A Cloud Model-Based CRITIC-EDAS Decision-Making Approach with Linguistic Information for Marine Ranching Site Selection
Abstract
:1. Introduction
1.1. Aims of This Study
1.2. Motivation for Developing a Cloud Model-Based CRITIC-EDAS
1.3. Contribution of This Study
- This study constructs a methodology for marine ranching site selection by considering fuzziness and randomness simultaneously. Existing decision-making approaches for marine ranching site selection only take into account the fuzziness of data, while the data collected by detectors and the linguistic terms given by experts are random due to the dynamics and volatility of sample points and human cognition. Therefore, a cloud model is first introduced to reveal the fuzziness and randomness of data in marine ranching site selection problems.
- A new method for determining the relative importance of attributes in marine ranching site selection problems is proposed by integrating CRITIC and the cloud model. The collected evaluation values are transferred from linguistic terms into corresponding clouds, and then the CRITIC approach is extended to handle these clouds in order to obtain the weights of attributes.
- A novel model, named cloud model-based EDAS, is developed to determine the ranks of alternatives in marine ranching site selection problems. The proposed model obtains the final evaluation scores of alternative sites in the form of clouds, which reserve the fuzziness and randomness of evaluation results in order to determine the optimal alternative for marine ranching site selection in a scientific way.
- A real-world marine ranching site selection problem in the city of Yantai is solved by using the cloud model-based CRITIC-EDAS model. Firstly, an evaluation attribute system for modern marine ranching site selection problems is determined from a comprehensive perspective, and then, by transforming linguistic evaluation values into clouds, the proposed model is utilized to obtain the optimal site for marine ranching in Yantai city.
- A comparison of the proposed model with the existing approaches is conducted in the same case to demonstrate its superiority and consistency.
1.4. Organization of This Study
2. Preliminaries
2.1. Cloud Model
- (1)
- (2)
- (3)
- (4)
- (5)
2.2. Linguistic Variables
- (1)
- The set is ordered: if and only if ;
- (2)
- There is the negation operator: .
3. An Innovative CRITIC-EDAS Approach Based on the Cloud Model
3.1. Framework of the Proposed Model
3.2. Cloud Model-Based CRITIC Methodology
- Step 1.
- Obtain the linguistic evaluation matrix of expert .
- Step 2.
- Transform to cloud evaluation matrices.
- Step 3.
- Construct a group cloud decision matrix.
- Step 4.
- Construct a normalized cloud decision matrix.
- Step 5.
- Identify the correlation coefficient.
- Step 6.
- Calculate the index of each attribute.
- Step 7.
- Determine the weights of attributes.
3.3. Cloud Model-Based EDAS Methodology
- Step 1.
- Construct a normalized cloud decision matrix.
- Step 2.
- Determine the cloud average solution vector.
- Step 3.
- Construct the cloud positive distance from the average matrix and the cloud negative distance from the average matrix.
- Step 4.
- Calculate the weighted arithmetic average of CPDA and CNDA.
- Step 5.
- Normalize the values of and .
- Step 6.
- Determine the cloud appraisal scores.
- Step 7.
- Determine the final ranking of alternatives.
4. Case Study: Marine Ranching Site Selection in Yantai
4.1. Problem Description
- (1)
- Six marine areas were identified beforehand as alternative sites for further evaluation, which are denoted as .
- (2)
- A committee composed of five experts was formed, denoted as . All the experts are professionals in marine economy, consisting of two enterprise managers, two governmental staff members and one college professor. In order to reserve their evaluation information impartially, we consider that each expert plays an equally important role, so the relative importance vector of the experts is .
- (3)
- The decision committee collects the data according to the evaluation index system as shown in Figure 6. The evaluation index system contains 5 primary indices and 16 secondary indices, which can be acquired by corresponding monitors. Table 1 shows the collected data of among all the secondary indices. In order to reduce complexity and interactivity among different secondary indices, experts evaluate each alternative from five primary indices by using linguistic terms according to the specific data of secondary indices. And the five primary indices are denoted as five attributes in the marine ranching site selection problem:
- Physical environment ();
- Chemical environment ();
- Biological environment ();
- Engineering environment ();
- Social environment ().
- (4)
- Collect the specific data of all the alternatives on 16 secondary indices, and then experts evaluate alternatives on 5 primary attributes by using the following 7-label linguistic terms:
4.2. Assessing the Significance of Attributes Using Cloud CRITIC
- Step 1.
- Collect the linguistic evaluation information of experts as described in Table 2.
- Step 2.
- Transform the linguistic evaluation matrix of each expert into a cloud evaluation matrix. Given the universe , the 7-label linguistic term set can be transformed to seven clouds by using the transformation rule in Definition 7. Selecting , the transformed clouds are depicted in Table 6.
- Step 3.
- Compile all decision matrices and create an aggregated cloud decision matrix . In these cases, we consider that the all the experts possess the same significance; therefore, we use the CAA operator depicted in Equation (3) to aggregate cloud evaluation information. The group cloud decision matrix is shown in Table 7.
- Step 4.
- Normalize the aggregated cloud assessment information by using Equation (10). The normalized cloud decision is conducted as shown in Table 8.
- Step 5.
- Calculate the distance correlation coefficient among all attributes.
- Step 6.
- Calculate the index by using Equation (13), which is illustrated in Table 12. To provide a clear understanding of how to obtain the index of each attribute, we use as an example.
- Step 7.
- Calculate the weights of attributes by using Equation (14); the results are described in the last column of Table 12.
4.3. Evaluating Alternatives Using Cloud EDAS
- Step 1.
- Similar to the procedure depicted in the cloud CRITIC, the normalized group cloud decision matrix can be constructed as shown in Table 8.
- Step 2.
- Calculate the cloud average solution of each attribute, which is equivalent to the mean value in the cloud CRITIC. Therefore, we can obtain the cloud average solution vector as depicted in Table 13.
- Step 3.
- Step 4.
- According to the CWAA operator shown in Equation (2) as well as the weight vector determined by the cloud CRITIC, the weighted arithmetic averages of CPDA and CNDA for each alternative can be calculated as shown in Table 16.
- Step 5.
- Normalize the weighted arithmetic averages by using Equations (25) and (26); the results are depicted in the right columns of Table 16.
- Step 6.
- The cloud appraisal scores of the marine ranching sites are depicted in the last column of Table 16 and are obtained with the help of Equation (27) based on the arithmetic average of and .
- Step 7.
- In order to compare the cloud appraisal scores and determine the ranking of marine ranching sites, we generate cloud drops and calculate the expected score value for each alternative. With different numbers of cloud drops, the expected scores and final rankings are depicted as shown in Table 17. The results in Table 17 illustrate that, according to different numbers of cloud drops, the ranking of the alternatives by expected scores can be determined as: . Thus, should be selected as the best site to establish marine ranching. The cloud appraisal scores of the six alternatives are plotted as shown in Figure 7.
4.4. Comparison and Discussion
5. Conclusions
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
References
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MADM Methods | Evaluations | Applications | Reference |
---|---|---|---|
AHP | Intervals | Select a house by home buyers | [16] |
TOPSIS | Linguistic terms | Online education satisfaction assessment | [20] |
VIKOR | Linguistic terms | Evaluate the risk of an informatization project | [18] |
CoCoSo | Linguistic terms | Select a trusted cloud service provider | [21] |
Complex network | Crisp numbers | Vulnerability assessment for traffic systems | [22] |
TOPSIS | Rough numbers | Sustainable supplier selection | [23] |
Environments | Applications | Reference |
---|---|---|
Interval-valued intuitionistic fuzzy sets | Transportation mode selection | [16] |
Linguistic Pythagorean fuzzy sets | Industrial waste management technique selection | [20] |
Probabilistic uncertain linguistic sets | Site selection for hospital constructions | [27] |
Fermatean fuzzy sets | - | [21] |
Picture fuzzy sets | Wearable health technology selection | [29] |
Type-2 fuzzy sets | Site selection for nursing homes | [30] |
Environments | Applications | Reference |
---|---|---|
Fuzzy sets | Supplier selection | [16] |
Probabilistic hesitant fuzzy sets | Selection of commercial vehicles and green suppliers | [20] |
Q-rung orthopair fuzzy sets | Supplier selection in the defense industry | [24] |
Linguistic intuitionistic fuzzy sets | Selection of houses and travel destinations | [21] |
Picture fuzzy soft sets | Robotic agrifarming | [24] |
Interval-type 2 fuzzy sets | Route selection of petroleum transportation | [30] |
Primary Indices | Secondary Indices | Data of Indices | e1 | e2 | e3 | e4 | e5 | |
---|---|---|---|---|---|---|---|---|
S1 | Physical environment | Average depth | 14.8 m | G | M | G | VG | M |
Sediment particle size | 0.2 mm | |||||||
Dissolved oxygen | 5.45 mg/L | |||||||
Chemical environment | Inorganic nitrogen | 1.67 mg/L | VG | EG | VG | VG | G | |
Sulfide content | 63 mg/kg | |||||||
Active phosphate | 0.032 mg/L | |||||||
Biological environment | Plant plankton biomass | 125 × 104 ind/m3 | G | VG | M | M | G | |
Zooplankton biomass | 76.3 mg/m3 | |||||||
Benthic biomass | 89.7 g/m2 | |||||||
Chlorophyll A | 3.78 mg/m3 | |||||||
Engineering environment | Bottom load | 1.2 t/m2 | EP | VP | VP | VP | VP | |
Silt thickness | 0.61 m | |||||||
Seabed slope | 4.1 m | |||||||
Social environment | Fishery resource density | 48 kg/m2 | M | P | M | G | P | |
Distance to scenic spots | 7.8 km | |||||||
Distance to submarine pipeline | 12.1 km |
C1 | C2 | C3 | C4 | C5 | |
---|---|---|---|---|---|
S1 | |||||
S2 | |||||
S3 | |||||
S4 | |||||
S5 | |||||
S6 |
Linguistic Terms | Clouds |
---|---|
EP | (0.000, 0.771, 0.042) |
VP | (1.667, 0.476, 0.026) |
P | (3.333, 0.294, 0.016) |
M | (5.000, 0.182, 0.010) |
G | (6.667, 0.294, 0.016) |
VG | (8.333, 0.476, 0.026) |
EG | (10.000, 0.771, 0.042) |
C1 | C2 | C3 | C4 | C5 | |
---|---|---|---|---|---|
S1 | (6.333, 0.305, 0.017) | (8.333, 0.522, 0.028) | (6.333, 0.305, 0.017) | (1.334, 0.548, 0.030) | (4.667, 0.255, 0.014) |
S2 | (6.667, 0.322, 0.018) | (2.333, 0.413, 0.023) | (9.667, 0.722, 0.039) | (1.334, 0.548, 0.030) | (6.000, 0.255, 0.014) |
S3 | (1.667, 0.522, 0.028) | (7.000, 0.338, 0.018) | (9.333, 0.669, 0.036) | (7.667, 0.413, 0.023) | (6.667, 0.322, 0.018) |
S4 | (7.667, 0.413, 0.023) | (8.666, 0.548, 0.030) | (6.667, 0.322, 0.018) | (7.000, 0.338, 0.018) | (2.333, 0.413, 0.023) |
S5 | (8.000, 0.446, 0.024) | (5.333, 0.255, 0.014) | (7.000, 0.363, 0.020) | (4.667, 0.255, 0.014) | (8.333, 0.522, 0.028) |
S6 | (3.000, 0.338, 0.018) | (8.333, 0.522, 0.028) | (3.333, 0.322, 0.018) | (7.000, 0.338, 0.018) | (6.000, 0.255, 0.014) |
C1 | C2 | C3 | C4 | C5 | |
---|---|---|---|---|---|
S1 | (0.737, 0.211, 0.007) | (0.947, 0.207, 0.011) | (0.474, 0.121, 0.007) | (0.000, 0.218, 0.012) | (0.389, 0.104, 0.006) |
S2 | (0.790, 0.223, 0.007) | (0.000, 0.164, 0.009) | (1.000, 0.287, 0.016) | (0.000, 0.218, 0.012) | (0.611, 0.104, 0.006) |
S3 | (0.000, 0.361, 0.011) | (0.737, 0.134, 0.007) | (0.947, 0.266, 0.014) | (1.000, 0.164, 0.009) | (0.722, 0.132, 0.007) |
S4 | (0.947, 0.285, 0.009) | (1.000, 0.218, 0.012) | (0.526, 0.128, 0.007) | (0.895, 0.134, 0.007) | (0.000, 0.169, 0.009) |
S5 | (1.000, 0.308, 0.010) | (0.474, 0.101, 0.006) | (0.579, 0.144, 0.008) | (0.526, 0.101, 0.006) | (1.000, 0.213, 0.012) |
S6 | (0.210, 0.234, 0.007) | (0.947, 0.207, 0.011) | (0.000, 0.128, 0.007) | (0.895, 0.134, 0.007) | (0.611, 0.104, 0.006) |
(0.614, 0.275, 0.009) | (0.684, 0.177, 0.010) | (0.588, 0.192, 0.010) | (0.553, 0.167, 0.009) | (0.556, 0.144, 0.008) |
C1 | C2 | C3 | C4 | C5 | |
---|---|---|---|---|---|
S1 | 0.1893 | 0.2315 | 0.0394 | 0.6057 | 0.1252 |
S2 | 0.2299 | 0.6703 | 0.3123 | 0.6057 | 0.0971 |
S3 | 0.7019 | 0.0979 | 0.2818 | 0.4508 | 0.1794 |
S4 | 0.3230 | 0.2732 | 0.0061 | 0.3769 | 0.5820 |
S5 | 0.3523 | 0.1305 | 0.0415 | 0.0433 | 0.3712 |
S6 | 0.3607 | 0.2315 | 0.5203 | 0.3769 | 0.0971 |
C1 | C2 | C3 | C4 | C5 | |
---|---|---|---|---|---|
C1 | 1.0000 | 0.6160 | 0.7393 | 0.7865 | 0.7357 |
C2 | 0.6160 | 1.0000 | 0.6860 | 0.8766 | 0.5713 |
C3 | 0.7393 | 0.6860 | 1.0000 | 0.7275 | 0.3138 |
C4 | 0.7865 | 0.8766 | 0.7275 | 1.0000 | 0.5981 |
C5 | 0.7357 | 0.5713 | 0.3138 | 0.5981 | 1.0000 |
C1 | 0.4336 | 0.4866 | 0.1956 |
C2 | 0.3627 | 0.4534 | 0.1823 |
C3 | 0.3003 | 0.4605 | 0.1851 |
C4 | 0.4946 | 0.5001 | 0.2010 |
C5 | 0.3296 | 0.5870 | 0.2360 |
(0.614, 0.275, 0.009) | (0.684, 0.177, 0.010) | (0.588, 0.192, 0.010) | (0.553, 0.167, 0.009) | (0.556, 0.144, 0.008) |
C1 | C2 | C3 | C4 | C5 | |
---|---|---|---|---|---|
S1 | (0.200, 0.443, 0.014) | (0.385, 0.330, 0.018) | (0.000, 0.000, 0.000) | (0.000, 0.000, 0.000) | (0.000, 0.000, 0.000) |
S2 | (0.286, 0.452, 0.014) | (0.000, 0.000, 0.000) | (0.701, 0.450, 0.025) | (0.000, 0.000, 0.000) | (0.100, 0.238, 0.013) |
S3 | (0.000, 0.000, 0.000) | (0.077, 0.269, 0.015) | (0.612, 0.428, 0.023) | (0.809, 0.315, 0.017) | (0.300, 0.261, 0.014) |
S4 | (0.543, 0.506, 0.016) | (0.461, 0.339, 0.019) | (0.000, 0.000, 0.000) | (0.619, 0.289, 0.016) | (0.000, 0.000, 0.000) |
S5 | (0.629, 0.527, 0.017) | (0.000, 0.000, 0.000) | (0.000, 0.000, 0.000) | (0.000, 0.000, 0.000) | (0.800, 0.345, 0.019) |
S6 | (0.000, 0.000, 0.000) | (0.385, 0.330, 0.018) | (0.000, 0.000, 0.000) | (0.619, 0.289, 0.016) | (0.100, 0.238, 0.013) |
C1 | C2 | C3 | C4 | C5 | |
---|---|---|---|---|---|
S1 | (0.000, 0.000, 0.000) | (0.000, 0.000, 0.000) | (0.194, 0.296, 0.016) | (1.000, 0.369, 0.020) | (0.300, 0.238, 0.013) |
S2 | (0.000, 0.000, 0.000) | (1.000, 0.292, 0.016) | (0.000, 0.000, 0.000) | (1.000, 0.369, 0.020) | (0.000, 0.000, 0.000) |
S3 | (1.000, 0.579, 0.018) | (0.000, 0.000, 0.000) | (0.000, 0.000, 0.000) | (0.000, 0.000, 0.000) | (0.000, 0.000, 0.000) |
S4 | (0.000, 0.000, 0.000) | (0.000, 0.000, 0.000) | (0.104, 0.301, 0.016) | (0.000, 0.000, 0.000) | (1.000, 0.297, 0.016) |
S5 | (0.000, 0.000, 0.000) | (0.308, 0.247, 0.013) | (0.015, 0.313, 0.017) | (0.048, 0.263, 0.014) | (0.000, 0.000, 0.000) |
S6 | (0.657, 0.461, 0.014) | (0.000, 0.000, 0.000) | (1.000, 0.301, 0.016) | (0.000, 0.000, 0.000) | (0.000, 0.000, 0.000) |
S1 | (0.109, 0.241, 0.010) | (0.308, 0.239, 0.013) | (0.303, 0.402, 0.016) | (0.197, 0.386, 0.021) | (0.250, 0.394, 0.019) |
S2 | (0.209, 0.301, 0.014) | (0.383, 0.207, 0.011) | (0.580, 0.502, 0.023) | (0.000, 0.335, 0.018) | (0.290, 0.427, 0.021) |
S3 | (0.361, 0.288, 0.016) | (0.196, 0.256, 0.008) | (1.000, 0.480, 0.026) | (0.490, 0.414, 0.013) | (0.745, 0.448, 0.021) |
S4 | (0.315, 0.296, 0.013) | (0.255, 0.194, 0.011) | (0.872, 0.494, 0.021) | (0.334, 0.313, 0.017) | (0.603, 0.413, 0.019) |
S5 | (0.312, 0.287, 0.012) | (0.068, 0.208, 0.011) | (0.864, 0.478, 0.019) | (0.821, 0.336, 0.018) | (0.843, 0.413, 0.019) |
S6 | (0.218, 0.223, 0.012) | (0.314, 0.242, 0.010) | (0.605, 0.372, 0.020) | (0.182, 0.390, 0.015) | (0.393, 0.381, 0.018) |
S1 | S2 | S3 | S4 | S5 | S6 | Ranking | |
---|---|---|---|---|---|---|---|
n = 5000 | 0.181 | 0.204 | 0.529 | 0.425 | 0.599 | 0.278 | |
n = 10,000 | 0.179 | 0.203 | 0.526 | 0.426 | 0.597 | 0.277 | |
n = 50,000 | 0.177 | 0.205 | 0.526 | 0.426 | 0.595 | 0.278 | |
n = 100,000 | 0.177 | 0.205 | 0.527 | 0.425 | 0.597 | 0.279 |
Alter. | L-TOPSIS | F-VIKOR | PL-MABAC | PL-EDAS | C-TOPSIS | C-VIKOR | Proposed Method |
---|---|---|---|---|---|---|---|
S1 | 6 | 5 | 5 | 6 | 5 | 6 | 6 |
S2 | 5 | 6 | 6 | 4 | 6 | 4 | 5 |
S3 | 3 | 3 | 2 | 3 | 2 | 2 | 2 |
S4 | 2 | 2 | 3 | 2 | 3 | 3 | 3 |
S5 | 1 | 1 | 1 | 1 | 1 | 1 | 1 |
S6 | 4 | 4 | 4 | 5 | 4 | 5 | 4 |
MADM Models | L-TOPSIS | F-VIKOR | PL-MABAC | PL-EDAS | C-TOPSIS | C-VIKOR | Proposed Method |
---|---|---|---|---|---|---|---|
L-TOPSIS | 1.000 | 0.943 | 0.886 | 0.943 | 0.886 | 0.886 | 0.943 |
F-VIKOR | - | 1.000 | 0.943 | 0.829 | 0.943 | 0.771 | 0.886 |
PL-MABAC | - | - | 1.000 | 0.771 | 1.000 | 0.829 | 0.943 |
PL-EDAS | - | - | - | 1.000 | 0.771 | 0.943 | 0.886 |
C-TOPSIS | - | - | - | - | 1.000 | 0.829 | 0.943 |
C-VIKOR | - | - | - | - | - | 1.000 | 0.943 |
Proposed method | - | - | - | - | - | - | 1.000 |
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Li, T.; Sun, M. A Cloud Model-Based CRITIC-EDAS Decision-Making Approach with Linguistic Information for Marine Ranching Site Selection. Water 2024, 16, 688. https://doi.org/10.3390/w16050688
Li T, Sun M. A Cloud Model-Based CRITIC-EDAS Decision-Making Approach with Linguistic Information for Marine Ranching Site Selection. Water. 2024; 16(5):688. https://doi.org/10.3390/w16050688
Chicago/Turabian StyleLi, Tao, and Ming Sun. 2024. "A Cloud Model-Based CRITIC-EDAS Decision-Making Approach with Linguistic Information for Marine Ranching Site Selection" Water 16, no. 5: 688. https://doi.org/10.3390/w16050688
APA StyleLi, T., & Sun, M. (2024). A Cloud Model-Based CRITIC-EDAS Decision-Making Approach with Linguistic Information for Marine Ranching Site Selection. Water, 16(5), 688. https://doi.org/10.3390/w16050688