1. Introduction
The race toward mass industrialization that our society is currently experiencing and the great trend toward unbridled consumption are the main causes of the great climate change that we are undergoing. This significant change generates more frequent natural disasters that cause disruptions in the supply chain. Greenhouse gas (GHG) emissions caused by human activities are the main cause of this climate change, and as populations, economies, and living standards increase, the cumulative level of greenhouse gas emissions also increases. Moreover, recent researches show that also many consumers have low-carbon preferences [1].
The most abundant GHG is carbon dioxide CO2, which is largely produced by the burning of fossil fuels, especially in logistics activities. In this context, the collaboration between supply chains has become essential. This collaboration improves the manager’s visibility and makes it easier to decide on the transport strategy to adopt in order to minimize the CO2 emissions of his supply chain [2,3].
Supply chain transportation pooling strategy (SCTPS) is one of the innovative supply chain collaboration strategies. This concept goes much further than the simple idea of grouping vehicles, which is quite common in the professional world. It is essentially based on a partnership agreement that consists of voluntarily pooling and sharing resources (infrastructure, vehicles, etc.) and information from several supply chains with the aim of achieving a particular level of performance or gains [4]. Initially, the only opportunities perceived by supply chain managers in the concept of logistics resource pooling were purely economic. However, new and stricter ecology legislation has led them to consider the concept of combining logistics resources for environmental purposes, such as reducing CO2 emissions [5,6].
1.1. Literature Overview
One of the main concepts for improving the sustainability of supply chains is the collaboration between stakeholders by increasing the efficiency of their shared resources [7,8,9,10]. There are two types of collaboration: vertical collaboration and horizontal collaboration. Vertical collaboration involves cooperation between stakeholders in the same supply chain, while horizontal collaboration includes cooperation between companies at the same level that can provide the same goods or services within a supply chain [11,12]. In the literature, there is a large amount of research related to vertical collaboration in the logistics industry [9,10,11]. However, horizontal collaboration such as shared freight carrier and freight consolidation has not received the same degree of attention [7,8,13], etc.
Over time, the concept of pooling logistics has been increasingly developed in the literature. Several research works are in line with collaboration approaches. Tuzkaya and nüt [14] addressed the problem of designing collaborative warehouses and transport networks through linear programming. The principal objective of their research was to determine the best strategy to distribute products from suppliers to a clustering hub and from this clustering hub to manufacturers. They looked at various constraints related to supplier and hub capacities, starting stock and backlog levels, transportation times, manufacturers’ demands, etc. The results of the linear programming model were compared for different scenarios. Further analyses were then performed by the authors to measure the sensitivity of the model results for different parameter values.
Ballot and Fontane [13] used an already optimized supply chain of a French distribution chain to study the possibility of further improving its performance using the logistic pooling strategy. The objective of the authors was to reduce the environmental impact of the supply chain by reducing transport emissions. The authors estimated CO2 emissions from different empirical models of supply-pooling network strategies. The results showed a reduction in CO2 emissions of about 25% with the new organizations. Qiu and Huang [15] study the pooling hub capacity across several supply chains using mathematical models and assess the impact of demand uncertainty on their financial performance measures. Two mathematical models were formulated for the studied supply chains. The first one does not consider the pooling hub, and the second one considers a pooling one. Therefore, the authors conducted different experiments to examine the clustering under different demand models and variances. The results show that the benefits of pooling hub capacity depend on the demand model. The results also indicate that demand variance can significantly influence the effect of central capacity pooling in terms of total supply chain costs. Leitner et al. [16] designed a centralized supply chain for automotive suppliers in Romania and Spain to reduce the cost of supply, CO2 emissions, and increase transportation efficiency. The results of this study showed that the grouping of transport operations by the different partners generated a significant reduction in the number of trips, fuel consumption, and CO2 emissions, in addition to transport costs.
Moutaoukil et al. [17] presented a pooling logistics model that takes into account the specificities of the agricultural and food supply chain flows. This model integrates the economic, environmental, and societal dimensions of the sustainable development objective. After identifying the different possible scenarios, the authors have shown the practical use of their proposal through the modeling of a particular scenario using a simulation technique to analyze the minimization of the total transport cost, the system’s CO2 emissions, and the risk of accidents per million kilometers travelled by transporters. Pan et al. [18] explored the effect of combining supply chains on their CO2 emissions with road and rail transport. They developed an optimization model with a piecewise linear objective function to assess quantitatively the impact of the products’ flows pooling on supply chains CO2 emission. This model was then tested with real data for 12 weeks in a large distribution network composed of the supply chains of two French retailers. The overall results show a 14% reduction in CO2 emissions with road transport and 52% with joint road and rail transport. Montoya-Torres et al. [19] conducted a case study through real data from the city of Bogotá, Colombia, for three companies in which each company has its own stores. They used mathematical modeling to compare the collaborative to the corresponding non-collaborative scenarios in terms of travel distance. In the non-collaborative scenario, each firm distributes goods to its own stores. While in the collaborative scenario the stores of the three companies are allocated to one of the three companies, serving as a pooling hub, and then routing is performed for each new allocation. On the basis of the obtained travel distances, the authors evaluated the travel time and carbon emission. The results highlight the quantitative benefits that can be obtained when pooling logistics operations are implemented, represented in both transportation costs and environmental impacts.
Ouhader and El kyal [7] tried to quantify the potential environmental and economic benefits of horizontal collaboration in transportation. Therefore, they studied the sensitivity between CO2 emissions and transportation costs through an approach based on bi-objective mathematical modeling to minimize both the total transportation cost and the total environmental effect by simultaneously combining the location and routing decisions of the facility in urban freight distribution. The results of a noncollaboration scenario with the corresponding collaboration one showed that collaboration leads to a reduction in CO2 emissions, transport costs, and distances traveled, in addition to the improvement of the vehicle load rate.
Habibi et al. [20] studied the problem of pooled hub location in the context of collaborative distribution network design in supply chains. The authors used two distribution networks of different supply chains to determine the best locations of the hubs that optimally serve their customers. Based on three collaborative cases and four cost-sharing strategies, the authors were able to verify whether collaboration offers a better decision and how to share the total cost between each supply chain to achieve a cost-effective solution.
Mrabti et al. [21] proposed a generic model of a pooled supply chain using discrete events simulation to assess economic indicators such as logistics cost, vehicles filling rate, and the environmental indicators CO2 emissions. The authors then addressed a case study to examine the performance of the pooled supply chain strategy. This strategy was shown to reduce logistics cost, improve vehicle fill rate, and reduce CO2 emissions.
Zouari [22] analyzed seven scenarios of logistic integration among a set of three companies in urban and interurban distribution. The main objective of this research was to choose the optimal path by showing the challenges and opportunities of pooling logistics. This resulted in reductions in transportation costs, congestion, and GHG emissions.
El Bouazzaoui et al. [23] discussed the concepts of transport and storage pooling in the Moroccan hydrocarbon supply chain. They studied the environmental impact of the pooling of resources used by the consolidation of transport trucks and storage tanks on the reduction of CO2 emissions from different trucks from two companies. Based on real data of petroleum product flows over seven years from two major importers before and after resources pooling simulation models were developed to determine CO2 emissions variation rates. The simulation results showed about 46% of the minimization of CO2 emissions.
Gallardo et al. [24] applied an interdisciplinary transition innovation, management, and engineering methodology to the conceptualization, redesign, and redevelopment of the existing freight systems to achieve a downshift in CO2 emissions.
In the literature, some research has studied CO2 emission using simulation techniques in other areas. For instance, Sopha et al. [25] developed an integrated approach based on agent-based modeling and DES to evaluate CO2 emission to decide between the existing evacuation plan for the Mount Merapi volcano eruption. Li and Lei [26] and Limsawasd and Athigakunagorn [27] applied DES in estimating and analyzing CO2 emission construction engineering projects.
Moreover, in the literature, collaboration in supply chain have two types of benefits: economic benefits and environmental aspects benefits. A recent example of research is Gansterer et al. [9], which found that cost savings of 20–30% were made by carrier collaboration. The reduction in vehicle kilometers is demonstrated as a component of cost savings. However, Gansterer et al. [9] have not quantified explicitly the CO2 emissions and the environmental aspect is not considered. In other examples [13,14,15,16,17,18,19,20,21,22,23,24,25,26,27,28], the GHG emissions is explicitly studied as benefits of supply chain collaboration.
1.2. Objectives and Contributions of the Study
Based on the literature review, this research starts from two major assertions. First, the majority of previous research in supply chain transportation pooling strategy (SCTPS), which can also be named freight consolidation, have studied the impact of only one type of SCTPS on the supply chain performances. Second, most of the previous research is related to vertical collaboration in the supply chain and rarely to horizontal collaboration. To fil this gap, the present research is about analyzing the effect of various SCTPS to reduce CO2 emissions using discrete event simulation (DES). In fact, the studied problem of SCTPS design considers both vertical and horizontal collaboration.
The studied supply chain is a network between two manufacturing companies and three customers and its suppliers to produce and distribute four product types. Five SCPS are studied and include the following: (1) non-pooling strategy; (2) multi-pick strategy; (3) multi-drop strategy; (4) central hub strategy; and (5) combined hub and multi-drop strategy. For each studied strategy, a three-step approach is applied. First, a simulation model for the strategy is developed using Siman/Arena software. Second, the verification and validation of the simulation model are based on the Pearson correlation test between CO2 emissions and the mean delivery time of each customer and between the mean delivery time of each pair of customers. Third, one-way analysis of variance (ANOVA) and Games-Howell simultaneous confidence intervals are used to interpret simulation results. The main result of the study, which will be obtained in the end, is that all SCTPSs significantly reduce CO2 emissions compared to the non-pooled supply chain.
2. Materials and Methods
2.1. The Applied Approach
The flowchart of the applied approach in this research is presented in Figure 1. To prepare the simulation model of each strategy, three inputs must be prepared. First, all supply chain transportation pooling strategies are described and provided in Section 2.2. Second, the studied supply chains network and parameters are presented in Section 2.3. Third, the formulation of the CO2 emissions indicator is provided in Section 2.4. After the models’ verification and validation, which are provided in Section 3.1, some of the studied strategy can be excluded from the comparative analysis. This step of verification and validation of the simulation models are based on the Pearson correlation test between CO2 emissions and the mean delivery time of each customer and between the mean delivery time of each pair of customers. The statistical analysis of the simulation results is provided in Section 3.2. One-way analysis of variance (ANOVA) and simultaneous Games-Howell confidence intervals are used to interpret simulation results. Finally, the selection of the best pooling strategy is provided in Section 3.3.
2.2. Supply Chains Transportation Pooling Strategies
Many definitions of transportation pooling exist. However, they all maintain that it is a partnership agreement between multiple actors that consists of the voluntary pooling of physical resources, information, and skills with the aim of obtaining economic, ecological, and financial collective benefits that they could not produce individually. The framework of this cooperation can take different organizational forms depending on the nature of the parties, the means, and the products or services.
2.2.1. Supply Chains with a Multi-Pick Pooling Strategy (Pick-Up Round)
This strategy involves consolidating supplies destined for the same delivery site (customer) from multiple shipping locations (suppliers). Therefore, orders intended for the same customer from multiple suppliers must be grouped through a pickup round performed by one or more vehicles [29]. Figure 2 presents a conceptual supply chain with multi-pick.
2.2.2. Supply Chains with Multi-Drop Pooling Strategy (Distribution Round)
Multi-drop strategy is based on the same logic as multi-pick, except that the consolidating starts from a single shipping location and goes to multiple delivery sites. One or more vehicles leave from the same supplier to transport different orders and deliver them successively to several customers through a distribution round. These customers are geographically close or are on the same transport line [29,30]. Figure 3 presents a conceptual supply chain with multi-drop.
2.2.3. Supply Chains with Pooling Hub Strategy
One or more shared intermediary hubs are integrated into the supply chain structure. Deliveries are then made in two stages, with suppliers routing their products to the shared hub, and when a customer sends them their delivery requirements, they send the order to the shared hub to make the delivery. Incorporating the hub into the supply chain structure increases the size of shipments and improves transportation costs by increasing vehicle fill rates [31]. Figure 4 presents a conceptual supply chain with central hub.
2.2.4. Supply Chains with Pooling Hub and Multi-Drop Delivery Strategy
This strategy is a combination of the two previous pooling strategies. Deliveries upstream of the hub follow the same form. However, deliveries downstream of the hub are made using the multi-drop technique. Therefore, these deliveries are made by distribution rounds between the pooling hub and the customers [30,31]. Figure 5 presents a conceptual supply chain with combined hub and multiple drops.
Five strategies are studied in this work, as presented in Table 1.
2.3. Supply Chain Network and Parameters
This study adopts a pooled supply chain composed of two companies and three customers. Companies feed the supply chain with products according to statistical distributions, which are summarized in Table 2. Every customer submits a delivery order to both companies at different times. These order times and the corresponding quantity of pallets for each type of product follows discrete distributions (Table 3). All the distances between the components of the supply chain are defined in kilometers in Table 4. The average speeds of the delivery vehicles are defined according to the location of the shipment and destination. In the case of long distances, the average speed of the vehicle has been set at 80 km per hour. For small and medium distances, speeds have been reduced to 40 km per hour (Table 4). The choice of vehicles’ load was based according to the French Environment and Energy Management Agency (ADEME) [32,33]. The chosen vehicle is a 12-tonne Gross Vehicle Weight Rating (GVWR) truck. The maximum loading capacity was limited to 6 tons due to pallet volume constraints. Each company has two trucks in its fleet. These trucks are then distributed between the companies and the pooling hub in the case of the pooled supply chains with hub models. Therefore, in these models, the companies operate one truck in common to deliver their pallets to the pooling hub. The other three trucks are assigned to the pooling hub for deliveries to customers.
2.4. Formulation of the CO2 Emissions Indicator
Tundys and Winiewski [34] affirmed that the important element to reduce the negative environmental impact of chains is a well-thought-out relationship with suppliers, a well-chosen and adapted logistics infrastructure, including means of transport. In this research, only the CO2 emissions related to the transport means is considered. Other sources of CO2 emissions related to product manufacturing, storage, etc., are not considered because it is assumed to be the same for all studied pooling strategies.
Moreover, in the literature there are two main methods used to estimate supply chain emissions: the spend-based method and the activity-based method [35]. The spend-based method is not used because it takes the financial value of an equipment and multiplies it by an emission factor. Then, the method used in this research is the activity-based method.
For the formulation of the emissions indicator of CO2, the works of Mrabti et al. [36,37] were used as a basis. These emissions depend on the weight of the transported load, the capacity of the vehicle, and the travelled distance. Hence, the formulas for estimating CO2 emissions for a delivery are presented in Equations (1) and (2):
Eloaded = Dij × [Eempty + (Efull − Eempty) × X],(1)
Eunloded = Dij × Eempty,(2)
With
Eloaded: The total CO2 emission of a loaded vehicle, in KgCO2, between nodes i and j.
Eunloaded: The total CO2 emission of an unloaded vehicle, in KgCO2, between nodes i and j.
Dij: The distance, in kilometers, between nodes i and j.
Eempty: The CO2 emission rate, in KgCO2/Km, of an empty vehicle.
Efull: The CO2 emission rate, in KgCO2/Km, of a full loaded vehicle.
X: The ratio between weight of the load of merchandise and the maximum payload of the vehicle.
The CO2 emission rates of empty and fully loaded vehicles, Eempty and Efull, are related to the vehicle speed as follow [37]:
Eempty = K+ a × v + b × v2 + c × v3 + d/v + e/v2 + f/v3,(3)
Efull = Eempty × Cload(v),(4)
Cload(v) = k + r × v + s × v2 + t × v3 + u/v,(5)
With
v: The vehicle speed
K and k: Constants determined according to the Gross Vehicle Weight Rating (GVWR).
a, b, c, d, e, f, r, s, t, u: Coefficients determined according to the vehicle GVWR.
Cload: The load correction factor
Based on the GVWR of the truck and the Equations (3) and (4), the values of full and empty emission rates are estimated [37,38]. The values obtained are Eempty = 0.48 KgCO2/km and Efull = 0.58 Kg CO2/km for the 40 km/hour speed and Eempty = 0.51 KgCO2/km and Efull = 0.58 KgCO2/km for the 80 km/hour speed. An average load capacity of 9.79 tons was adopted for each truck [32]
2.5. Simulation Models
All simulation models are developed using the Arena 14.0 commercial simulation software. This tool integrates all the functions needed for simulation including animation, analysis of input, and output data. The simulation model of the non-pooled supply chain is fully detailed in the next subsection. However, the others simulation models of the pooled strategies can be founded in the supplementary file.
2.5.1. Non-Pooled Supply Chain Model
The structure of the non-pooled supply chain model is composed of two parts: companies and customers. The first part contains two sub-models, each corresponding to one company. The second part contains three sub-models each corresponding to a customer (Figure 6).
Every company sub-model is composed of the three sections “Company i: order preparation”, “Company i: customer assignment”, and “Company i: loading docks” (Figure 7). The first section “Company i: order preparation” acts as a generator of pallets of products and manages the order preparation. Every company produces two types of products for which as many “Create” modules are lined up. Each pallet of products is placed on hold in a storage area materialized by a “Hold” module waiting for an order from customers. In this case, the corresponding customer sends a signal to the appropriate “Hold” module to release the necessary number of pallets. These pallets pass through a “Decide” module to check whether their number matches the loading capacity of the transport vehicles. If this variable is greater than or equal to the vehicle loading capacity, pallets corresponding to this capacity are grouped into a full load by the module “Volume load preparation company” “Batch”. This load passes then through an “Assign” module where it receives different attributes and variables referring to the load size and the order size. The order size variable is then reduced by the number of pallets already grouped. In contrast, if the load matching condition is not verified, all the pallets are sent to the “Partial load preparation company i” “Batch” module. But before, a variable referring to the remaining part of the order is incremented by passing these pallets through the “Assign” module named “Remaining load company i”. Next, this load passes through other “Assign” modules to receive the new value of the load size attribute and reset all the other variables.
In the second section “Company i: Customer Assignment”, each delivery is assigned to the corresponding customer through a “Decision” module. This module is connected to three “Assign” modules, each corresponding to one customer. In these modules, necessary attributes, such as order number, the number of pallets, and the delivery sequence, are assigned to each delivery before it is loaded into a vehicle. The stations that make up each of the delivery sequences are previously defined in the “sequence” modules.
Each delivery is made to wait in the queue of a “Request” module for the nearest free vehicle in the third section named “Company i: Loading docks”. This vehicle collects the shipment from the station “Company I” and passes to the “Transport” module, where the speed of the trip is defined, to be finally sent to its corresponding customer.
As for the company sub-model, each customer “j” sub-model comprises three sections named “Customer j: order generation and management”, “Customer j: unloading dock”, and “Customer j: order reception” (Figure 8).
In the “Customer j: order generation and management” section a “Create” module generates delivery orders. These orders are duplicated according to the number of companies through a “Separate” module called “Duplication order customer j”. Each copy of this order is then transferred to an “Assign” module. Each of these modules will increment the number of orders and assign the value of ordered pallet number per type of product to the order. Then, every order goes through a “Decide” module, named “Storage Company i Customer j” to verify the availability of the pallet in the storage of the companies. If availability is verified, the order is validated and goes through a “Signal” module to send a signal to the corresponding company to release the requested number of pallets. If the storage availability is not verified, the order will be cancelled for unavailable storage and will be filed in a “Dispose” module.
Each vehicle, entering the section “Customer j: loading docks”, is sent to the “Free” module. This module frees the vehicles from their loads, which are forwarded to “Record” modules. The first one is used to store the total number of delivered pallets, while the second one is used to calculate CO2 emissions rate.
In the section “Customer j: order reception”, each delivered load is split into individual pallets by a “Separate” module. These pallets are sent to a “Batch” module, whose function is to group all the pallets of each order. Once all the ordered pallets are regrouped, a “Match” module matches them with the corresponding order. To validate the reception of the order, the matched informational (order) and physical (pallets) flows are grouped together by a “Batch” module and removed from the system via a “Dispose” module.
2.5.2. Pooled Supply Chains with Multi-Pick Model
This simulation model has the same structure as the non-pooled simulation model, except for the companies’ sub-models. Indeed, a new section, which manages the flow of multi-pick deliveries, appears in these sub-models. Moreover, each company sub-model has a different structure from the other. For more details about this simulation model, the reader can consult Figure S1 in the Supplementary Material.
2.5.3. Pooled Supply Chains with Multi-Drop Model
In this simulation model, each company must manage the joint delivery of several parts to different customers. For this purpose, a new section named “Company i: multi-drop management” appears in each company sub-model. In addition, the customers must manage the reception of their corresponding partial loads of these multi-drop deliveries and the dispatch of the other partial loads to their customers. This is the role of the section “Customer j: multi-drop management”. These sections differ from customer 1 to other customers since it is the closest to the companies and must manage the reception and the dispatch of more partial loads. For more details about this simulation model, the reader can consult Figure S2 in the Supplementary Material.
2.5.4. Pooled Supply Chains with Hub Model
In contrast to the previous models, this model consists of three sub-models: the production companies’ sub-model, which contains two sections each corresponding to one company, the customers’ sub-model, which contains three sections each corresponding to one customer, and the pooling hub sub-model. Intermediary deliveries are directed from the companies to the pooling hub, which in turn is responsible for supplying all the customers. For more details about this simulation model, the reader can consult Figure S3 in the Supplementary Material.
2.5.5. Pooled Supply Chains with Hub and Multi-Drop Model
Different modifications are necessary with the hybridization between the multi-drop delivery policy and the pooling hub. These modifications are mainly concentrated on the sub-models of the pooling hub. Indeed, this section integrates a new “Hub: multi drop management” sub-section, which is based on the operating mode of the “Company j: multi drop management” one in the pooled supply chain with multi-drop simulation model. For more details about this simulation model, the reader can consult Figure S4 in the Supplementary Material.
3. Results and Discussion
The simulation of each model was replicated 30 times. Each replication lasted a full year of operation. The CO2 emissions mean per delivered pallet (MCO2R), the mean delivery times to the customer 1 (MDTC1), the mean delivery times to the customer 2 (MDTC2), and the mean delivery times to the customer 3 (MDTC3) have been compiled. Salutation results are provided in Appendix A. Table A1 contains the four variable results of the non-pooling strategy. Table A2 contains the four variable results of the multi-pick strategy. Table A3 contains the four variable results of the multi-drop strategy. Table A4 contains the four variable results of the hub strategy. Table A5 contains the four variable results of the combined hub and multi-drop strategy. All statistical tests are performed using Minitab 18 software.
3.1. Models Verification and Validation
To verify and validate each of the five developed simulation models, the Pearson’s correlation test statistics are used. This test is based on the estimation of the Pearson product moment correlation coefficient between each pair of the studied four variables (MCO2R, MDTC1, MDTC2, and MDTC3). Indeed, Pearson’s correlation test is chosen because it tests the statistical relationship, or association, between two variables. It should be noted that, to our knowledge, this is the first time that the Pearson correlation test is used to both verify and validate simulation models.
Figure 9 displays the correlation for the lower triangle of the correlation matrix for all four variables of each of the five strategies using Minitab Software. Each cell contains two numbers. The number above is the correlation coefficient, which is assumed a value between −1 and +1. The number below is the p-value. If the p-value is less than 0.01, then the null hypothesis (H0: correlation coefficient equal to 0) is rejected and a significant correlation between the two variables is concluded. While p-value is higher than 0.01, the absence of any correlation between the variables is concluded at 1% of risk significance.
The Pearson’s correlation test statistics are applied twice. In the first interpretation, the variable TCO2R (CO2 emission rate) should not be correlated to any of the delivery times for each customer, and this is for each valid strategy. Since all the p-values are higher than 0.01, there is sufficient evidence at 0.01 that the correlations are zero. Except for the last strategy (hub and multi-drop strategy) there is a significate correlation between TCO2R and MDTC3 and consequently a no logic relation between them. Consequently, the strategy will be excluded from the analysis. In the second interpretation of Pearson’s correlation test statistics, the relation between delivery time variables should be confirmed as mentioned in Table 1. Indeed, only in multi-drop strategy and hub and multi-drop strategy there are possible relations between customers. Customers in all other strategies (non-pooling, multi-pick, and hub) should not have any relations between them. In Figure 9, there are only two p-values (written by the Minitab software as p-value), which are less than 0.01. A significate relation between MDTC1 and MDTC2 in both multi-drop strategy (p-value = 0.003) and combined hub and multi-drop strategy (0.007). Consequently, all results of this second interpretation are perfect.
3.2. Simulation Results and Interpretation
Four supply chain pooling strategies are remaining in the analysis, because the strategy based on combined hub and multi-drop strategy was excluded during the verification and validation phase. The following Table 5 presents the simulation results of MCO2R of all studied strategies, which are replicated 30 times. Each replication lasted a full year of operation. Consequently 120 replications are made. To select the best supply chain pooling strategy according to CO2 emissions, one-way analysis of variance (ANOVA) test is applied, as mentioned in Figure 10. This test has two hypotheses (H0: all means of the four strategies are the same, vs. H1: not all the means are equal). To the right of the one-way ANOVA, under the column headed P, is p-value. In this case, p-value = 0.000 is less than 0.1. H0 is rejected and the result provides sufficient evidence to conclude that the MCO2R are not all the same for all strategies and at least one mean is different to the others. Note that this does not mean that all MCO2R are different (some pairs may be the same).
The ANOVA test does not tell which strategy is statistically different. It is necessary to look at confidence intervals or run post hoc tests to determine that. In Figure 10, an (*) indicate the coordinate of the mean at each level. In this research, a pair-wise comparison of the simulation results of all the studied strategies was carried out using Games-Howell’s two-by-two comparison procedure. This procedure does not require the assumption of equality between the variances of the compared groups of values [39]. The results of the Games-Howell procedure are shown in Figure 11.
On the first hand, according to ANOVA showed in Figure 10, the values of the CO2 emissions mean in the non-pooled supply chain were higher than those obtained by the different pooling strategies. Indeed, this value exceeds 50.777 KgCO2/pallet in the case of the non-pooled supply chain. While it does not exceed, in the most unfavorable case, 45.476 KgCO2/pallet for the various studied pooling strategies. On the other hand, the values of the CO2 emissions of the different pooling strategies are close to each other. Games-Howell comparison procedure results, as depicted in Figure 11, show that all the confidence intervals for differences between the CO2 emission means strategies do not include the value zero. Therefore, the CO2 emission means each pooling strategy are considered statistically different.
3.3. Selection of the Best Pooling Strategy
The MCO2R results of all simulation scenarios are ranked in decreasing order in Table 6. All pooling strategies significantly reduce the emissions of CO2 compared to the non-pooled supply chain. Indeed, the reductions vary from 10.439% to 13.58%. The last and largest reduction corresponds to the hub and multi-drop strategy. Moreover, the best strategy which gives the minimum of CO2 is the hub strategy, followed by the multi-pick strategy and the multi-drop strategy.
4. Conclusions and Perspectives
This paper focuses on simulation exploration of the effect of different supply chain pooling strategies on their CO2 emissions. Using a case study of two manufacturing companies and three customers, five SCPS studied included the following: (1) non-pooling strategy; (2) multi-pick strategy; (3) multi-drop strategy; (4) central hub strategy; and (5) combined hub and multi-drop strategy. A DES-based approach is used for all SCTPS studied. First, simulation models for all these strategies are developed using Siman/Arena software. Second, the verification and validation are based on the Pearson correlation test between CO2 emissions and the mean delivery time of each customer and between the delivery time of each pair of customers. Third, one-way analysis of variance (ANOVA) and Games-Howell simultaneous confidence intervals are used to interpret simulation results. The main result of the study is that all SCTPSs significantly reduce the CO2 emissions compared to the non-pooled supply chain. In fact, the reduction in CO2 emissions can reach 13% compared to the non-pooled strategy. Moreover, the best SCTPS that gives the minimum of CO2 is the hub strategy, followed by the multi-pick strategy and the multi-drop strategy.
This research may provide some reasonable insight into current collaboration in the low-carbon supply chain. Some future research perspectives should be addressed:
In this study, five SCTPS strategies are studied. Only one combined strategy approach is envisaged, which is based on both elementary strategies: hub and multidrop. Using the same logic, there are other possible strategies such as combined hub and multi-pick, combined multi-pick and multi-drop. Moreover, a combined three-based strategies hub, multi-pick, and multi-drop seems to be also possible. Extending the current research in the other combined strategies is the first of our interesting perspective;
SCTPS are studied using DES which is a widely used technique in supply chain performance analysis. The simulation technique takes into account all dynamic and stochastic aspects of the system without using advanced mathematics formulation. Although the present methodology is applied to a specific supply chain, which contains only two manufacturing companies and three customers, it can be readily generated by an automatic simulation model generation for large-scale supply chain with many manufacturing companies and many customers. Extending the current research for large-scale supply chain and for real supply chains is the second of our interesting perspective;
In this paper, the majority of the simulation models’ parameters are studied as stochastic. Some other parameters are assumed deterministic such as the speed of the vehicles, vehicles loading capacity, etc. Integrating the stochastic aspect to all supply chain parameters is the third of our interesting perspective;
Many aspects of this simulation exploration are currently being developed. The first aspect is the scope of enlargement of the exploration scope to other supply chain performances. In the second aspect, the study and optimization of the delivery vehicle fleet and their load capacities will be investigated. In addition, a multi-objective optimization of supply chain pooling strategies, taking into account other performance indicators such as order satisfaction rates is the fourth of our interesting perspectives.
Conceptualization, A.J., H.J. and F.M.; methodology, A.J. and W.H.; software, A.J. and H.J.; validation, A.M.A., W.H. and F.M.; formal analysis, W.H. and A.M.A.; investigation, A.J.; resources, A.J. and H.J.; data curation, A.J., A.M.A., W.H. and F.M.; writing—original draft preparation, A.J., H.J. and F.M.; writing—review and editing, A.M.A. and W.H.; visualization, W.H.; supervision, W.H. and F.M.; project administration, A.J., A.M.A., W.H. and F.M.; funding acquisition, A.M.A. All authors have read and agreed to the published version of the manuscript.
This research was supported and funded by Taif University Researchers Supporting Project number (TURSP-2020/229), Taif University, Taif, Saudi Arabia.
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Data are contained within the article.
This research was supported by Taif University Researchers Supporting Project number (TURSP-2020/229), Taif University, Taif, Saudi Arabia. First, the authors are grateful for this financial support. Second, the authors thank the editors and anonymous reviewers for their helpful and constructive comments.
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Figure 7. Simulation model of a Company i section for the non-pooled supply chain.
Figure 8. Simulation model of a Customer j section for the non-pooled supply chain.
Description of the five supply chain pooling strategies.
Type | Strategy | Relation between Customers | Description |
---|---|---|---|
Non-pooling strategy | No | ||
Pooling | Multi-pick | No |
|
Multi-drop | Yes |
|
|
Hub | No |
|
|
Hub and multi-drop | Yes |
|
Time and quantity of pallet feeding in supply chain.
Inter-Arrival Time (Hour) | Palettes Quantity | ||
---|---|---|---|
Company 1 | Product 1 | N (4, 0.5) | 2 |
Product 2 | N (3, 0.5) | 2 | |
Company 2 | Product 3 | N (3.5, 0.5) | 2 |
Product 4 | N (3.5, 0.5) | 2 |
N: Normal distribution.
Time between orders and quantity of pallets per order.
Time Between Order | Quantity of Pallets Per Order | |||
---|---|---|---|---|
Customer 1 | Unif (12, 24) | Company 1 | Product 1 | DISC (0.6, 4, 1.0, 5) |
Product 2 | DISC (0.3, 5, 1.0, 7) | |||
Company 2 | Product 3 | DISC (0.8, 6, 1.0, 7) | ||
Product 4 | DISC (0.7, 4, 1.0, 6) | |||
Customer 2 | Unif (12, 24) | Company 1 | Product 1 | DISC (0.4, 4, 1.0, 5) |
Product 2 | DISC (0.6, 5, 1.0, 7) | |||
Company 2 | Product 3 | DISC (0.5, 3, 1.0, 5) | ||
Product 4 | DISC (0.8, 4, 1.0, 6) | |||
Customer 3 | Unif (24, 36) | Company 1 | Product 1 | DISC (0.5, 3, 1.0, 6) |
Product 2 | DISC (0.5, 4, 1.0, 8) | |||
Company 2 | Product 3 | DISC (0.3, 3, 1.0, 6) | ||
Product 4 | DISC (0.3, 6, 1.0, 8) |
DISC: discrete distribution, Unif: Uniform distribution.
Distances and speeds in the pooled supply chain.
Hub | * | |||||
Company 1 | D:35 v:40 | * | ||||
Company 2 | D:46 v:40 | D:11 v:40 | * | |||
Customer 1 | D:155 v:80 | D:190 v:80 | D:201 v:80 | * | ||
Customer 2 | D:180 v:80 | D:210 v:80 | D:221 v:80 | D:20 v:40 | * | |
Customer 3 | D:245 v:80 | D:280 v:80 | D:291 v:80 | D:90 v:80 | D:55 v:40 | * |
Hub | Company 1 | Company 2 | Customer 1 | Customer 2 | Customer 3 |
D: distance in kilometers, v: speed in kilometers per hour, * not possible.
Results of mean CO2 emission rate (MCO2R) factor according the adopted strategy.
Replication | No Pooling Strategy | Multi-Pick Strategy | Multi-Drop Strategy | Hub |
---|---|---|---|---|
1 | 50.521 | 44.469 | 45.186 | 43.735 |
2 | 50.858 | 44.869 | 45.536 | 44.06 |
3 | 51.042 | 44.903 | 45.723 | 43.957 |
4 | 50.617 | 44.761 | 45.62 | 43.882 |
5 | 50.549 | 44.744 | 45.435 | 43.886 |
6 | 50.56 | 44.828 | 45.505 | 43.814 |
7 | 50.788 | 44.699 | 45.27 | 43.903 |
8 | 50.784 | 44.812 | 45.853 | 43.835 |
9 | 50.55 | 44.737 | 45.282 | 44.141 |
10 | 50.947 | 44.966 | 45.491 | 44.061 |
11 | 50.516 | 44.873 | 45.579 | 43.916 |
12 | 50.89 | 44.266 | 44.924 | 44.052 |
13 | 50.907 | 44.77 | 45.646 | 43.965 |
14 | 50.642 | 44.855 | 45.36 | 43.994 |
15 | 50.947 | 45.102 | 45.948 | 43.685 |
16 | 50.568 | 44.887 | 45.248 | 43.99 |
17 | 50.876 | 44.679 | 45.857 | 44.211 |
18 | 50.847 | 44.739 | 45.47 | 44.024 |
19 | 50.906 | 44.941 | 45.943 | 44.121 |
20 | 50.808 | 44.615 | 45.266 | 43.879 |
21 | 50.833 | 44.83 | 45.575 | 43.911 |
22 | 50.984 | 44.762 | 45.271 | 44.081 |
23 | 50.899 | 44.769 | 45.422 | 43.704 |
24 | 50.903 | 44.626 | 45.076 | 43.774 |
25 | 50.851 | 45.022 | 45.558 | 43.998 |
26 | 50.609 | 44.697 | 45.361 | 44.033 |
27 | 50.928 | 44.779 | 45.79 | 43.808 |
28 | 50.595 | 44.768 | 45.428 | 44.138 |
29 | 50.648 | 44.732 | 45.215 | 44.077 |
30 | 50.93 | 44.772 | 45.448 | 43.984 |
Summary of results.
Pooling Strategy | No Pooling | Multi-Pick | Multi-Drop | Hub |
---|---|---|---|---|
MCO2R (KgCO2/pallet) | 50.777 | 44.776 | 45.476 | 43.954 |
Variation of MCO2R | Reference | −11.818% | −10.439% | −13.437% |
Supplementary Materials
The following supporting information can be downloaded at:
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Abstract
One of the main concepts for improving the sustainability of supply chains is the collaboration between stakeholders by increasing the efficiency of their shared resources. In the literature, there are many research papers related to vertical collaboration in the logistics industry. However, horizontal collaboration has not received the same degree of attention. In fact, horizontal collaboration such as shared freight carrier and freight consolidation can also be considered vital for low-carbon supply chain solutions. In this paper, the problem of the design of supply chain transportation pooling strategies (SCTPS) is studied, which considers both vertical and horizontal collaboration. The purpose of this paper is to study the impact of these SCTPSs to reduce CO2 emissions using discrete-event simulation (DES)-based methodology. Using a numerical case study of two manufacturing companies and three customers, five SCTPS are studied including the following: (1) non-pooling strategy; (2) multi-pick strategy; (3) multi-drop strategy; (4) central hub strategy; and (5) combined hub and multi-drop strategy. The main result of the study is that all SCTPSs significantly reduce the CO2 emissions compared to the non-pooled supply chain. In fact, the reduction in CO2 emissions can reach 13% compared to the non-pooled strategy. Moreover, the best SCTPS that gives the minimum of CO2 is the hub strategy, followed by the multi-pick strategy and the multi-drop strategy.
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1 OLID Laboratory, Higher Institute of Industrial Management of Sfax (ISGIS), University of Sfax, Sfax 3021, Tunisia;
2 Faculty of Economics and Management of Sfax, University of Sfax, Sfax 3018, Tunisia;
3 Department of Industrial Engineering, College of Engineering, Taif University, Taif 21944, Saudi Arabia;
4 LA2MP Laboratory, National Engineering School of Sfax (ENIS), University of Sfax, Sfax 3038, Tunisia;