7.3, 9, 9.7;0.8, 0.8) |
| A3 | (5, 6, 7;1,1) (5.5, 6, 6.5;0.8, 0.8) |
(4.5, 5.5, 6.5;1,1) (5, 5.5, 6;0.8, 0.8) |
(4.5, 6, 7.5;1,1) (5, 6, 7;0.8, 0.8) |
(7, 9, 10;1,1) (7.6, 9, 9.4;0.8, 0.8) |
(8, 9, 10;1,1) (8.3, 9, 9.7;0.8, 0.8) |
| A4 | (5.5, 6.4, 8;1,1) (6, 6.4, 7.5;0.8, 0.8) |
(3, 4, 5.5;1,1) (3.3, 4, 5.2;0.8, 0.8) |
(6, 7.5, 9;1,1) (6.6, 7.5, 8.4;0.8, 0.8) |
(3, 4, 5;1,1) (3.4, 4, 4.6;0.8, 0.8) |
(2, 3.5, 5;1,1) (2.5, 4, 4.5;0.8, 0.8) |
| A5 | (8, 9, 10;1,1) (8.5, 9, 9.5;0.8, 0.8) |
(9, 9.5, 10;1,1) (9.2, 9.5, 9.8;0.8, 0.8) |
(9, 9.5, 10;1,1) (9.3, 9.5, 9.7;0.8, 0.8) |
(9, 9.5, 10;1,1) (9.2, 9.5, 9.8;0.8, 0.8) |
(5, 6, 7;1,1) (5.5, 6, 6.5;0.8, 0.8) |
| Criterion | Best | |
| CF (Minimize) | (2, 3.5, 5;1,1) (2.5, 3.5, 4.5;0.8, 0.8) |
(8, 9, 10;1,1) (8.5, 9, 9.5;0.8, 0.8) |
| WMRR (Maximize) | (9, 9.5, 10;1,1) (9.2, 9.5, 9.8;0.8, 0.8) |
(3, 4, 5.5;1,1) (3.3, 4, 5.2;0.8, 0.8) |
| TCMU (Minimize) | (1, 2.5, 4;1,1) (1.3, 2.5, 3.7;0.8, 0.8) |
(9, 9.5, 10;1,1) (9.3, 9.5, 9.7;0.8, 0.8) |
| GEU (Maximize) | (9, 9.5, 10;1,1) (9.2, 9.5, 9.8;0.8, 0.8) |
(3, 4, 5;1,1) (3.4, 4, 4.6;0.8, 0.8) |
| EELI (Maximize) | (8, 9, 10;1,1) (8.3, 9, 9.7;0.8, 0.8) |
(2, 3.5, 5;1,1) (2.5, 4, 4.5;0.8, 0.8 |
| Alternatives |
CF (Minimize) |
WMRR (Maximize) |
TCMU (Minimize) |
GEU (Maximize) |
EELI (Maximize) |
| A1 | (0, 0, 0;1,1) (0, 0, 0;0.8, 0.8) |
(0.1355, 0.1183, 0.1084;1,1) (0.1323, 0.1183, 0.1131;0.8, 0.8) |
(0, 0, 0;1,1) (0, 0, 0;0.8, 0.8) |
(0.1070, 0.1051, 0.1027;1,1) (0.1107, 0.1051, 0.0988;0.8, 0.8) |
(0.1525, 0.1663, 0.1829;1,1) (0.1630, 0.1829, 0.1700;0.8, 0.8) |
| A2 | (0.1015, 0.1107, 0.1217;1,1) (0.0981, 0.1107, 0.1258;0.8, 0.8) |
(0.0542, 0.0296, 0.0000;1,1) (0.0524, 0.0148, 0.0035;0.8, 0.8) |
(0.1761, 0.1869, 0.2013;1,1) (0.1787, 0.1869, 0.1979;0.8, 0.8) |
(0.0856, 0.0584, 0.0514;1,1) (0.0797, 0.0584, 0.0593;0.8, 0.8) |
(0.0508, 0.0000, 0.0000;1,1) (0.0526, 0.0000, 0.0000;0.8, 0.8) |
| A3 | (0.1015, 0.0922, 0.0812;1,1) (0.1015, 0.0922, 0.0812; 0.8, 0.8) |
(0.1220, 0.1183, 0.1138;1,1) (0.1157, 0.1183, 0.1343;0.8, 0.8) |
(0.0881, 0.1007, 0.1174;1,1) (0.0931, 0.1007, 0.1107;0.8, 0.8) |
(0.0428, 0.0117, 0.0000;1,1) (0.0354, 0.0117, 0.0099;0.8, 0.8) |
(0, 0, 0;1,1) (0, 0, 0;0.8, 0.8) |
| A4 | (0.2367, 0.2213, 0.2029;1,1) (0.2266, 0.2213, 0.2151; 0.8, 0.8) |
(0.1626, 0.1626, 0.1463;1,1) (0.1626, 0.1626, 0.1626;0.8, 0.8) |
(0.1258, 0.1438, 0.1678;1,1) (0.1334, 0.1438, 0.1577;0.8, 0.8) |
(0.1284, 0.1284, 0.1284;1,1) (0.1284, 0.1284, 0.1284;0.8, 0.8) |
(0.3049, 0.3049, 0.3049;1,1) (0.3049, 0.3049, 0.3049;0.8, 0.8) |
| A5 | (0.2029, 0. 2029, 0. 2029;1,1) (0.1961, 0.2029, 0.2110; 0.8, 0.8) |
(0, 0, 0;1,1) (0, 0, 0;0.8, 0.8) |
(0.2013, 0.2013, 0.2013;1,1) (0.2013, 0.2013, 0.2013;0.8, 0.8) |
(0, 0, 0;1,1) (0, 0, 0;0.8, 0.8) |
(0.1525, 0.1663, 0.1839;1,1) (0.1472, 0.1829, 0.1876;0.8, 0.8) |
| Alternatives | (The sum of all criteria) | (he largest criterion value) |
| A1 | (0.3950, 0.3897, 0.3940;1,1) (0.4060, 0.4063, 0.3819;0.8, 0.8) |
(0.1525, 0.1663, 0.1829;1,1) (0.1630, 0.1829, 0.1700;0.8, 0.8) |
| A2 | (0.4682, 0.3856, 0.3744;1,1) (0.4615, 0.3708, 0.3865;0.8, 0.8) |
(0.1761, 0.1869, 0.2013;1,1) (0.1787, 0.1869, 0.1979;0.8, 0.8) |
| A3 | (0.3544, 0.3229, 0.3124;1,1) (0.3457, 0.3229, 0.3361;0.8, 0.8) |
(0.1220, 0.1183, 0.1174;1,1) (0.1157, 0.1183, 0.1343;0.8, 0.8) |
| A4 | (0.9584, 0.9610, 0.9503;1,1) (0.9559, 0.9610, 0.9684;0.8, 0.8) |
(0.3049, 0.3049, 0.3049;1,1) (0.3049, 0.3049, 0.3049;0.8, 0.8) |
| A5 | (0.5567, 0.5705, 0.5881;1,1) (0.5446, 0.5871, 0.5999;0.8, 0.8) |
(0.2029, 0.2029, 0.2029;1,1) (0.2013, 0.2029, 0.2110;0.8, 0.8) |
| Alternative | VIKOR Index () |
| A1 | (0.1170, 0.1810, 0.2386;1, 1) (0.1744, 0.2384, 0.1408;0.8, 0.8) |
| A2 | (0.2421, 0.2329, 0.2723;1, 1) (0.2614, 0.2213, 0.2263;0.8, 0.8) |
| A3 | (0.0000, 0.0000, 0.00000;1, 1) (0.0000, 0.0000, 0.0000;0.8, 0.8) |
| A4 | (1.0000, 1.0000, 1.00000;1, 1) (1.0000, 1.0000, 1.0000;0.8, 0.8) |
| A5 | (0.3886, 0.4207, 0.4441;1, 1) (0.3892, 0.4337, 0.4334;0.8, 0.8) |
| has been taken | |
| Alternative | |
| A1 | 0.1817 |
| A2 | 0.2427 |
| A3 | 0.0000 |
| A4 | 1.0000 |
| A5 | 0.4183 |
| Alternatives | A3 | A1 | A2 | A5 | A4 |
| Values of Alternatives Calculated Using the DEMATEL-QFD-IT2 F-VIKOR Method | 0.0000 | 0.1817 | 0.2427 | 0.4183 | 1.0000 |
| Ranking Performance of Alternatives | 1 | 2 | 3 | 4 | 5 |
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