Inaugural Issue
October 2025
A New Era in Shipping: Global Trust and Green Transformation

Dynamic Optimisation of Green-Fuel Pathways for China Merchants Group’s Asia-Europe Fleet: A System-Dynamics MILP Approach under the 2030 ETS/IMO Regime

ZHANG Yunsong

Ph.D., Research Fellow of Institute of Applied Ecology (IAE) of the Chinese Academy of Science. CEO of Dalian SinoFuture Company.

Abstract

The Asia–Europe shipping corridor faces 2030 decarbonization mandates from the EU ETS (€110–150/t CO₂) and IMO's 40% carbonintensity reduction target, impacting China Merchants Group (CMG)'s bulk and MPP fleet. This study uses a hybrid System Dynamics–MILP model to optimize green-fuel transitions (VLSFO → LNG → methanol → ammonia), calibrated with AIS data (21,150 nm, 15.2 kn). The optimal pathway (LNG 2026, methanol 2028) achieves 53% emissions reduction by 2030, with 6–14% lower NPV than VLSFO or LNG-only scenarios. EUA price volatility drives 49% of NPV variance. Recommendations include LNG retrofits by 2026, methanol contracts by 2028, and a Green-Belt Alliance for bunkering infrastructure. This framework provides a robust decarbonization roadmap for CMG, emphasizing collaboration and hedging.

Keywords :

Green Fuel Transitions; System Dynamics; Mixed-Integer Linear Programming; EU ETS

1. Introduction: The Green Route Challenge

The International Maritime Organization (IMO) now requires a 40% carbon-intensity cut by 2030 (MEPC.377(80)) (IMO, 2023) while the European Union has extended its Emissions Trading System (EUETS) to ocean shipping, phasing-in 100% coverage for voyages to, from and inside the EU by 2026 (Directive 2023/959). These converging policies expose China Merchants Group (CMG) to rising carbon costs on its bulk and multi-purpose (MPP) services between China and North-west Europe and on a prospective 24k TEU container relaunch after 2028 (China Merchants Port Holdings Company Limited (2023).

The research question is therefore: Which staged adoption of low-/zero-carbon fuels minimises CMG's life-cycle cost while meeting the 2030 ETS/IMO constraints under fuel-price, carbon-price, and technology uncertainties?

We answer this by coupling a feedback-rich system-dynamics (SD) core to a mixed-integer linear programme (MILP). Section 2 outlines the model; Section 3 applies it to CMG's fleet; Section 4 derives industry collaboration mechanisms; Section 5 synthesises strategic recommendations.

2. Method: Hybrid SD-MILP Model

2.1 Architecture

Figure 1 shows a two-layer structure. The SD layer tracks: (i) fleet stock by vintage, (ii) cumulative alternative-fuel power, and (iii) bunkering-infrastructure maturity; endogenous feedback capture learning-curve CAPEX erosion and fuel-infrastructure delay. The MILP layer selects retrofit timing, new-build orders, fuels, and sailing speeds to minimise discounted cost. Stocks at year t act as state constraints for decision variables at t+1, providing full optimisation over the dynamic state space—an advance on static or scenario studies.

Figure 1. SD-MILP Model Architecture

2.2 Key Equations

Fleet stock: \begin{equation} N_{s,t+1} = N_{s,t} + A_{s,t} - R_{s,t} \end{equation}(1)

\begin{equation} N_{s,t+1}  \end{equation}: Number of ships in cohort s at the start of year t+1; unit: vessels; role: state variable. s: Ship cohort index (vintage × size class); set S (e.g., Capesize, MPP, optional 24k TEU container). t: Year index; set T = {2022, …, 2035}; unit: year; role: index.

\begin{equation} N_{s,t} \end{equation}: Number of ships in cohort s at the start of year t; unit: vessels; role: state variable.

\begin{equation} A_{s,t} \end{equation}: Newbuild arrivals into cohort s during year t; unit: vessels/year; role: decisiondependent flow.

\begin{equation} R_{s,t} \end{equation}: Retirements (or removals) from cohort s during year t; unit: vessels/year; role: endogenous/exogenous outflow.
Installed power:\begin{equation} P_{f,t+1} = P_{f,t} + \sum_{s} (\alpha_{s,f,t} + \beta_{s,f,t}) \end{equation}(2)

\begin{equation} P_{f,t+1} \end{equation}: Cumulative installed propulsion power using fuel f at the start of year t+1; unit: MW; role: state variable. f: Fuel/propulsion option index; set F = {VLSFO, LNG, MeOH (methanol), NH3 (ammonia)}; role: index.

\begin{equation} P_{f,t} \end{equation}: Cumulative installed propulsion power using fuel f at the start of year t; unit: MW; role: state variable.

\begin{equation} \alpha_{s,f,t} \end{equation}: Newbuildinstalled propulsion power for fuel f in cohort s during year t; unit: MW/year; role: decision variable.

\begin{equation} \beta_{s,f,t} \end{equation}: Retrofitinstalled propulsion power for fuel f in cohort s during year t; unit: MW/year; role: decision variable.
Infrastructure: \begin{equation} B_{f,t+1} = B_{f,t} + \gamma_f P_{f,t} - \delta_f B_{f,t} \end{equation}(3)

\begin{equation} B_{f,t+1} \end{equation}: Bunkering availability (infrastructure) index for fuel f at the start of year t+1; unit: index (0–1 or 0–B_fmax); role: state variable.

\begin{equation} B_{f,t} \end{equation}: Bunkering availability index for fuel f at the start of year t; unit: index; role: state variable.

\begin{equation} \gamma_f \end{equation}: Learning/scale coefficient linking installed power to infrastructure buildout for fuel f; unit: index units per MW (per year); role: parameter.

\begin{equation} P_{f,t} \end{equation}: Cumulative installed propulsion power using fuel f at the start of year t; unit: MW; role: state variable (reused).

\begin{equation} \delta_f \end{equation}: Depreciation/decay coefficient for fuelspecific infrastructure; unit: fraction/year; role: parameter.
Objective:

\begin{equation}
\begin{aligned}
minZ = \sum_{t=2022}^{2035} \frac{1}{(1 + i)^{t-22}} \Bigg[ &\sum_{s, f} \left( C_{f,t}^{fuel} + p_t^{EUA} EF_f K_r \right) F_{s,f,t} \\
&+ \sum_{s, f} \left( C_{s,f}^{NB} \alpha_{s,f,t} + C_{s,f}^{retro} \beta_{s,f,t} \right) + OPEX_{s,t} \Bigg]
\end{aligned}
\end{equation}(4)

\begin{equation} C_{f,t}^{fuel} \end{equation}: Unit fuel price for fuel f in year t; unit: USD/ton (or USD/GJ if energybased accounting is used consistently); role: parameter.

\begin{equation} p_t^{EUA} \end{equation}: EU Emissions Trading System allowance price in year t; unit: USD per tCO2 (if quoted in EUR, converted at annual average rate); role: parameter.

\begin{equation} EF_f \end{equation}: Welltowake greenhousegas emission factor of fuel f; unit: tCO2 per ton of fuel (or tCO2/GJ if energybased); role: parameter.

\begin{equation} K_r \end{equation}: EUETS coverage coefficient for voyage leg category r (e.g., 0 for nonEU leg, 0.5 for extraEU in/out leg, 1 for intraEU leg). In the compressed formulation \begin{equation} K_r \end{equation} represents the routeaverage coverage factor; unit: dimensionless; role: parameter. r: Voyageleg category index (e.g., EU segment, extraEU segment); set R; role: index (appears only through\begin{equation} K_r \end{equation}).

\begin{equation} F_{s,f,t} \end{equation}: Annual fuel consumption of cohort s using fuel f in year t; unit: tons/year (or GJ/year if energybased); role: endogenous variable derived from speed, power, hours, and efficiency.

\begin{equation} C_{s,f}^{NB} \end{equation}: Specific newbuild capital expenditure for cohort s configured for fuel f, per unit installed power; unit: USD/MW; role: parameter.

\begin{equation} \alpha_{s,f,t} \end{equation}: Newbuildinstalled propulsion power for fuel f in cohort s during year t; unit: MW/year; role: decision variable (reused).

\begin{equation} C_{s,f}^{retro} \beta_{s,f,t} \end{equation}: Specific retrofit capital expenditure for cohort s converting to fuel f, per unit installed power; unit: USD/MW; role: parameter.

\begin{equation} \beta_{s,f,t} \end{equation}: Retrofitinstalled propulsion power for fuel f in cohort s during year t; unit: MW/year; role: decision variable (reused).

\begin{equation} OPEX_{s,t} \end{equation}: Nonfuel operating expenditure for cohort s in year t (e.g., crew, maintenance, insurance, lube oils); unit: USD/year; role: parameter or semiendogenous variable (may depend on speed and technology in implementation).

2.3 Data & Calibration

  1. AIS data for fourteen CMG Capesize and MPP ships (2022–2024, 12Hz) yield average China–EU round-trip distance 21,150nm and modal speed 15.2kn.
  2. Fuel baselines (2024): VLSFO 620USD t-1; LNG 950; green methanol 1,380; green ammonia 1,590 (Sun et al., 2024).
  3. Carbon price: base path 110€/t rising to 150€/t by 2030; shock path to 250€/t after 2028 (Wang et al., 2023) .
  4. Discount rate 3.5% (CMG annual report 2023); yard-CAPEX ceiling 80M USD yr-1.
  5. Gurobi 10.0 solves the MILP (≈ 7,200 binaries) and exchanges state variables with the SD module at each step.

3. CMG Case Study: Vessel-Fuel Optimisation

3.1 Scenarios

Four pathways are assessed for the existing bulk/MPP fleet plus a hypothetical 24k TEU ship delivered 2028:

  • P0 – VLSFO business-as-usual
  • P1 – LNG dual-fuel retrofit 2026 → stay LNG
  • P2 – LNG 2026 → green methanol 2028
  • P3 – Methanol 2028 → ammonia-ready new-build 2030+

All comply with TRL≥8 and CII≤0.60 by 2030.

3.2 Cost & Emission Results

Figure 2 shows discounted cost frontiers. Under the base carbon path, P2 yields a 6% lower net present value (NPV) than P1 and 12% below P0; under the Carbon-Shock path the NPV gap widens to 14%. Cumulative well-to-wake emissions (Figure 3) fall 53% by 2030 in P2 and 61% in P3, exceeding IMO's 40% target.

Figure 2. Discounted Cost Frontiers

Figure 3. Cumulative Well-to-wake Emissions

A sensitivity tornado (Table 1) reveals that EUA price volatility explains 49% of NPV variance, green-methanol bunker price 23%, and retrofit CAPEX 12%. Monte-Carlo runs (10,000 draws) show P2 outperforms P1 in 87% of cases.

Table 1. Drivers of NPV Variance (Tornado Decomposition, 10 000 Monte-Carlo draws)

Rank

Uncertainty Parameter

Range Tested

Contribution to NPV Variance

1

EUA price, 2026-30

90–250€/t (triangular)

49%

2

Green-methanol bunker price

1,100–1,600USD t⁻¹

23%

3

LNG retrofit CAPEX

220–320USDkW⁻¹ (triangular)

12%

4

Discount rate (WACC)

2.5–5.0%

7%

5

Annual demand growth

0–3% p.a.

5%

6

Yard-slot availability

60–100M USD yr⁻¹

4%

Statistical method: Pearson regression on normalised rank-order outputs.
Sum≈100%; minor rounding differences.

3.3 Operational Insights

  1. Optimal service speed shifts from 14.8kn (P0) to 15.5kn (LNG phase) and drops to 13.9kn during a simulated LNG price spike—echoing the speed-cost trade-off mapped by Sun et al. (2025).
  2. The yard-CAPEX ceiling limits LNG retrofits to three hulls per year; backlog inflates marginal abatement cost by 18€/t CO2 unless CMG coordinates across subsidiaries.
  3. If ammonia TRL-8 slips to 2033 ("Tech-Bottleneck"), P2 still beats LNG-only by 4% NPV, confirming the robustness of the methanol bridge fuel.

4. Industry Pathway: Collaboration & Trust

4.1 Shared Infrastructure & R&D

SD feedback shows that bunkering-availability delay critically shapesadoption timing: bringing green-methanol facilities online at Rotterdam, Algeciras and, Ningbo by 2028 reduces CMG's total cost by 7%. We propose a Green-Belt Alliance—CMG plus charterers and fuel producers—to pool demand (≥0.8Mt yr-1) and unlock a 12% CAPEX learning effect, consistent with the retrofit-dominant roadmap in Zhao et al. (2023) and fleet-age optimisation in Wu et al. (2022).

4.2 Risk-Pooling & Carbon-Price Hedging

A group-wide EUA-futures desk could hedge 70% of exposure; simulations cut annual bunker-budget volatility by 40%. A collar-and-swap structure referencing EU Allowances lowers the 90th-percentile NPV downside by 5% (Wang et al, 2023).

4.3 Governance & Trust

Joint verification of well-to-wake life-cycle data, audited to ISO 14083, addresses cargo-owner Scope-3 concerns and trims green-finance spreads by 5bp. Transparent MRV strengthens stakeholder trust and accelerates the learning loop in the SD core.

5. Conclusions & Strategic Recommendations

  1. Optimal pathway: LNG retrofit (2026) followed by green-methanol conversion (2028) delivers a 50%+ emission cut and 6-14% NPV gain versus LNG-only, even if ammonia slips beyond 2030.
  2. Key uncertainties: EUA price and e-fuel cost account for >70% of value at risk; proactive hedging and offtake contracts are therefore essential.
  3. Infrastructure collaboration: A Green-Belt Alliance that co-invests in methanol/ammonia bunkering removes the infrastructure-delay penalty and captures 12% CAPEX learning.
  4. Policy message: Stable, forward EU-ETS price corridors and fast-tracked safety codes for ammonia will reduce the discount-rate penalty on zero-carbon assets.
  5. Next research: integrate real-time port-congestion dynamics and multi-carrier competition into the SD-MILP platform.

The hybrid framework offers a transferable blueprint for carriers navigating the turbulent 2020s decarbonization landscape while anchoring decisions in rigorous, feedback-aware optimisation.

  1. China Merchants Port Holdings Company Limited. (2023). 2023 annual report. https://www.cmport.com.hk/UpFiles/bpic/2024-04/20240425050415396.pdf
  2. European Commission. (2023). Directive (EU) 2023/959 of the European Parliament and of the Council Amending Directive 2003/87/EC Establishing a System for Greenhouse Gas Emission Allowance Trading within the Union. Official Journal of the European Union, L 130: 134–202. https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:32023L0959
  3. International Energy Agency. (2024). Gas Market Report, Q3 2024. https://www.iea.org/reports/gas-market-report-q3-2024
  4. International Maritime Organization. (2023). 2023 IMO Strategy on Reduction of GHG Emissions from Ships. Resolution MEPC.377(80). London: IMO..
  5. Zulma, K. A. P., Chougule, K. M., Brand, U. (2025). Well-to-Wake Prospective Life Cycle Assessment of Synthetics Fuels for the Maritime Sector in the Baltic and North Seas (Doctoral dissertation, Carl von Ossietzky Universität Oldenburg). https://elib.dlr.de/213703/1/170225_Thesis_Document_KA_VF%20%281%29.pdf.
  6. Sun, L., Wang, X., Hu, Z., Ning, Z. (2024). Carbon and Cost Accounting for Liner Shipping Under the European Union Emission Trading System. Frontiers in Marine Science, 11, 1291968. https://doi.org/10.3389/fmars.2024.1291968
  7. Sun, M., Vortia, M. P., Xiao, G., Yang, J. (2025). Carbon Policies and Liner Speed Optimization: Comparisons of Carbon Trading and Carbon Tax Combined with the European Union Emissions Trading Scheme. Journal of Marine Science and Engineering, 13(2), 204. https://doi.org/10.3390/jmse13020204
  8. Wang, H., Liu, Y., Li, F., Wang, S. (2023). Sustainable Maritime Transportation Operations with Emission Trading. Journal of Marine Science and Engineering, 11(9), 1647. https://doi.org/10.3390/jmse11091647
  9. Wu, Y., Huang, Y., Wang, H., Zhen, L., Shao, W. (2022). Green Technology Adoption and Fleet Deployment for New and Aged Ships Considering Maritime Decarbonization. Journal of Marine Science and Engineering, 11(1), 36. https://doi.org/10.3390/jmse11010036
  10. Zhao, Y., Chen, Y., Fagerholt, K., Lindstad, E., Zhou, J. (2023). Pathways Towards Carbon Reduction Through Technology Transition in Liner Shipping. Maritime Policy & Management, 52(3), 417–439. https://doi.org/10.1080/03088839.2023.2224813