Green Chemical Systems

Explainable Degradation-Aware Sizing for Off-Grid Green Hydrogen

A critical note on an off-grid PV-battery-PEM hydrogen TEA that folds PEM degradation, battery fade, replacement timing, and Sobol/XGBoost/SHAP interpretation into the sizing objective.

Why this paper matters

Off-grid solar hydrogen has a simple economic problem: the electrolyzer is expensive, but solar power is intermittent. A PEM stack cannot earn back its capital cost if it only operates during a limited part of the day. Rinchi et al. report PEM utilization around 32-33% in the solar-only off-grid cases they study, so the levelized cost of hydrogen is pushed up by low annual hydrogen output per unit of installed PEM capacity.

The second problem is more subtle. Many techno-economic analyses size the system on a representative year, repeat that production profile across the project lifetime, and then add replacements using coarse calendar assumptions. That misses the path dependence of the system. PEM stacks degrade under high load and start-stop cycling. Batteries lose effective capacity through cycle and calendar aging. Replacement timing is therefore not just an accounting line; it is a consequence of the dispatch trajectory.

This paper is useful because it puts those pieces into the objective evaluation itself. The main contribution is not a new optimizer. Differential Evolution, Sobol analysis, XGBoost, and SHAP are standard tools. The contribution is the engineering consistency of the pipeline:

historical hourly weather
  -> PV generation
  -> rule-based PV-battery-PEM dispatch
  -> PEM degradation and battery fade
  -> physics-scheduled replacements
  -> discounted lifetime cost and hydrogen output
  -> LCOH-based sizing
  -> Sobol/XGBoost/SHAP interpretation

That is a useful TEA move: make the optimizer see the same degradation-aware lifecycle economics that the paper later reports.

What is optimized

The design vector is small:

x = [ PPV , Ebat , PPEM ]

Here PPV is PV capacity, Ebat is battery energy capacity, and PPEM is PEM rated power. The objective is LCOH plus penalties for production shortfall and residual energy imbalance.

The dispatch policy itself is not optimized. Operation is rule-based: run the PEM at full load if PV and the battery can support it, run at partial load if PV is above the minimum stable PEM load, and turn the PEM off if the minimum load cannot be met. This matters. The paper is degradation-aware in the evaluation, but it is not a joint design-operation optimization paper. It is closer to optimized capacity sizing under a fixed dispatch heuristic.

That distinction is not a minor wording issue. Full-load operation improves utilization and capital recovery, but it can also accelerate degradation. If stack replacement is near a threshold, partial-load smoothing could be economically better than forcing full-load operation. This paper accounts for that degradation cost after the rule acts; it does not optimize the rule against that cost.

Degradation is the important modeling step

The PEM degradation model links operation to efficiency loss. Operating degradation increases with load fraction through a power-law term, while start-up events add extra degradation. The accumulated degradation then increases the specific energy consumption:

SECdeg (t) = SEC (t) [1+D(t)]

The economic mechanism is direct. High load and frequent start-stop events increase degradation; degradation raises SEC; higher SEC lowers hydrogen output for the same electrical input; lower lifetime production and stack replacement costs raise LCOH.

The battery model is simpler. Effective battery capacity declines according to the more severe of cycle fade and calendar fade, with a floor on remaining capacity. This is not a detailed electrochemical aging model, but the paper’s results suggest that battery sizing is not the main economic driver in the studied cases.

What the results say

The optimized systems are roughly half-megawatt PV systems with PEM capacities around 240-290 kW:

Site PV kW Battery kWh PEM kW LCOH
UAE 536.7 99.9 286.9 7.83 $/kg
KSA 532.0 149.5 285.6 8.06 $/kg
Qatar 477.4 182.2 242.2 8.22 $/kg

These are high values, but the reason is not mysterious. A solar-only off-grid system cannot keep the PEM stack highly utilized, so capital cost is spread over a smaller hydrogen output. Grid connection or wind-solar complementarity could change the utilization story, but that is outside this paper’s system boundary.

The degradation effect is large enough to matter. Lifetime-averaged hydrogen yield is about 5-6% below year-one output. PEM stack replacement occurs around years 8, 16, and 24, while battery replacement occurs around year 15. The paper reports that stack replacement alone adds about 1.20 $/kg to LCOH. Ignoring degradation would therefore bias the economics downward in a structural way.

The cost hierarchy is also clear. CAPEX dominates the LCOH, stack replacement is the next important term, and battery replacement is small. The strongest improvement levers are PEM efficiency, PEM CAPEX, PV CAPEX, and discount rate. A 20% SEC reduction is reported to cut Abu Dhabi LCOH by about 1.62 $/kg, which is larger than the effect of a comparable PEM CAPEX reduction.

Explainability is useful, but not causal proof

The paper adds Sobol sensitivity analysis, an XGBoost surrogate, and SHAP values to interpret the simulator. That is useful because the full model is a non-smooth black-box objective: dispatch regimes switch, replacement events are triggered by thresholds, and weather-year effects interact with sizing.

The Sobol results make intuitive sense. PV capacity has the largest total-effect index, followed by PEM capacity. Degradation rate and PEM CAPEX matter, while battery capacity has much weaker influence. XGBoost approximates the simulated LCOH mapping with high holdout accuracy, and SHAP then attributes surrogate predictions mostly to PV capacity and degradation-related variables.

The limitation is that this is explanation of a simulator, not validation of the physical plant. SHAP is not causal evidence. A careful interpretation is: given this simulator, this sampling range, and this surrogate model, degradation-related parameters receive high attribution in the learned LCOH mapping. That is still informative. It is just not a proof that the same ranking would hold under a different dispatch policy, degradation law, or downstream hydrogen boundary.

The main weakness

The strongest limitation is the fixed dispatch policy. The paper is called degradation-aware, but the control policy does not appear to solve a degradation-aware dispatch problem. It follows a heuristic that prioritizes PEM utilization. A stronger formulation would optimize both capacity and dispatch policy:

minx,π Cdisc(x,π) Mdisc(x,π)

where π controls whether to run at full load, smooth partial-load operation, charge the battery, or delay operation to avoid crossing a replacement threshold. That would turn the paper from degradation-accounting sizing into degradation-aware operation and design.

There are other limits too. The degradation law is an engineering surrogate. Real PEM degradation depends on temperature, pressure, water purity, current-density profile, shutdown protocol, and balance-of-plant behavior. Weather uncertainty is represented through historical records rather than a full climate-risk model. The LCOH boundary is closer to production-gate hydrogen because compression, storage, transport, and delivery are not the main focus.

One-sentence evaluation

This is not a new optimization-theory paper. It is a practical process-systems TEA paper that makes off-grid PV-battery-PEM hydrogen sizing more internally consistent by carrying degradation, replacement, and lifetime economics through the objective, then using explainability tools to inspect the resulting cost drivers.

Reference

Rinchi, B., Al-Dahidi, S., Ayadi, O., & Alrbai, M. (2026). Explainable degradation-aware techno-economic optimization of off-grid green hydrogen production. Energy Conversion and Management, 364, 121710.