According to the analysis of the weight of the evaluation criteria by the AHP (Table 6), the environmental dimension is evaluated to be the most important (0.636), followed by economic (0.217) and social dimensions (0.147). Molinos-Senante et al. (2014) seemed the first to propose evaluation criteria for the social dimension in sustainability assessment, but its importance is lower than that of the environmental impact associated with large and old WWTPs, consistent with previous findings (Lizot et al. 2021).
Final weights of evaluation criteria
Dimension . | Weight . | Evaluation criteria . | Weight . | Final weight . | Rank . |
---|---|---|---|---|---|
Economic | 0.217 | Capital cost | 0.371 | 0.081 | 6 |
O&M cost | 0.629 | 0.137 | 2 | ||
Environmental | 0.636 | Improvement of biological reactors | 0.107 | 0.068 | 7 |
First flush treatment during the storm event | 0.090 | 0.057 | 8 | ||
Advanced treatment processes | 0.083 | 0.053 | 11 | ||
Odor impact | 0.128 | 0.082 | 5 | ||
Recycling possibility | 0.129 | 0.082 | 4 | ||
Sludge disposal | 0.269 | 0.171 | 1 | ||
Energy independence | 0.194 | 0.123 | 3 | ||
Social | 0.147 | Effective land use | 0.365 | 0.054 | 10 |
Public acceptance | 0.366 | 0.054 | 9 | ||
Willingness to pay tariff | 0.269 | 0.040 | 12 |
Dimension . | Weight . | Evaluation criteria . | Weight . | Final weight . | Rank . |
---|---|---|---|---|---|
Economic | 0.217 | Capital cost | 0.371 | 0.081 | 6 |
O&M cost | 0.629 | 0.137 | 2 | ||
Environmental | 0.636 | Improvement of biological reactors | 0.107 | 0.068 | 7 |
First flush treatment during the storm event | 0.090 | 0.057 | 8 | ||
Advanced treatment processes | 0.083 | 0.053 | 11 | ||
Odor impact | 0.128 | 0.082 | 5 | ||
Recycling possibility | 0.129 | 0.082 | 4 | ||
Sludge disposal | 0.269 | 0.171 | 1 | ||
Energy independence | 0.194 | 0.123 | 3 | ||
Social | 0.147 | Effective land use | 0.365 | 0.054 | 10 |
Public acceptance | 0.366 | 0.054 | 9 | ||
Willingness to pay tariff | 0.269 | 0.040 | 12 |