1. Introduction
The problems of climate change and greenhouse gas (GHG) emission have attracted extensive attention from both industry and academia [
1,
2,
3,
4,
5,
6]. In the 21st United Nations Climate Change Conference, the United Nations adopted the Paris Agreement, which proposes the target to control the global average temperature rise within 2 degree Celsius compared to pre-industrial levels, and pursuing 1.5 degree Celsius [
7]. It is believed that under such relatively mild temperature rise, the risks and impacts of climate change would be significantly reduced. However, the global average temperature rise will reach 3 degrees Celsius by the end of this century without more efficient measures coming into force [
8]. The transportation industry and the maritime industry also put efforts on the task of emission reduction [
9,
10,
11,
12,
13,
14,
15,
16,
17,
18,
19,
20,
21]. According to the latest Review of Maritime Transport, international shipping accounts for approximately 3 percent of global GHG emissions from human activities, and thus decarbonization has become an increasingly urgent priority in the industry [
22]. Various emission reduction targets and agreements have been proposed and approved recently. The “Getting to Zero Coalition’s Call to Action for Shipping Decarbonization”, which is signed by over 200 maritime industry organizations, is committed to implementing the commercial deployment of zero-emission vessels along deep-sea trade routes by 2030 and the entirely net-zero energy sources for international shipping by mid-century [
23]. It is highlighted that private party actions must go hand in hand with government actions in the decarbonization of the maritime sector, constructing the necessary infrastructure for scalable zero-emission energy sources, including production, distribution, storage, and bunkering [
23]. At the United Nations Framework Convention on Climate Change (UNFCCC) Conference of the Parties (COP) 26, the Dhaka–Glasgow Declaration was launched to establish a mandatory GHG levy on international shipping, and the Clydebank Declaration aims to set zero-emission maritime routes between ports [
24,
25].
With the ambitious emission-reduction plan, the uptake of zero and net-zero fuels, for example, hydrogen, synthetic non-carbon fuels (ammonia), battery power derived from zero carbon electricity based on solar, wind, hydro or nuclear power, and biomass, is advancing slowly [
8,
22]. As transitional measures, other alternative fuels are adopted, in which LNG is the most widely used one. LNG is the greenest fossil energy source for ship use, almost eliminates the sulfur emissions and particulate matters, and reduces nitrogen oxides to 20 percent and
emissions to 80 percent of the emission levels of heavy fuel oil (HFO), which is the traditional fuel in the maritime. From the technology and economic perspectives, dual-fuel engines enable ships to be operated on LNG and traditional marine fuels to comply with emission reduction regulations while remaining competitive [
8,
26,
27]. As the transitional fuels for maritime transport, the consumption volume of LNG as marine fuel is growing fast, and the investment on application promotion is also soaring [
28].
One of the critical issues in the popularization of dual-fueled vessels is the infrastructure construction, especially the establishment of LNG bunkering facilities [
29,
30]. According to the statistics, in addition to the existing ones, dozens of LNG bunkering facilities are under construction globally [
30]. Therefore, research on the implementation of LNG bunkering facilities is in urgent need.
Numerous studies have been conducted focusing on the promotion of LNG as marine fuel. One branch comprises papers investigating dual-fueled ship retrofitting and deployment from the ship operators’ perspective [
26,
31,
32,
33,
34]. The other one comprises studies considering the infrastructure construction, including the design of bunkering facilities [
35,
36] and number and location of bunkering stations [
37,
38]. In this paper, we focus on the deployment problem of the LNG bunkering stations, namely, how to arrange the construction work of various LNG bunkering stations. China has seven of the world’s top ten container ports, including Hong Kong, and is a pioneer in the promotion of LNG as marine fuel [
39,
40]. Thus, in this paper, we conduct a case study of the LNG bunkering station deployment problem based on the Chinese shipping network. In the case study, the deployment of ships is considered as well.
Given the literature, the contribution of this paper is threefold. First, we abstract the Chinese container shipping network on the basis of liner shipping routes operated by the China Ocean Shipping (Group) Company (COSCO), which is the largest shipping company in China. Data of LNG bunkering price, traditional fuel price, LNG bunkering station construction costs, and other critical parameters were collected from real-world cases and official websites. This case study validates the model and algorithm proposed in academic research better than numerical experiments that are randomly generated. Second, this study provides specific suggestions for the LNG bunkering station deployment problem in China, and managerial insights can be provided for the competent department. Third, sensitive analyses conducted in this paper also investigate the effectiveness of the deployment plan with different budgets, LNG bunkering station costs, and LNG prices.
The remainder of this paper is organized as follows.
Section 2 provides the concrete problem description and the mathematical model.
Section 3 introduces the solution method briefly.
Section 4 presents the numerical experiments and corresponding results. Last but not least, the paper closes with conclusions in
Section 5.
2. Model Formulation
The problem description and the specific mathematical model for the LNG bunkering station problem in a container shipping network are provided in this section.
2.1. Problem Description
In this study, we consider a container shipping network consisting of multiple ports that will be equipped with LNG bunkering stations. Given the limited construction budget, not all ports will be equipped with an LNG bunkering station. In this paper, from the government’s perspective, we determine the number of LNG bunkering stations and the specific ports to provide the LNG bunkering service as well.
The set of physical ports in the container shipping network is denoted by . A set of liner shipping routes, , are operated on the shipping network by different shipping companies. On route j, homogeneous ships are chartered in and deployed to sail along a closed loop. The set of ports of call on route j is denoted by , and represents the one.
Route
j can be divided into
voyages with the sailing distance of
. Ships deployed on route
j berth at port of call
k for
hours for cargo handling, and sail at the speed of
knots (nautical mile per hour). For each route, the weekly service frequency should be maintained as stated in previous studies on ship deployment [
41,
42,
43].
Currently, no LNG bunkering service is available in the network, and therefore all ships deployed consume MDO as the main bunker fuel for power. The weekly chartering cost of such a traditional diesel ship for route
j is denoted by
. The market bunkering price of MDO is denoted by
USD/ton. The MDO consumption rate of ship
j,
ton/n mile, depends on the sailing speed and is in an approximate third power relationship with
[
41,
44,
45]. Meanwhile, the consumption rate while berthing, denoted by
, does not change with the sailing speed [
28,
46]. Due to the damage caused by ship emissions, in this paper, we consider that the environmental costs of
USD will be incurred when a ton of MDO is consumed.
When the LNG bunkering service is available, dual-fueled ships may also be deployed on route
j at the weekly chartering price of
USD. A dual-fueled ship deployed on route
j consumes
tons of LNG per nautical mile and
tons of LNG per berthing hour. Following [
47], it is assumed that the LNG tanker of the dual-fueled ships will be filled up at each bunkering station on its route. MDO will be used if LNG is in short, considering the limited LNG tank capacity, denoted by
tons. For MDO, the fuel consumption rates for traditional ships and dual-fueled ships for the same route are the same. Based on this, we have
, in which
Q is a coefficient, namely, the MDO consumption rate is proportional to the LNG consumption rate. Therefore, for route
j, when one ton of LNG is consumed,
Q tons of MDO are saved [
47]. To assure that the study is not trivial, we further assume that LNG is more economical than MDO, namely,
and
, in which
is the bunkering price of LNG (USD/ton).
Compared with MDO, LNG has a much lower environmental cost . To lower the ship emission levels, the government will allocate a budget to build LNG bunkering stations at some of the ports. The construction costs of a bunkering station at port , are denoted by USD. The given total budget for LNG bunkering station construction is denoted by USD. The government decides which LNG bunkering station to build, and shipping companies make the ship deployment decisions. In this paper, the government aims to minimize the annual ship emission costs, and shipping companies minimize their annual operating costs.
2.2. Mathematical Model
Here, we list the notations used in the mathematical model.
Sets and indices |
| the set of physical ports in the network, , indexed by i; |
| the set of shipping routes operated by different shipping companies, , indexed by j; |
| the set of ports of call covered by route j, , indexed by k. |
Parameters |
| binary parameter, equal to 1 if the port of call of route j refers to physical port i, 0 otherwise, ; |
| the sailing distance (nm) from the port of call on route j to the port of call, ; |
| the sailing distance (nm) from the port on route j to the 1st port, ; |
| the upper limit of sailing speed (knot) of ships deployed on route j, ; |
| the lower limit of sailing speed (knot) of ships deployed on route j, ; |
| the weekly chartering cost (USD/week) of traditional diesel ships deployed on route j, ; |
| the weekly chartering cost (USD/week) of dual-fueled ships deployed on route j, ; |
| the bunkering price of MDO (USD/ton); |
| the bunkering price of LNG (USD/ton); |
| the construction cost (USD) of LNG bunkering station at physical port i, ; |
T | the number of stages of the LNG bunkering system deployment plan; |
| the given budget (USD) that is allocated to LNG bunkering station construction; |
Q | the coefficient that represents the relationship between the consumption rate of MDO and LNG; |
| the ship emission cost of one ton of MDO (USD/ton); |
| the ship emission cost of one ton of LNG (USD/ton); |
| the LNG tank capacity of dual-fueled ships that are deployed on route j, ; |
| the berthing time (hour) at the port of call on route j, . |
Upper-level decision variables |
| binary variable, equal to 1 if LNG bunkering station at physical port i will be constructed, 0 otherwise, . |
Lower-level decision variables |
| binary variable, equal to 0 if traditional diesel ships are deployed on route j, equal to 1 if dual-fueled ships are deployed on route j, ; |
| integer variable, the number of ships chartered in and deployed on route j, ; |
| the sailing speed (knot) of ships chartered in and deployed on route j, ; |
| the MDO consumption rate (ton/n mile) of ships deployed on route j while sailing, ; |
| the MDO consumption rate (ton/hour) of ships deployed on route j while berthing, ; |
| the LNG consumption rate (ton/n mile) of dual-fueled ships deployed on route j while sailing, ; |
| the LNG consumption rate (ton/hour) of dual-fueled ships deployed on route j while berthing, ; |
| binary variable, equal to 1 if port of call k on route j has LNG bunkering station, 0 otherwise, ; |
| the LNG remaining volume when dual-fueled ships leave port of call k on route j (after refueling, if any), ; |
| the LNG remaining volume when the cargo handling at port of call k on route j is just finished (before refueling, if any), ; |
| the weekly LNG consumption volume (ton) of route j, ; |
| the weekly MDO consumption volume (ton) of route j, . |
Vectors |
| the vector of ; |
| the vector of , , . |
The LNG bunkering system deployment problem can be described by the following model
:
subject to
and
where
are determined by the following lower-level model:
subject to
In
, which demonstrates the problem faced by the government, the objective function (
1) minimizes the annual emission costs of all shipping routes. Constraint (
2) indicates the budget constraint. Constraints (3) are the domains of
.
In
, which demonstrates the problem faced by the operator of route
j, the objective function (
5) minimizes the weekly operating costs consisting of the ship chartering cost and bunker cost. Constraints (
6) calculate the LNG remaining volume at different ports of call
k. Constraints (7) and (8) state that dual-fueled ships consume MDO if and only if LNG is in short. Constraints (9) show that the LNG tank of dual-fueled ships will be filled up at every port with the LNG bunkering station. Constraint (10) is the weekly service frequency constraint. Constraints (11) and (12) calculate the MDO and LNG consumption volumes. Constraints (13) to (19) are variable domains.
4. Numerical Experiments
In this study, we conducted numerical experiments based on the shipping routes operated by COSCO, which is the largest Chinese shipping company. The solution method is programmed in C++ with Visual Studio 2021, and CPLEX 20.10 was used to solve . Computational experiments were conducted on a HP ENVY x360 Convertible 15-dr1xx laptop with i7-10510U CPU, 2.30 GHz processing speed and 16 GB of memory.
4.1. Parameter Settings
A case study was conducted based on a Chinese container shipping network, which was abstracted from the operating routes of COSCO, the biggest shipping company in China [
48]. The shipping network consists of 43 container ports and 44 sailing routes in total and covers China’s coastline and the Guangdong–Hong Kong–Macao Greater Bay Area. For the specific ports and routes, please see
Appendix A. Given the large scale of the case study, CPLEX still solves all the numerical experiments within 120 s.
In this paper, the LNG station construction costs for ports in the shipping network were set between CNY 10,000,000 and CNY 20,000,000 (approximately USD 1,450,000 to USD 2,900,000), referring to real-case LNG bunkering station construction projects [
49,
50,
51]. Details of deployed ships are obtained from authoritative studies and reports [
8,
22,
27,
28,
46,
52]. The emission costs of MDO and LNG are calculated based on the studies of [
28,
53,
54]. Specifically, four types of emissions are considered in this study, namely
,
,
, and
, which make up more than 99% of ship emissions. When one tonne of MDO is consumed by a shipping vessel, 0.0001 tonnes of
, 0.167 tonnes of
, 3.206 tonnes of
, and 0.00203 tonnes of
are emitted; when one tonne of LNG is consumed by a shipping vessel,
tonnes of
, 0.0466 tonnes of
, 2.75 tonnes of
, and
tonnes of
are emitted. The social costs associated with the emissions of
,
,
, and
are 11,123 USD/ton, 6,282 USD/ton, 33 USD/ton, and 61,179 USD/ton, respectively. As a result, we have
USD/ton,
USD/ton. To compare the bunkering station cost investment and the environmental benefits, we adopt a depreciation time of 20 years with 8% of interest rate to convert the LNG bunkering construction costs
into the equivalent annual costs, denoted by
[
27].
Based on the calibration of the study by [
41], the fuel consumption rate parameters of route
j while sailing,
and
, were randomly generated within the ranges of
and
, respectively. As for the fuel consumption rate while berthing, two sets of parameters were required: the auxiliary engine power and the specific fuel consumption. Referring to the GHG studies by the IMO [
28,
46], the auxiliary engine powers were set at 900 to 1000 kW, and the specific fuel consumption of LNG was set at 135 g fuel/kWh. The concrete sailing distances of each voyage were not available on the official website of COSCO; instead, they were collected from a professional shipping big data online platform [
55].
4.2. Results and Analyses
First, we conducted the numerical experiments with the total budget of USD 30,000,000, and the results are listed in
Table 1.
From
Table 1, we can see that 14 out of 43 ports will be equipped with LNG bunkering stations after the construction work, including Hong Kong. Meanwhile, USD 29,029,000 in total will be spent on the construction of these bunkering stations. As a result, 38 shipping routes will switch from traditional ships to dual-fueled ships, and the annual total emission costs will be reduced by 3,266,300 USD/year, from 24,092,400 to 20,826,100 USD/year. Although the total construction costs spent are higher than the reduced annual emission costs, the annualized construction costs, which equal USD 2,958,060, make the investment worthwhile. Therefore, the LNG bunkering station deployment plan is cost-effective when the durability of the bunkering stations and interest rate are considered.
Table 1 shows that with the 14 LNG bunkering stations out of the 43 candidate locations being built, most of the shipping routes will switch from traditional vessels to dual-fueled vessels. Such effectiveness is due to the fact that some ports are frequently visited by various shipping routes. Meanwhile, it is not necessary to equip all ports of call with LNG bunkering stations to make dual-fueled vessels preferable for a shipping route, especially for short routes. In this case, among all 125 ports of call in the 44 shipping routes, 73 ports of call are covered by the 14 bunkering stations, and thus most of the routes switch to dual-fueled vessels.
To investigate the deployment plan under various scenarios, we conducted numerical experiments with different values of the total budget, the bunkering station construction costs and the LNG bunkering price.
The third row in
Table 2 indicates that the bunkering station construction costs varies from 50% to 150% of that in the original case. Regarding the total budget, we set the value from 5% of the total construction costs of bunkering stations at all the ports, which equals USD 4,611,400, to 100%, which equals USD
. Results are listed in
Table 3,
Table 4 and
Table 5.
The results of sensitive analyses indicate that the annual emission costs increase with LNG bunkering price and LNG bunkering station costs, and decrease with the total budget for bunkering station establishment. In other words, in addition to allocating a large budget, lowering the LNG bunkering price and the station construction costs help to promote the adoption of LNG as marine fuel and reduce shipping emissions. For the government, two measures can be adopted: (i) giving subsidies to ship operators for consuming LNG as marine fuel, and (ii) reducing the bunkering station construction costs by production optimization and efficiency improvement. Regarding the cost-effectiveness, it is revealed in
Table 5 that the reduced annual emission costs exceed the annualized construction costs when the total budget is no lower than USD 27,668,400, which equals 30% of the total costs to build bunkering stations at all ports in the Chinese container shipping network. It should be mentioned that the annual emission costs reach the lowest level when the total budget is USD
, and further investment brings no environmental benefits. Thus, equipping all ports with bunkering stations is unnecessary from the cost-effective perspective.
For the competent government, in addition to maximizing emission reduction with the given construction budget, it is also viable to set a desired emission reduction target and make a corresponding LNG bunkering station deployment plan with the aim to minimize the total costs. The three methods, namely, investment in LNG bunkering station construction, improve the production efficiency, and a subsidy for consuming LNG can be adopted simultaneously to maximize the emission reduction effect with the given budgets or minimize the total costs to achieve the predetermined emission reduction target.
5. Conclusions
In this paper, we conducted a case study of the LNG bunkering station deployment problem based on a Chinese container shipping network. Referring to the shipping routes operated by the biggest shipping company in China, COSCO, a network of 43 ports and 44 shipping routes was abstracted. Generally speaking, LNG bunkering station construction is cost-effective when the facility durability and the inflation rate are taken into consideration. Sensitive analyses on LNG price, bunkering station construction costs, and total budget reveal that the effectiveness of the deployment plan in LNG promotion and emission reduction increases with the total budget and decreases with the LNG bunkering price and the construction costs. Therefore, it is indicated that allocating a large budget is not the only way to promote LNG as marine fuel. Specifically, when the emission reduction effectiveness reaches the highest level before the total budget can cover all the construction works, more investment will be in vain. To sum up, two sets of constructive managerial insights for the governmental were obtained: (i) reducing LNG usage cost and lowering bunkering station construction costs can promote the LNG application, and (ii) it is not always necessary to build bunkering stations at all ports.
This case study is based on a realistic Chinese container shipping network, and it validates the model and solution method proposed in academic studies. The managerial insights obtained provide constructive suggestions for the government and help in identifying the optimal LNG bunkering station deployment plan that reaches an obvious emission reduction plan and avoids extra costs. Compared to previous studies on this topic, this paper investigates the problem of a large-scale realistic shipping network and therefore yields more practical conclusions and managerial insights.
For future research, there are several directions that could be followed. First, when the demands for LNG from ships increase to a high level, the bunkering and storage capacities of bunkering stations should be considered. Second, the establishment of other infrastructure facilities can be integrated into the problem, for example, the transportation approach of LNG to the port-side bunkering stations. Third, the situation in which the ship operator is also the ship owner is worth investigation in the future.