Multi-Objective Optimization of Municipal Solid Waste Collection Based on Adaptive Large Neighborhood Search
Abstract
:1. Introduction
1.1. Background
1.2. Literature Review
1.3. Contributions
- A multi-objective optimization model was developed to balance the costs and workload variations among employees involved in the vehicle collection process. Previous VRP models usually aim to minimize the cost and ignore differences in employee workload. However, when the cost is optimal, there may be significant differences between different routes. Neglecting these differences can lead to psychological imbalance among employees. Balancing workload differences can improve employee satisfaction and overall work efficiency.
- A multi-objective adaptive large neighborhood search algorithm based on the ALNS algorithm was designed. The MOALNS algorithm tackles the multi-objective problem in the proposed model by integrating balance removal and balance insertion heuristic strategies.
- To evaluate the effectiveness of the proposed MOALNS algorithm, test cases based on realistic models were designed and compared with four multi-objective algorithms. The results indicate that the MOALNS algorithm exhibits a distinct advantage within this model.
1.4. Paper Organization
2. Modeling and Analysis
2.1. Problem Description
- During the collection process, vehicles visit each collection site only once;
- After completing the collection, vehicles must return to their originating depot;
- Each collection route is serviced by only one vehicle, and the capacity of the vehicles is limited.
2.2. Notations
2.3. Mathematical Model
2.3.1. Objective Functions
- Fixed CostsThe fixed vehicle cost includes expenses related to vehicle operation, such as insurance, taxes and employee wages. The total fixed cost for all vehicles in the model can be calculated using the following formula:
- Variable CostsVariable costs include expenses related to fuel consumption and carbon emissions incurred during transportation between different nodes. The fuel consumption from node i to node j can be calculated using the fuel consumption model proposed by Xiao et al. [39], as follows:The total fuel consumption cost can be calculated by
- Carbon Emission CostsWith global climate change receiving increasing attention, carbon emissions have become a major concern. The most widely adopted method for the management of carbon emissions is the implementation of a carbon tax. The calculation for the carbon tax is outlined below:
- Workload VariationsIn addition to optimizing the costs, it is essential to balance the workload across different routes. Balancing the workload among vehicles helps to ensure that employees feel that they are treated equitably. Workload disparities are measured using the variance in driving times and the variance in vehicle loads.
2.3.2. Model Formulated
3. Proposed Algorithm
3.1. Basic ALNS
Algorithm 1 SAAcceptanceCriteria |
Input: Current solution S, new solution , temperature T Output: Accepted solution Compute if then Accept as the new solution else Generate a random number if then Accept as the new solution else Reject and keep S as the current solution end if end if |
Algorithm 2 Basic ALNS |
|
3.2. MOALNS
3.2.1. Balance Remove
3.2.2. Balance Insert
3.2.3. Score Adjustment Method
3.2.4. Acceptance Criteria
Algorithm 3 MOALNS |
|
4. Computational Experiments
4.1. Performance Indicator
4.2. Sensitivity Analysis of Scoring Strategies
4.3. Complexity Analysis
4.4. Experiments on the Test Dataset
4.5. Experiments on a Real Case
4.6. Decision-Making in Real Case
5. Conclusions
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
References
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Notation | Explanation |
---|---|
Set of depot points | |
Set of waste sites | |
Set of vehicles | |
The depot point to which vehicle k belongs, | |
The set of points accessible to vehicle k, | |
Distance between node i and node j () | |
Load transported from node i to node j () | |
Fuel consumption rate when the vehicle is unloaded (L/km) | |
Fuel consumption rate when the vehicle is fully loaded (L/km) | |
Q | Maximum load capacity of a vehicle (t) |
Fuel consumption between node i and node j (L) | |
Carbon emissions factor | |
Carbon tax price (CNY/kg) | |
Fixed cost per vehicle (CNY) | |
Fuel price per unit (CNY/L) | |
Total fixed cost for all vehicles (CNY) | |
Total fuel cost (CNY) | |
Total carbon tax cost (CNY) | |
Distance vector; represents the route length of the i-th vehicle (km) | |
Load vector; represents the total load of the i-th vehicle (t) | |
Parameter | Description |
---|---|
The selected remove–insert operation resulted in a new global best solution. | |
The selected remove–insert operation resulted in an unaccepted solution, and the cost of this solution is better than the current solution. | |
The selected remove–insert operation resulted in a solution that has not been accepted before. The cost of this new solution is worse than the current one, but it is still accepted. |
Parameter | Description |
---|---|
The chosen remove–insert operation resulted in a solution that dominates the solutions in the Pareto optimal set. | |
The chosen remove–insert operation resulted in a non-dominated solution. | |
The chosen remove–insert operation resulted in a previously unaccepted solution, but this solution is dominated by solutions in the Pareto optimal set. |
Instance | Parameter | |||
---|---|---|---|---|
[25, 5, 1] | [25, 5, 0] | [25, 50, 1] | [25, 10, 1] | |
P-n23-k8 | 0.754 (0.139) | 0.694 (0.136) | 0.672 (0.175) | 0.771 (0.084) |
P-n101-k4 | 0.743 (0.187) | 0.681 (0.166) | 0.663 (0.229) | 0.702 (0.200) |
X-n237-k14 | 0.626 (0.082) | 0.548 (0.101) | 0.513 (0.075) | 0.543 (0.107) |
X-n367-k17 | 0.763 (0.171) | 0.775 (0.155) | 0.573 (0.154) | 0.630 (0.089) |
X-n401-k29 | 0.754 (0.078) | 0.678 (0.187) | 0.701 (0.152) | 0.715 (0.132) |
Instance | NSGA-II | MOEA/D | UNSGA-III | Multi-GPO | MOALNS | Best Solution | BKS |
---|---|---|---|---|---|---|---|
P-n23-k8 | 0.905 (0.099) + | 0.575 (0.221) ≈ | 0.862 (0.108) + | 0.821 (0.083) + | 0.417 (0.165) | 346.5 | 529 |
P-n40-k5 | 0.792 (0.120) − | 0.569 (0.130) − | 0.743 (0.064) − | 0.768 (0.038) ≈ | 0.827 (0.048) | 403.7 | 458 |
P-n45-k5 | 0.633 (0.138) − | 0.458 (0.127) − | 0.787 (0.066) − | 0.765 (0.064) − | 0.922 (0.038) | 482.4 | 510 |
P-n50-k7 | 0.651 (0.084) − | 0.488 (0.105) − | 0.789 (0.090) − | 0.775 (0.053) − | 0.902 (0.042) | 515.1 | 554 |
P-n50-k8 | 0.723 (0.093) − | 0.600 (0.060) − | 0.762 (0.067) − | 0.858 (0.058) ≈ | 0.897 (0.062) | 613.2 | 631 |
P-n50-k10 | 0.767 (0.054) − | 0.589 (0.072) − | 0.750 (0.096) − | 0.828 (0.055) − | 0.902 (0.083) | 659.1 | 696 |
P-n51-k10 | 0.743 (0.059) − | 0.508 (0.049) − | 0.727 (0.063) − | 0.732 (0.074) − | 0.825 (0.068) | 682.8 | 741 |
P-n55-k7 | 0.734 (0.072) − | 0.605 (0.083) − | 0.659 (0.163) − | 0.748 (0.060) − | 0.938 (0.029) | 537.2 | 568 |
P-n55-k15 | 0.752 (0.057) − | 0.454 (0.102) − | 0.783 (0.153) ≈ | 0.781 (0.140) ≈ | 0.798 (0.132) | 831.8 | 989 |
P-n60-k10 | 0.672 (0.088) − | 0.437 (0.097) − | 0.807 (0.077) ≈ | 0.838 (0.076) ≈ | 0.829 (0.089) | 705.5 | 744 |
P-n65-k10 | 0.640 (0.130) − | 0.495 (0.123) − | 0.651 (0.090) − | 0.689 (0.130) − | 0.902 (0.042) | 750.9 | 792 |
P-n70-k10 | 0.656 (0.072) − | 0.556 (0.103) − | 0.705 (0.077) − | 0.752 (0.116) − | 0.897 (0.075) | 797.4 | 827 |
P-n76-k5 | 0.729 (0.082) − | 0.642 (0.074) − | 0.740 (0.096) − | 0.827 (0.103) − | 0.947 (0.038) | 590.9 | 627 |
P-n101-k4 | 0.420 (0.097) − | 0.259 (0.114) − | 0.347 (0.083) − | 0.518 (0.125) − | 0.956 (0.023) | 616.3 | 681 |
A-n32-k5 | 0.851 (0.044) ≈ | 0.623 (0.082) − | 0.844 (0.051) ≈ | 0.867 (0.059) ≈ | 0.842 (0.062) | 648.5 | 784 |
A-n39-k6 | 0.758 (0.112) − | 0.514 (0.124) − | 0.824 (0.093) − | 0.841 (0.102) − | 0.916 (0.027) | 787.3 | 831 |
A-n44-k6 | 0.775 (0.120) − | 0.452 (0.165) − | 0.801 (0.081) − | 0.814 (0.092) − | 0.926 (0.049) | 858.8 | 937 |
A-n46-k7 | 0.724 (0.114) − | 0.490 (0.098) − | 0.784 (0.103) − | 0.733 (0.129) − | 0.858 (0.075) | 874.7 | 914 |
A-n48-k7 | 0.745 (0.069) − | 0.479 (0.119) − | 0.755 (0.074) − | 0.774 (0.088) − | 0.901 (0.055) | 831.9 | 1073 |
A-n55-k9 | 0.702 (0.056) − | 0.479 (0.126) − | 0.781 (0.089) − | 0.745 (0.082) − | 0.912 (0.084) | 935.8 | 1073 |
A-n60-k9 | 0.737 (0.089) − | 0.608 (0.082) − | 0.763 (0.078) − | 0.734 (0.101) − | 0.922 (0.035) | 1022 | 1354 |
A-n61-k9 | 0.683 (0.068) − | 0.501 (0.092) − | 0.736 (0.104) − | 0.764 (0.102) − | 0.871 (0.104) | 883.7 | 1034 |
A-n62-k8 | 0.651 (0.102) − | 0.504 (0.113) − | 0.673 (0.095) − | 0.687 (0.084) − | 0.875 (0.084) | 899.7 | 1288 |
A-n63-k9 | 0.720 (0.076) − | 0.495 (0.153) − | 0.774 (0.061) − | 0.748 (0.068) − | 0.924 (0.043) | 996.9 | 1616 |
A-n63-k10 | 0.657 (0.069) − | 0.436 (0.114) − | 0.653 (0.095) − | 0.588 (0.078) − | 0.834 (0.059) | 1015.7 | 1314 |
A-n64-k9 | 0.690 (0.085) − | 0.551 (0.121) − | 0.728 (0.081) − | 0.739 (0.101) − | 0.923 (0.063) | 1021 | 1401 |
A-n65-k9 | 0.659 (0.068) − | 0.483 (0.118) − | 0.737 (0.068) − | 0.722 (0.064) − | 0.905 (0.083) | 1028 | 1174 |
A-n69-k9 | 0.661 (0.076) − | 0.517 (0.111) − | 0.711 (0.101) − | 0.669 (0.096) − | 0.934 (0.072) | 968.1 | 1159 |
A-n80-k10 | 0.576 (0.065) − | 0.432 (0.147) − | 0.631 (0.081) − | 0.645 (0.086) − | 0.875 (0.053) | 1204 | 1763 |
X-n106-k14 | 0.602 (0.140) − | 0.401 (0.073) − | 0.658 (0.074) − | 0.683 (0.104) − | 0.797 (0.090) | 9960.8 | 26,362 |
X-n125-k30 | 0.681 (0.089) − | 0.430 (0.065) − | 0.697 (0.072) − | 0.666 (0.102) − | 0.781 (0.059) | 18,475.3 | 55,539 |
X-n134-k13 | 0.517 (0.083) − | 0.534 (0.084) − | 0.557 (0.077) − | 0.479 (0.073) − | 0.912 (0.037) | 7498.5 | 10,916 |
X-n148-k46 | 0.528 (0.080) − | 0.167 (0.070) − | 0.563 (0.116) − | 0.517 (0.121) − | 0.894 (0.063) | 21,804.1 | 43,448 |
X-n153-k22 | 0.576 (0.090) − | 0.294 (0.190) − | 0.638 (0.096) − | 0.609 (0.102) − | 0.731 (0.061) | 12,155.7 | 21,220 |
X-n162-k11 | 0.535 (0.095) − | 0.608 (0.073) − | 0.385 (0.186) − | 0.513 (0.084) − | 0.790 (0.044) | 11,959.1 | 14,138 |
X-n181-k23 | 0.561 (0.079) − | 0.494 (0.083) − | 0.536 (0.088) − | 0.627 (0.085) − | 0.929 (0.023) | 12,595.7 | 24,145 |
X-n200-k36 | 0.451 (0.049) − | 0.403 (0.092) − | 0.543 (0.089) − | 0.580 (0.074) − | 0.805 (0.082) | 26,108.8 | 58,578 |
X-n204-k19 | 0.474 (0.067) − | 0.364 (0.150) − | 0.492 (0.042) − | 0.439 (0.061) − | 0.761 (0.106) | 17,997.6 | 19,565 |
+/−/≈ | 1/36/1 | 0/37/1 | 1/34/3 | 1/32/5 |
Type of Waste | NSGA-II | MOEAD | UNSGA-III | AGE-MOEA2 | MOALNS |
---|---|---|---|---|---|
Recyclable waste | 0.632 (0.091) − | 0.501 (0.083) − | 0.620 (0.096) − | 0.609 (0.103) − | 0.743 (0.129) |
Kitchen waste | 0.548 (0.141) − | 0.363 (0.118) − | 0.621 (0.091) ≈ | 0.669 (0.128) ≈ | 0.652 (0.914) |
Other types of waste | 0.455 (0.071) − | 0.362 (0.086) − | 0.481 (0.814) − | 0.504 (0.719) − | 0.975 (0.028) |
+/−/≈ | 0/3/0 | 0/3/0 | 0/2/1 | 0/2/1 |
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Li, W.; Wang, P.; Xu, Y.; Pan, L.; Nie, C.; Yang, B. Multi-Objective Optimization of Municipal Solid Waste Collection Based on Adaptive Large Neighborhood Search. Electronics 2025, 14, 103. https://doi.org/10.3390/electronics14010103
Li W, Wang P, Xu Y, Pan L, Nie C, Yang B. Multi-Objective Optimization of Municipal Solid Waste Collection Based on Adaptive Large Neighborhood Search. Electronics. 2025; 14(1):103. https://doi.org/10.3390/electronics14010103
Chicago/Turabian StyleLi, Wenbin, Peiyang Wang, Yunsheng Xu, Li Pan, Chuhui Nie, and Bo Yang. 2025. "Multi-Objective Optimization of Municipal Solid Waste Collection Based on Adaptive Large Neighborhood Search" Electronics 14, no. 1: 103. https://doi.org/10.3390/electronics14010103
APA StyleLi, W., Wang, P., Xu, Y., Pan, L., Nie, C., & Yang, B. (2025). Multi-Objective Optimization of Municipal Solid Waste Collection Based on Adaptive Large Neighborhood Search. Electronics, 14(1), 103. https://doi.org/10.3390/electronics14010103