Submitted:
24 August 2026
Posted:
26 August 2026
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Abstract
Energy-burdened rural communities require hybrid renewable energy storage solutions that are not only economically viable but also resilient to extended generation shortfalls. This study develops a spatially informed techno-economic and resilience assessment framework for hydrogen-biogas renewable microgrids and applies it to Robeson County, North Carolina. A Hydrogen Priority Index (HPI) is used to identify locations where high household energy burden coincides with favorable renewable energy suitability. Four community-scale microgrid configurations are then evaluated in HOMER Pro under standard economic criteria and an embedded seven-day winter solar shortfall stress scenario. Results show that biogas integration reduces net present cost by 28.4% by restructuring the optimal system architecture and reducing PV and battery oversizing. PV-battery configurations cannot achieve near-complete resilience under the imposed stress scenario regardless of component scaling, while hydrogen-inclusive configurations reduce stress-period unmet load by 97.2%. The full hydrogen-biogas hybrid delivers this resilience-constrained performance at 26% lower net present cost than the hydrogen-only configuration. These findings demonstrate that combining spatial prioritization with resilience-constrained techno-economic assessment supports more equitable and deployment-ready planning of renewable microgrids for underserved rural communities.
Keywords:
hydrogen energy storage
; biogas integration
; off-grid microgrids
; microgrid optimization
; techno-economic assessment
; energy resilience
; energy burden
1. Introduction
Hydrogen-integrated microgrids represent a technically viable pathway to resilient electrification in underserved communities, yet existing deployment frameworks remain misaligned with the equity-based siting and resilience requirements these communities specifically impose [1,2]. Low-income and rural communities in the southeastern United States face energy burdens exceeding 10% of gross household income, more than three times the national median, while simultaneously lacking the financial capacity to invest in backup systems or participate in clean energy markets [3,4]. North Carolina exemplifies this challenge: with 80 of its 100 counties classified as rural and nearly 1.5 million residents classified as energy-overburdened, the state presents among the most acute concentrations of residential energy vulnerability in the country, driven by energy-inefficient housing stock and persistent structural disinvestment [5,6]. Energy burden, defined as the percentage of gross household income allocated to residential energy expenditures, is the established metric for identifying communities where energy costs impose disproportionate financial stress [7]. The U.S. Department of Energy Low-Income Energy Affordability Data (DOE LEAD) dataset provides census-tract-level energy burden estimates that enable spatially explicit identification of high-vulnerability communities [8], forming the equity data foundation of this study's site selection framework.
Off-grid solar photovoltaic (PV) microgrids have emerged as technically and economically viable pathways to electrification in underserved communities, bypassing costly grid extension while delivering clean generation at community scale [9]. Within this landscape, hydrogen storage has attracted growing attention as a long-duration resilience energy storage medium capable of bridging multi-day generation deficits that battery systems cannot economically address [9,10]. On the other hand, biogas, produced through anaerobic digestion of organic feedstocks including livestock manure, provides a weather-independent dispatchable complement to intermittent PV generation, making it a natural partner for rural hybrid energy systems where agricultural feedstocks are locally available [11]. Together, these technologies directly address the structural deficiencies that produce chronic energy burdens: hydrogen provides multi-day resilience storage, biogas provides dispatchable renewable firm power, and PV provides cost-effective primary generation.
Despite this technical promise, most design frameworks used to evaluate hydrogen-integrated microgrids have been developed primarily for cost minimization under normal operating conditions, without incorporating the social equity criteria or resilience stress testing that deployment in energy-burdened communities specifically requires [12]. Existing site selection approaches optimize technical and economic suitability without accounting for community vulnerability, systematically bypassing the populations most in need of resilient energy access. At the same time, resilience evaluation in the hydrogen microgrid literature has relied on post hoc scenario analysis rather than on optimization-embedded stress protocols, resulting in designs that are cost-optimal under normal conditions but not inherently stress-hardened. North Carolina's rural counties offer a compelling and underserved context in which to address this triple gap directly: the state ranks among the highest in residential energy burdens in the southeastern United States, within predominantly agricultural landscapes that offer both strong solar resources and substantial livestock-based biogas potential. This study therefore develops and demonstrates a spatially informed interdisciplinary techno-economic and resilience optimization framework that integrates equity-based site prioritization, community-scale biogas resource quantification, and embedded resilience stress testing within a single hydrogen-biogas microgrid comparative assessment methodology, providing a deployment-ready framework explicitly built for energy-burdened rural communities rather than adapted from frameworks designed for cost-optimal contexts.
1.1. Literature Review
1.1.1. Hydrogen-Integrated Hybrid Renewable Systems
The techno-economic feasibility of hydrogen-integrated off-grid microgrids has been extensively evaluated using simulation-based optimization platforms, most prominently HOMER Pro (Hybrid Optimization Model for Multiple Energy Resources), a widely used medium for techno-economic optimization of hybrid energy systems [13,14]. A hydrogen-integrated microgrid typically couples a PV array with a proton exchange membrane (PEM) electrolyzer, compressed hydrogen storage tank, and PEM fuel cell: during surplus generation periods, excess PV output drives electrolysis; stored hydrogen is later reconverted via the fuel cell during generation shortfalls [15,16]. This architecture enables multi-day and seasonal energy storage at scales that lithium-ion battery systems cannot cost-effectively achieve, making it particularly relevant for sites subject to extended low-irradiance periods [10,17]. Recent HOMER Pro-based feasibility studies confirm the viability of off-grid hydrogen-integrated hybrid systems across diverse resource-constrained contexts [18]. Comprehensive reviews of hybrid hydrogen-battery storage optimization approaches further identify resilience stress testing and equity-based siting as consistently unaddressed gaps in existing frameworks [19], where optimization under normal operating conditions remains the dominant paradigm.
Ghenai et al. demonstrated for a residential desert community that hydrogen storage improves system reliability at a cost premium relative to PV-battery configurations, quantifying the trade-off between reliability and levelized cost of energy (LCOE) [20]. Lokar and Virtic established that hydrogen is essential for complete seasonal energy self-sufficiency in residential buildings at mid-latitude locations where winter solar constraints cannot be bridged by battery storage alone [17]. Babatunde et al. showed that applying multi-criteria sustainability objectives shifts the optimal off-grid configuration from PV-battery to PV-fuel cell hybrid, underscoring the inadequacy of single-criterion cost optimization frameworks for communities that require reliability alongside affordability [12]. Abdin and Merida conducted a techno-economic comparison across multiple hybrid off-grid configurations and demonstrated that hydrogen becomes cost-competitive under specific resource and load conditions, with LCOE sensitivity strongly dependent on discount rate and component cost assumptions [21]. Moller et al. further demonstrated that seasonal hydrogen storage enables complete off-grid self-sufficiency for prosumer systems in Germany and Finland, confirming the technology’s scalability across diverse climatic contexts [10]. Collectively, these studies establish that cost-optimal and resilience-optimal system designs diverge significantly as reliability constraints tighten. However, the specific reliability constraint level at which hydrogen storage transitions from an economic trade-off to an operationally necessary component, and whether PV-battery configurations can satisfy resilience-constrained operation under extended solar shortfall, has not been empirically examined under optimization-embedded stress conditions in any existing study.
1.1.2. Biogas-Integrated Hybrid Renewable Systems
Biogas-integrated hybrid microgrids have been evaluated across a range of scales, feedstock types, and geographic contexts. Nassereddine et al. demonstrated that a PV-biogas hybrid system maintains stable power supply during solar generation shortfalls without requiring additional storage, confirming the dispatchability advantage of biogas over weather-dependent renewables [22]. Mukhtar et al. optimized a PV-biogas-hydropower-battery system for a rural village in northwest Pakistan using HOMER Pro, achieving cost-effective electrification through multi-source dispatch; the study highlighted that biogas contributes disproportionately to system reliability relative to its generation share [23]. Ennemiri et al. optimized a PV-biogas-battery system for a commercial platform in Morocco, finding that biogas integration reduced CO₂ emissions by 40% relative to a biogas-only reference and that capital subsidies significantly affect economic viability [24]. Tiam Kapen et al. demonstrated the technical feasibility of a combined PV-battery-fuel cell-electrolyzer-biogas system in Cameroon using HOMER Pro, one of the few studies to integrate both biogas and hydrogen within a single hybrid configuration [25]. Despite these contributions, the architectural mechanism through which biogas dispatch restructures the entire optimal system design, reducing PV capacity, halving battery bank size, and shifting dispatch strategy, rather than simply adding generation capacity, has not been explicitly characterized. Furthermore, no existing study has integrated county-level livestock feedstock quantification with proportional community-scale downscaling for direct simulation input, maintaining methodological traceability from agricultural census data to system design parameters.
1.1.3. Geospatial Siting Frameworks for Hydrogen Systems
Geographic Information System (GIS) methods combined with multi-criteria decision analysis (MCDA) have been applied to renewable hydrogen facility siting in a growing body of literature. Messaoudi et al. developed a GIS-MCDA framework for solar hydrogen siting in Algeria, finding that only 0.49% of assessed land qualified as highly suitable under combined technical and environmental constraints, demonstrating the critical importance of spatially explicit screening over uniform deployment assumptions [26]. Rezaei et al. applied a hybrid wind-solar MCDA using HOMER and Fuzzy-TOPSIS to identify optimal hydrogen generation sites across 31 capital cities, demonstrating the tractability of multi-criteria spatial optimization at regional scale [27]. Fotsing Metegam et al. applied a GIS-based framework incorporating Monte Carlo simulation and fuzzy AHP to rank optimal sites for solar-wind hybrid hydrogen production in Cameroon, showing that probabilistic uncertainty handling substantially improves site ranking robustness over deterministic MCDA approaches [28]. While these studies demonstrate the value of spatially explicit siting, they address resource and technical feasibility exclusively, without incorporating community socioeconomic vulnerability as a co-equal criterion. The spatial coincidence of high energy burden and strong renewable resource potentially identifying communities where deployment is simultaneously most needed and most viable, has not been operationalized as a composite siting index in any prior hydrogen energy study. Frameworks that prioritize communities on social grounds alone risk selecting sites with weak resource bases; those that optimize on technical and economic grounds tend to bypass the communities most in need.
1.1.4. Microgrid Resilience Design and Stress Testing
Microgrid resilience, defined as the ability to maintain adequate load service during adverse operating conditions, has emerged as a distinct and increasingly prioritized design objective beyond conventional cost optimization [29,30]. Hirsch et al. reviewed resilience technologies and metrics for microgrids and concluded that conventional techno-economic studies systematically undervalue storage technologies by evaluating their performance under normal operating conditions rather than stress events, where storage transitions from a cost-optimization lever to a survival mechanism [31]. Khodaei et al. proposed a resilience-oriented planning framework for distribution microgrids that explicitly models extreme events, finding that multi-day outage survivability requires fundamentally different system architectures than those produced by LCOE minimization alone [32]. Panteli and Mancarella further articulated the conceptual distinction between reliability, which addresses routine contingencies, and resilience, which addresses low-probability high-impact events, arguing that resilience-oriented design requires dedicated planning methodologies rather than extensions of standard reliability optimization [29]. In the hydrogen microgrid literature, resilience evaluation has typically been conducted through post-hoc analytical scenarios applied to pre-optimized economic designs rather than embedded directly within the optimization process. This approach structurally fails to produce stress-hardened designs, because the optimizer has no incentive to size storage for survivability beyond the modeled normal-year conditions. An embedded, physics-grounded stress protocol that forces the optimizer itself to target survivability under defined worst-case conditions does not yet exist in the hydrogen microgrid literature.
1.2. Research Gaps and Contributions
The review above identifies a coherent and unaddressed macro-gap: no existing interdisciplinary optimization framework integrates equity-based spatial prioritization, resilience-constrained comparative evaluation, and hydrogen-biogas technology interaction characterization within a single community microgrid design methodology. This study addresses that gap by developing a spatially informed techno-economic and resilience optimization framework for hydrogen-biogas microgrid hybrid renewable energy storage in energy-burdened rural communities, applied to North Carolina as a representative case, through four integrated components: (i) spatial equity-based site prioritization using the Hydrogen Priority Index; (ii) local biogas resource quantification from county-level livestock census data; (iii) comparative hydrogen–biogas microgrid configuration assessment across four system architectures; and (iv) embedded seven-day solar shortfall stress testing within the HOMER Pro optimization year. The specific study objectives are: (i) to construct a Hydrogen Priority Index (HPI) combining socioeconomic vulnerability and multi-criteria technical suitability to identify priority deployment sites; (ii) to quantify community-scale biogas potential from livestock feedstocks and incorporate it into HOMER Pro optimization across different microgrid architectures under both economic and resilience constraints; and (iii) to evaluate the cost and resilience implications of hydrogen storage through an embedded solar shortfall protocol that forces resilience-aware optimization under identical boundary conditions across all configurations.
This study makes four principal novelty contributions: (a) the first composite siting index that operationalizes social equity and technical feasibility as co-equal criteria for hydrogen-biogas microgrid deployment, enabling site selection that cost-only approaches structurally cannot perform; (b) an embedded physics-grounded solar shortfall protocol that empirically identifies a configuration-level feasibility threshold under the modeled Robeson County conditions, beyond which hydrogen storage becomes the operationally necessary component for resilience-constrained performance; (c) a controlled four-scenario decomposition revealing the complementary rather than substitutable temporal roles of hydrogen storage and biogas dispatch; and (d) equity-oriented, planning-relevant insights for rural electrification in energy-burdened agricultural communities, with a replicable methodology transferable to analogous regions nationally and globally.
2. Material and Methods
2.1. Methodological Overview
Building on the literature reviewed in Section 1, the study asks how electrochemical hydrogen equipment and biogas-linked firm generation shift least-cost microgrid layouts and electricity service during stretched low-irradiance conditions, relative to a PV-battery baseline, for a fixed rural community load. County selection follows multi-criteria geospatial screening integrating energy burden and technical suitability [33]; biogas supply is quantified through livestock inventories and a standard manure-screening tool [34]; dispatch, hybrid renewable energy storage economics are optimized in HOMER Pro [13]. The solar resource uses a full hourly annual trace with an embedded seven-day reduced-GHI window, an explicit resilience stress protocol rather than an incidental modeling artifact.
The study proceeds in three phases. Phase 1 justifies Robeson County as the priority deployment site, quantifies livestock-linked biogas potential and HOMER Pro biomass inputs, and fixes the NSRDB solar node used across all scenarios. Phase 2 assembles the community load and solar series including the embedded low-GHI window and optimizes four microgrid configurations under shared economic and reliability constraints. Phase 3 compares configurations on cost outcomes and stress-period performance to identify the reference architecture under the defined criteria. All inputs are drawn from public geospatial, agricultural, meteorological, and catalog-based techno-economic sources.
2.2. Study Area and Community Load Profile
Robeson County, North Carolina, was selected as the representative case study based on the composite Hydrogen Priority Index (HPI) derived from the geospatial screening framework described in Section 2.2.1. The county, located in the southeastern coastal plain of North Carolina (approximately 34.75°N, 79.25°W), is home to approximately 42,509 households and ranks among the most energy-burdened jurisdictions in the state. A representative community of 200 households was defined to reflect a realistic off grid microgrid deployment scale consistent with rural electrification targets in underserved regions.
2.2.1. Geospatial Site Selection Framework
A two-stage GIS-based screening framework was developed to systematically identify priority locations for hydrogen microgrid deployment across North Carolina. The framework integrates spatially explicit socioeconomic vulnerability assessment with engineering-based technical suitability modeling, performed in ArcGIS Pro v3.5.0. The combined output - “Hydrogen Priority Index” identifies locations where high community energy vulnerability coincides with strong renewable energy potential and favorable infrastructure conditions.
Energy burden data at the census-tract level were obtained from the U.S. Department of Energy Low-Income Energy Affordability Data (DOE LEAD) dataset [8] and spatially joined to TIGER/Line census tract boundaries using the GEOID identifier [35]. Energy burden is defined as the percentage of gross household income allocated to residential energy expenditures. It was used as the primary indicator of energy vulnerability. To enable integration with engineering suitability scores; raw burden values were normalized using min-max scaling:
where EBI_i is the normalized Energy Burden Index for tract i, and EB_min and EB_max represent the statewide minimum and maximum values, respectively.
EBI_i = (EB_i − EB_min) / (EB_max − EB_min)
Global Moran's I was computed to assess spatial dependence in the EBI distribution (Appendix A.); results confirmed statistically significant clustering of high-burden tracts, supporting the use of spatially targeted rather than dispersed deployment strategies. Localized clusters of elevated energy burden were subsequently identified using Getis-Ord Gi* statistics; census tracts with a Gi* z-score exceeding 1.96 (p < 0.05) were classified as statistically significant hotspots, constituting the social prioritization layer for subsequent integration with the technical suitability assessment represented in the Figure 1.
Stage 2: Technical Suitability Modeling
Technical feasibility for hydrogen microgrid siting was evaluated through a Multi-Criteria Decision Analysis (MCDA) framework. Seven spatial criteria were selected to represent renewable resource potential, grid interconnection feasibility, constructability, and environmental constraints (Table 1).
Protected areas (PAD-US) were treated as hard exclusion zones and masked prior to suitability scoring. Surface water features were incorporated through Euclidean distance rasters, reflecting increased siting risk rather than categorical restriction. Each remaining criterion was reclassified to a standardized ordinal suitability scale (1-3), where higher values indicate greater suitability for photovoltaic-driven hydrogen systems.
Weights reflect engineering relevance, with solar irradiance prioritized highest (35%) for its direct influence on PV-driven hydrogen production, followed by transmission proximity (25%), land cover (15%), hydrological constraints (12%), road accessibility (10%), and substation proximity (3%). A Weighted Linear Combination (WLC) was applied to produce the continuous Suitability Score (SS) raster:
where xk is the standardized suitability score for criterion k and wk is its assigned weight. The weighted linear combination result, for North Carolina is represented in Figure 2 technical suitability map.
To assess the sensitivity of the county ranking to the expert-assigned weighting scheme, a supplementary equal-weight test was conducted in which six of the seven MCDA criteria were each assigned a weight of 14% and GHI was assigned 16%, producing a total of 100%. This integer-rounded uniform distribution was applied to the same score matrix used in the primary HPI calculation to determine whether the priority ranking is robust to the solar-irradiance-dominant weighting scheme in Table 1.
Hydrogen Priority Index. The Hydrogen Priority Index (HPI) was computed by multiplying the normalized tract-level EBI by the mean technical suitability score extracted to each census tract via Zonal Statistics and joined via the GEOID identifier:
where EBI_i ∈ [0,1] is the normalized Energy Burden Index and SS_i ∈ {0,1,2,3} is the ordinal technical suitability class assigned to census tract i. The multiplicative formulation therefore produces HPI values ranging from 0 to 3, where higher values indicate communities where both energy burden and renewable resource potential are simultaneously elevated. The resulting HPI was aggregated to the county level for ranking and case study selection represented in Figure 3.
HPI_i = EBI_i × SS_i
2.2.2. Community Load Profile and Data Collection
The community electrical load profile was derived from the U.S. Department of Energy Low-Income Energy Affordability Data (DOE LEAD) 2022 county-level dataset [8], filtered to prioritized Robeson County households at or below 60% of Area Median Income (AMI), the population segment most represented in the county's energy burden hotspot zones (Section 2.2.1). Unit-count-weighted electricity expenditure (ELEP×UNITS) and income (HINCP×UNITS) columns were used to compute household-level averages across tenure categories.
Average annual electricity consumption was derived by dividing the weighted expenditure ($1,690.89/household/year) by the Robeson County residential electricity rate ($0.1381/kWh) [36], yielding 12,243.95 kWh/household/year. Scaled to 200 households, this produces a community daily demand of 6,710 kWh/day and a peak of 829.8 kW, with a cohort energy burden of 10.78%, consistent with the county's elevated EBI. Derived load parameters are summarized in Table 2, and the resulting daily and seasonal profiles are shown in Figure 4.
A full 8,760-hour synthetic load profile was constructed by applying a residential diurnal demand shape to the daily average, capturing the characteristic evening peak between 18:00 and 22:00 in Figure 4. Seasonal scaling accounts for elevated summer cooling loads and a moderate winter heating baseline; the latter coincides with the period of lowest solar resource availability and represents the most operationally demanding condition for the microgrid (Figure 4). This profile was held constant across all four modeled configurations (S1–S4).
2.3. Biogas Resource Assessment
2.3.1. Feedstock Characterization, and Biogas Yield Estimation
Biogas potential for Robeson County was estimated using the U.S. EPA Anaerobic Digestion (AD) Screening Tool v2.5 [34], which applies ASABE D384.2-aligned manure characterization and volatile solids (VS)-based methane yield coefficients consistent with IPCC 2006 Guidelines (Vol. 4, Ch. 10) [37]. Livestock populations were obtained from the 2022 USDA NASS Census of Agriculture: 9,348,864 broiler chickens and 331,520 hogs and pigs [38]. The system was configured as a wet mesophilic anaerobic reactor, consistent with the lagoon-based manure management systems predominant in the county. Full feedstock characterization including moisture content, total solids, volatile solids, ash, nitrogen, and carbon fractions for each species and the weighted combined profile is provided in Supplementary Table S1.
The weighted combined C:N ratio of approximately 9:1 falls below the optimal 26-27.5:1 range for stable anaerobic digestion which is considered as an expected characteristic of nitrogen-rich poultry swine co-digestion [39]. Amendment with locally available corn stover (53,036 harvested acres in Robeson County) would correct this imbalance in a full-scale deployment [38]. Tool outputs are accordingly treated as conservative county-level resource estimates rather than design-grade projections.
County-level biogas production was estimated following the sequential volatile solids loading and biochemical methane potential approach described in the EPA AD Screening Tool v2.5 documentation, applying species-specific B₀ coefficients of 0.28 m³ CH₄/kg VS for broiler manure and 0.36 m³ CH₄/kg VS for swine per IPCC 2006 Guidelines (Vol. 4, Ch. 10, Table 10A) [37]. Total daily biogas volume was derived from the methane fraction using a volumetric CH₄ content of 0.59, calculated by the tool from feedstock composition, with a lower heating value of 5.5 MJ/kg and biogas density of 1.18 kg/m³, sourced from EPA AD Screening Tool v2.5 output for the configured feedstock mix [34]. Numerical results are reported in Section 3.2.
2.3.2. Community-Scale Downscaling for HOMER Pro Integration
County-level VS loading was back-calculated from the weighted VS fraction (19.7%) to total wet biomass, and a 70% collection recovery factor was applied to account for practical constraints on manure collectability from distributed farm operations. The recoverable county-level biomass (~6,772 t/day) was then allocated proportionally to the 200-household community based on Robeson County’s total household count (42,509) [3], yielding a daily community biomass availability of 31.86 t/day. At a generator electrical efficiency of 40% and LHV of 5.5 MJ/kg, this supports a continuous electrical output of approximately 72 kW. A rated generator capacity of 100 kW was entered into HOMER Pro with a minimum load ratio of 25% to accommodate partial-load dispatch flexibility during solar shortfall events.
In HOMER Pro, the biogas generator was modeled as a dispatchable fuel-based generator with a fixed daily biomass fuel availability of 31.86 t/day, entered as a fuel resource supply constraint rather than a must-run baseload. This dispatch architecture allows the optimizer to schedule generator output according to system load and renewable availability, enabling the biogas generator to respond to solar deficits rather than operating continuously at full capacity. The biomass fuel constraint ensures that total annual generator throughput does not exceed the resource ceiling derived from the county-scale livestock inventory, maintaining physical consistency between the resource assessment and the simulation model.
2.4. Solar Resource Assessment and Resilience Stress Protocol
2.4.1. Solar Resource
Hourly solar irradiance data for the study site (34.75°N, 79.25°W) were obtained from the NREL National Solar Radiation Database (NSRDB) [40]. The site records an annual average GHI of 4.45 kWh/m²/day, which is adequate for utility-scale PV deployment and consistent with the regional solar resource characteristic of the North Carolina coastal plain. December represents the most constrained solar month, with an average GHI of 2.36 kWh/m²/day and a clearness index of 0.498; the full monthly GHI and clearness index profile is provided in Supplementary Figure S1.
2.4.2. Embedded Resilience Stress Protocol
A key methodological contribution of this study is the development of an embedded, physics-based resilience stress protocol embedded directly within the HOMER Pro simulation year. Rather than evaluating resilience through post-hoc analytical scenarios, the approach modifies the NSRDB hourly GHI file to embed a defined solar shortfall event, forcing HOMER Pro’s optimizer to size each system configuration for survivability rather than cost minimization alone.
The stress scenario reduces hourly GHI values for seven consecutive days (December 25-31) to 10% of their recorded magnitudes, applied to each hourly W/m² value individually to preserve the natural diurnal shape while suppressing generation magnitude across the full 168-hour window. The original daily GHI range of 1.007-3.220 kWh/m²/day is reduced to 0.101-0.322 kWh/m²/day, yielding a 7-day mean of 0.223 kWh/m²/day, 8.3% of the December monthly mean [40]. This end-of-December placement coincides with the winter solstice minimum solar declination and shortest daylength at this latitude, producing the lowest clear-sky GHI ceiling of any week in the NSRDB annual record for Robeson County; the most adverse 7-day window available for stress testing. The duration constitutes a severe but physically plausible generation shortfall, enabling discriminating comparison of storage architectures under identical boundary conditions across all four configurations. The feasibility outcomes of this stress protocol across S1-S4 are reported in Section 3.4.
This protocol serves two functions: it produces inherently stress-hardened system designs, and it enables direct resilience comparison across configurations under identical solar input, load, and economic assumptions. The capacity shortage constraint was set to 0% for resilience runs and relaxed to 5% for economic runs, enabling structured quantification of the cost premium associated with resilience-constrained operation.
2.5. System Configurations and HOMER Pro Modeling
2.5.1. Scenario Definitions
HOMER Pro software; originally developed by NREL and later enhanced by UL Solutions integrates simulation, optimization, and sensitivity analysis to evaluate off-grid and grid-connected power systems, ranking them by net present cost (NPC) [13]. In this study, four microgrid configurations were developed and optimized in HOMER Pro v3.18.4. All scenarios share an identical solar resource file (with embedded reduced GHI), community load profile (section 2.2.2), optimization settings, and component cost database; the only variation between scenarios is component availability: S1 (PV + Battery): Baseline configuration with no dispatchable generation; represents the conventional approach to off-grid renewable microgrids. S2 (PV + Battery + Biogas): Introduces a biogas-fueled internal combustion generator as a dispatchable renewable resource to complement intermittent PV generation. S3 (PV + Battery + H₂): Introduces a PEM electrolyzer, compressed hydrogen storage tank, and PEM fuel cell for long-duration energy storage without dispatchable backup. S4 (PV + Battery + Biogas + H₂; Full Hybrid): Combines all generation and storage technologies to evaluate whether the synergy between biogas dispatch and hydrogen storage yields performance advantages beyond either technology in isolation. All the configurations are illustrated in Figure 5.
This comparative hybrid renewable energy storage optimization framework enables isolation of the marginal contribution of each technology. The progression from S1 to S4 traces the pathway from a cost-optimal but resilience-limited baseline to a fully resilience-hardened hybrid system. Each intermediate comparison isolates a specific technology contribution: S1→S2 quantifies the incremental value of biogas dispatch, S1→S3 isolates the effect of hydrogen storage in the absence of dispatchable backup, and S2→S4 reveals the marginal benefit of hydrogen when biogas is already present, enabling a structured decomposition of each technology's role.
2.5.2. Component Cost Parameters
All component costs are expressed in 2024 USD and were sourced from authoritative institutional and peer-reviewed references, including the NREL 2024 Annual Technology Baseline (ATB) [41], DOE Pathways to Commercial Liftoff: Clean Hydrogen (2023) [42], NREL H2A Production Analysis Tool[43], DOE 2023 Fuel Cell Technologies Market Report [44], IRENA Renewable Power Generation Costs 2022[45], and the EPA CHP Catalog[46]. Community-scale biogas generator costs were drawn from IRENA rather than the NREL ATB biopower figures, which reflect utility-scale dedicated biomass plants and are not applicable at the generator capacities modeled here. The full component cost summary is presented in Table 3; detailed component specifications including efficiency parameters, operating constraints, and size search spaces are provided in Appendix B.
2.5.3. Economic and Optimization Settings
Financial parameters follow NREL ATB 2024 [41] assumptions; the Robeson County residential electricity rate of $0.1381/kWh was applied as the grid reference price [36]. Sensitivity analyses were conducted across nominal discount rates of 5%, 6.5%, and 8%, combined with capacity shortage constraints of 0% and 5%, to evaluate cost and sizing robustness under varying financial and reliability conditions.
Both Load Following (LF) and Cycle Charging (CC) dispatch strategies were enabled, with the optimal dispatch selected endogenously by the optimizer for each scenario. The capacity shortage constraint was set to 0% for resilience-constrained runs and relaxed to 5% for economic optimization runs, enabling direct quantification of the cost premium associated with resilience-constrained operation. The optimizer selected 100 kW as optimal across all biogas-inclusive configurations, consistent with the community-scale feedstock ceiling derived in Section 2.3.2. All remaining economic and optimization parameters are reported in Appendix B (Table B.3).
The minor CO₂ emissions associated with biogas combustion in S2 and S4 (2,012-2,019 kg/yr) are classified as biogenic under standard lifecycle accounting conventions and do not affect the 100% renewable fraction reported by HOMER Pro, consistent with IPCC and EPA bioenergy accounting frameworks [46,47].
3. Results and Discussion
3.1. Spatial Prioritization and County Selection
Global Moran's I analysis confirmed statistically significant spatial clustering of high-burden tracts across North Carolina (I = 0.598, z = 65.65, p < 0.001) (Appendix A.), validating spatially targeted over dispersed deployment strategies. Getis-Ord Gi* hotspot analysis identified a contiguous zone of elevated vulnerability in the southeastern coastal plain, with secondary clusters in the south-central and western piedmont regions (Figure 1). The technical suitability map (Figure 2) shows the same southeastern coastal plain as the highest-scoring region for photovoltaic-driven hydrogen system deployment, driven by above-average solar irradiance, accessible transmission infrastructure, and predominantly agricultural land cover. This spatial coincidence is a key structural finding: the communities most in need of resilient energy access are located precisely where renewable-based microgrids are most viable. The HPI multiplicative formulation is designed to surface exactly this convergence. County-level aggregation of the normalized EBI and technical suitability score produced the priority index map (Figure 3) and identified the top five priority counties (Table 4).
Robeson County achieved the highest composite HPI (2.67), reflecting a near-maximum normalized energy burden (EBI = 0.89) and the highest ordinal suitability class (SS = 3), consistent with the HPI scale range of 0 to 3. Its maximum suitability score corresponds to strong solar resource quality, limited overlap with protected areas, accessible transmission corridors, and predominantly open agricultural land cover.
The robustness of this selection was confirmed through the equal-weight sensitivity test described in Section 2.2.1. Under the integer-rounded uniform weighting scheme (14% for six criteria, 16% for GHI), Robeson County retained the highest composite HPI score, driven by its simultaneous concentration of the maximum normalized EBI (0.89) and top-tier technical suitability score across all seven criteria. The second-tier group retained their relative positions, demonstrating that county selection reflects a genuine spatial concentration of energy vulnerability and renewable resource potential rather than an artifact of the weighting scheme.
The same agricultural economy contributing to the county's low-income profile generates the livestock feedstock underpinning the biogas resource quantified in Section 3.2: a co-location the HPI captures but cost-only siting approaches would not. The HPI provides a replicable middle path between social-only and technical-only siting, applicable across other states using publicly available DOE LEAD, NSRDB, NLCD, and PAD-US datasets.
3.2. Biogas Resource Estimation
Applying the AD Screening Tool [34] to Robeson County's livestock populations, daily VS loading was computed at 1,905,813 kg/day, dominated by broiler chicken manure, which accounts for 98.5% of total VS input. Daily biogas production reaches 506,394 m³/day at 59% CH₄ and 41% CO₂. Per-feedstock VS loading, methane yield coefficients, and individual biogas volumes are provided in Supplementary Table S2; county-level totals are reported here. At the county level, the direct biogas combustion pathway yields 708,837 MWh/year, equivalent to a continuous generation capacity of approximately 80.9 MW. The direct combustion pathway was adopted for HOMER Pro modeling in preference to upgraded biogas (RNG), avoiding gas-upgrading capital costs inappropriate at community-microgrid scale.
Following proportional downscaling to the 200-household community boundary (Section 2.3.2), recoverable biomass is 31.86 t/day, supporting a continuous electrical output of approximately 72 kW at 40% generator efficiency, with a rated capacity of 100 kW applied in HOMER Pro to accommodate partial-load dispatch. The biogas resource is thus established as a modestly scaled but dispatchable complement to PV generation, sufficient to sustain essential loads during solar shortfall but not sized to displace PV as the primary generation source. The biogas generator operated at a near-constant dispatch level throughout the year, consistent with the uniform daily biomass input, with modestly elevated output during December (~60 MWh/month) reflecting increased dispatch during the period of lowest solar generation.
3.3. Optimal System Architecture, Energy Production, and Technology-Specific Effects
Table 5 presents the consolidated system architecture and cost outcomes across all six modeled cases, four scenarios under the economic constraint (5% capacity shortage) and two under the resilience constraint (0% capacity shortage) for the hydrogen-inclusive configurations. Results are reported at the 6.5% baseline discount rate; the scenario schematic is shown in Figure 5, and LCOE and NPC comparisons are presented in Figure 6.
Table 6 highlights that PV dominates annual energy supply across all economic configurations, with battery discharge providing the primary overnight and overcast-day buffer. The biogas generator contributes approximately 618-620 MWh/yr in S2 and S4, substituting for a portion of both PV and battery capacity rather than supplementing them. Under the economic constraint, fuel cell output is marginal in both S3 and S4, confirming that hydrogen operates at the system margin when a 5% shortage allowance is permitted. Under the resilience constraint, the divergence between S3 (190.8 MWh/yr) and S4 (70.5 MWh/yr) fuel cell output reflects the biogas generator absorbing a substantial share of the S4 deficit that hydrogen alone must cover in S3, a distinction with direct cost implications explored in Section 3.4. Hourly battery dispatch heatmaps for all scenarios are provided in Appendix C.
The scenario ranking by LCOE is stable across the full discount rate range tested (5% - 8%); full sensitivity curves are provided in Supplementary Figure S2.
S2 consistently yields the lowest LCOE at all discount rates, S4 the second lowest among hydrogen-inclusive configurations, and S3 under the resilience constraint the highest in all cases.
The S4 resilience LCOE rises from $0.884/kWh at 5% discount to $1.077/kWh at 8%, a 21.8% range that is wider than the economic configurations, reflecting the capital-intensive nature of the resilience design. Critically, the feasibility boundary is discount-rate invariant: S1 and S2 remain infeasible at 0% shortage regardless of financial assumption, confirming that the threshold finding in Section 3.4 is a physical constraint rather than a cost artifact. The pattern of results reflects three distinct and physically interpretable architectural effects, each isolating the marginal contribution of a specific technology.
S1 → S2: Biogas as a system restructuring agent. The introduction of the biogas generator does not simply add a generation component; it reconfigures the entire optimal design. PV capacity falls by 1,343 kW (21.6%), the battery bank nearly halves from 11,231 to 5,791 strings, and the dispatch strategy shifts from Cycle Charging to Load Following. With dispatchable generation available, the optimizer no longer requires a large pre-charged battery bank to bridge overnight and low-generation periods, redirecting that capital into a leaner configuration. This collectively drives a 28.4% NPC reduction ($22.9M → $16.5M), the largest cost improvement of any single technology addition in this study. PV generation falls from 4,019 MWh/yr to 3,153 MWh/yr as the 619 MWh/yr biogas contribution displaces oversized solar capacity rather than supplementing it, confirming the substitution mechanism (Table 6). For rural communities with limited technical capacity, the simpler architecture may carry as much practical weight as the cost reduction in determining long-term project viability. The 28.4% NPC reduction exceeds cost savings reported for biogas-integrated rural hybrid systems in prior studies [22,23,24], confirming that the cost advantage of biogas integration is structural and architectural rather than a marginal generator addition, a distinction that single-criterion cost rankings cannot isolate.
S1 → S3: Hydrogen storage under economic constraint. Adding hydrogen storage alone produces minimal architectural change under the 5% shortage allowance: PV and battery size remain effectively unchanged, and the 50-kW fuel cell contributes only 16.6 MWh/yr, 0.3% of annual served energy. NPC rises modestly to $25.2M (LCOE: $0.684/kWh). Hydrogen in S3-economic operates at the system margin, sized as a supplementary seasonal buffer rather than a primary resilience mechanism. However, the moment the shortage tightens to zero, the system demands order-of-magnitude scaling across every hydrogen component, a gap no amount of PV or battery oversizing can close without hydrogen storage present. The 99.2% NPC increase from S3 economic to S3 resilience substantially exceeds premiums reported in smaller residential-scale studies, consistent with community-scale load placing qualitatively different demands on long-duration storage[17,20,21].
S2 → S4: Complementarity of biogas and hydrogen. The S4 economic configuration achieves the second-lowest NPC ($18.6M, LCOE: $0.503/kWh), below S1 despite incorporating both hydrogen and biogas hardware, by combining the architectural efficiency of biogas dispatch with a hydrogen subsystem sized for extended-event coverage. PV falls further to 4,374 kW and battery to 6,354 strings, the most capital-efficient economic design in the study. The annual energy data (Table 6) confirm the complementary roles: PV contributes 2,821 MWh/yr as the primary source, the biogas generator 620 MWh/yr as the dispatchable complement, battery discharge 1,056 MWh/yr for overnight bridging, and the fuel cell 16.9 MWh/yr as a marginal long-duration reserve, a four-source hierarchy in which each technology occupies a distinct temporal niche. Under the resilience constraint, the fuel cell contribution rises to 70.5 MWh/yr while the biogas generator sustains 600.8 MWh/yr unchanged, confirming that biogas absorbs routine deficits while hydrogen concentrates on extended stress events. The $13.0M saving of S4 over S3 at the resilience constraint demonstrates that biogas materially lowers the capital cost of achieving zero-shortage survivability through this complementary mechanism, one that cost-only optimization frameworks neither require nor reveal.
The 97.2% reduction in stress-period unmet load achieved by the full hybrid configuration has no directly comparable figure in any prior HOMER-based hydrogen microgrid study identified in this review, as existing studies do not embed stress events within the optimization year. The hydrogen component scaling magnitudes observed here, 20-fold fuel cell scaling from economic to resilience constraint in S3, and 5-fold tank scaling in both S3 and S4, substantially exceed the scaling ratios reported in smaller residential-scale studies [17,20], consistent with the community-scale load (829.8 kW peak) placing qualitatively different demands on long-duration storage than the single-household systems examined in those analyses. The S4 resilient LCOE of $0.962/kWh is high relative to grid reference but comparable to documented costs for diesel-based islanded community microgrids in remote rural settings [48], representing a meaningful benchmark when framed as the cost of weather-independent, resilience-constrained electricity service for 200 energy-burdened households.
3.4. The Hydrogen Feasibility Threshold and Stress Event Analysis
A central finding of this study is the identification of a configuration-level feasibility threshold under the modeled stress conditions: beyond a certain reliability requirement, hydrogen storage transitions from an economic trade-off to an operationally necessary component, a transition that PV-battery and PV-battery-biogas configurations could not satisfy under the imposed seven-day winter solar shortfall regardless of component scaling. Under the 0% shortage constraint, S1 and S2 are infeasible regardless of component scaling; no combination of PV and battery oversizing can eliminate unmet load during the embedded 25–31 December solar shortfall event. Only configurations incorporating hydrogen storage (S3 and S4) can satisfy this constraint. This is not a cost argument, it is a feasibility argument, and the distinction is consequential wherever energy system failure carries consequences beyond economic loss: medical equipment dependence, heating in extreme cold, water infrastructure, or food safety.
The resilience constraint requires a 5× increase in hydrogen tank capacity in both S3 and S4, from 500 kg to 2,500 kg, with corresponding fuel cell scaling of 20× in S3 (50 → 1,000 kW) and 10× in S4 (100 → 1,000 kW) (Table 5). These amplifications quantify the physical storage requirement of a seven-day severe overcast event at this latitude and load, an empirical characterization of the resilience threshold that standard cost-optimized HOMER studies, which do not embed stress events, cannot produce. The resilience cost premium for S4, the incremental NPC required to move from 5% to 0% shortage tolerance, is $18.6M (50.0%) (Table 9). This is most meaningfully framed as the insurance cost of full energy independence under worst-case winter conditions rather than as a cost penalty. The $13.0M saving of S4 over S3 at the resilience constraint, a 26% reduction is attributable to the biogas generator absorbing short-duration deficits, allowing hydrogen to concentrate exclusively on the extended stress event. For community planners and emergency preparedness agencies, the operative question is not which system has the lowest LCOE under normal conditions, but which system remains operational when conditions are not normal and at what cost. Most existing techno-economic studies of hydrogen microgrids compare LCOE values under normal operating conditions without subjecting configurations to defined stress events systematically understating hydrogen's value under infrequent but operationally catastrophic conditions [25]. The embedded stress protocol developed here provides a direct, reproducible answer and is transferable to other sites and stress scenarios without modification.
Figure 7a,b show the monthly energy dispatch for S4 under the economic (5%) and resilience (0%) constraints respectively, with the December stress period shaded in both. Under the economic constraint (Figure 7a), electrolyzer input peaks at approximately 6 MWh/month during May-June and tapers to near 1 MWh/month by December, reflecting reduced surplus PV generation. Hydrogen operates as a marginal seasonal buffer at this constraint level.
Under the resilience constraint (Figure 7b), the dispatch profile differs fundamentally in scale and December behavior. Electrolyzer input peaks at 27-29 MWh/month during spring and early summer, nearly five times the economic-case peak, as the larger PV array actively stores surplus generation as hydrogen in anticipation of the winter shortfall. In December, electrolyzer input collapses to approximately 5 MWh/month as surplus generation is diverted entirely to load service, and the fuel cell assumes the role of primary backup source throughout the stress window. The contrast between the two figures encapsulates the operational logic of the resilience design: summer surplus is the fuel for winter survivability, and hydrogen is the medium that bridges the two.
Figure 8 quantifies the resilience differential at hourly resolution during December 25-31. Panel A shows stored H₂ declining steadily from approximately 2,100 kg at the start of the stress window to near-zero by December 30-31, with the fuel cell discharging at up to 600 kW during peak demand hours. Panel B compares unmet load between S1 and S4 during the same window: S1 accumulates 37,879 kWh of unmet energy across the seven-day period, persistent and severe load curtailment concentrated in nighttime and early morning hours; while S4 accumulates only 1,078 kWh, a 97.2% reduction, concentrated in the final hours of December 30-31 as the hydrogen tank approaches depletion. The residual 1,078 kWh shortfall in S4 occurs in the final hours of the stress window as the hydrogen tank approaches depletion. The optimizer selected 2,500 kg as the cost-optimal tank size within a search space extending to 7,000 kg, indicating that larger tank configurations were available but not selected under the modeled cost and load assumptions. This residual shortfall represents 2.8% of total stress-period demand and does not diminish the primary finding: the S4 configuration served 97.2% of stress-period load without interruption, a level of resilience-constrained performance that PV-battery configurations could not approach under identical boundary conditions.
Figure 9 shows the monthly battery state of charge distribution for S3 and S4 under the resilience constraint. December SOC (highlighted in red) is substantially lower and more variable than the rest of the year in both scenarios, approaching the 20% minimum threshold during the stress window.
The interquartile range in S3 December is wider and the minimum lower than in S4, reflecting the absence of biogas dispatch in S3. Without the biogas generator absorbing overnight and multi-day deficits, the battery in S3 depletes more deeply before hydrogen dispatch is engaged, placing greater cumulative stress on electrochemical storage. This comparison makes visible the complementary temporal roles of biogas and hydrogen in a way that cost tables and architecture comparisons cannot: biogas protects the battery from routine deep cycling; hydrogen protects the system from events that exhaust both PV and battery reserves entirely. Under the resilience constraint, fuel cell contribution in S4 is 1.2% of annual served energy versus 2.6% in S3, the halving reflecting biogas absorbing the routine deficits that would otherwise require hydrogen dispatch, concentrating hydrogen on the extended stress event where it is operationally irreplaceable (Table 6). Full hourly SOC calendars for all scenarios under both constraint levels are provided in Appendix C.
3.5. Levelized Cost of Hydrogen
LCOH is reported here as a diagnostic metric characterizing hydrogen subsystem productivity within the community resilience function, not as an indicator of market-competitive hydrogen production. LCOH results are provided in Supplementary Table S3; key values are reported here. Under the economic constraint, S3 yields $1,753/kg H₂ and S4 yields $1,259/kg H₂; under the resilience constraint, both fall markedly to $282/kg H₂ and $605/kg H₂ respectively. The cost reduction is driven entirely by utilization scaling: the S3 resilience electrolyzer processes 524,694 kWh/yr versus 42,346 kWh/yr under the economic constraint, a 12.4× increase that spreads fixed capital cost across substantially more hydrogen output despite a larger overall system. This reflects a system sized for extended stress-event dispatch rather than marginal buffering.
These values exceed current green hydrogen benchmarks ($3-$8/kg at dedicated large-scale facilities) and are not positioned as competitive with standalone electrolysis. The operative evaluation metrics remain NPC and LCOE. S3 achieves the lowest LCOH ($282/kg) through aggressive electrolyzer scaling but at the highest NPC ($50.2M); S4's higher LCOH ($605/kg) reflects a system optimized for load-serving resilience, with biogas absorbing routine deficits and concentrating hydrogen dispatch on extended stress events. For energy-burdened communities, the relevant metric is the lowest cost per unit of resilience achieved, a distinction that consistently favors S4.
Projected DOE Hydrogen Shot cost trajectories ($1/kg by 2030) and IRA Section 45V Production Tax Credit eligibility applicable to energy communities including Robeson County ($3/kg H₂ offset) would compress the S4 resilience cost premium from 50% to an estimated 30-35% [42,44]. Under a 50% capital subsidy scenario, the S4 resilient NPC falls from $37.2M to approximately $18.6M, producing an effective LCOE of ~$0.48/kWh within reach of state-level rural affordability targets. These projections do not alter the feasibility threshold finding, which is constraint-driven rather than cost-driven, but substantially improve the investment case for resilience-oriented hydrogen microgrid deployment over the 2026-2032 horizon.
3.6. Limitations and Future Work
This study operates at pre-feasibility scale, where county-level aggregates and conservative resource estimates are the appropriate inputs; site-specific farm surveys, interval-metered load data, and engineering-grade feasibility assessments represent natural next steps as projects advance toward implementation. The resilience stress protocol is intentionally deterministic, centered on the physically worst solar week at the study latitude, providing a reproducible worst-case bound; extension to stochastic shortfall scenarios drawn from historical National Oceanic and Atmospheric Administration (NOAA) surface radiation and cloud cover records would complement this bound with probability-weighted survivability estimates. Component costs reflect 2024 benchmarks; the rapid PEM electrolyzer and fuel cell cost trajectories projected through 2030-2035 are expected to improve the competitive position of hydrogen-inclusive configurations relative to the baselines reported here. Finally, the HPI framework addresses technical and economic prioritization; integration of stakeholder acceptance, land tenure, and permitting layers would extend it toward a full deployment-readiness index, a direction that future work will pursue.
4. Conclusions
This study developed and demonstrated an integrated spatially informed interdisciplinary techno-economic and resilience optimization framework connecting geospatial equity prioritization, local renewable resource quantification, and resilience-constrained comparative system evaluation for hydrogen-biogas microgrid deployment in energy-burdened rural communities. The HPI framework identified Robeson County as the highest-priority deployment site in North Carolina by surfacing the spatial coincidence of high household energy burden and strong photovoltaic-biogas resource potential; a co-location that cost-only siting approaches would not detect. Biogas integration fundamentally restructured the optimal system architecture, reducing net present cost by 28.4% and nearly halving battery bank size relative to the photovoltaic-battery baseline, while the full hybrid configuration (S4) achieved resilience-constrained performance at $37.2M - $13.0M less than the hydrogen-only resilience design.
Under the modeled Robeson County load profile, component cost assumptions, HOMER Pro search space, and embedded seven-day winter solar shortfall protocol, hydrogen storage marks a feasibility threshold for achieving resilience-constrained operation that PV-battery and PV-battery-biogas configurations could not satisfy - reducing stress-period unmet energy by 97.2% compared to the PV-battery baseline. These findings reframe hydrogen storage in community microgrid design: within the modeled case study and stress-test assumptions, hydrogen storage provides the long-duration backup function that PV-battery and PV-battery-biogas configurations could not achieve under the resilience-constrained scenario, a distinction with direct implications for rural electrification policy, emergency preparedness planning, and equitable clean energy deployment in underserved regions. While numerical results are case-specific, spatial prioritization, biogas quantification, and resilience stress-testing methodology is transferable to analogous energy-burdened rural communities nationally and globally. Results are derived at pre-feasibility scale using county-level aggregates; site-specific surveys and interval-metered load data represent the natural next step toward engineering-grade implementation. By unifying equity-based spatial prioritization, resilience-constrained comparative system assessment, and hydrogen-biogas integration characterization within a single deployable interdisciplinary energy storage optimization framework, this study provides the methodological foundation for scaling resilience-oriented hydrogen microgrids to energy-burdened rural communities nationally.
Author Contributions
Sadia Jahan Noor: Conceptualization, Methodology, Software, Validation, Formal analysis, Resources, Data curation, Writing original draft, Writing review and editing, Visualization. Hyosoo Moon: Conceptualization, Methodology, Formal analysis, Investigation, Data curation, Writing original draft, Writing review and editing, Visualization, Supervision, Project administration. Raymond C. Tesiero: Conceptualization, Methodology, Supervision, Project administration. Seyedali Mirmotalebi: Methodology, Writing original draft, Writing review and editing.
Funding
This research was funded by the Center for Energy Research & Technology (C.E.R.T.) at North Carolina A&T State University.
Data Availability Statement
Acknowledgments
This material is based upon work supported by the Center for Energy Research & Technology (C.E.R.T.) at North Carolina A&T State University.
Declaration: of Generative AI and AI-Assisted Technologies in the Manuscript Preparation Process.
During the preparation of this work, the authors used Claude (Anthropic) to support language refinement, structural editing, and title and abstract optimization; Grammarly for grammar and readability checking; and SciSpace for literature navigation and reference organization. All AI-assisted outputs were critically reviewed, substantially edited, and verified by the authors. The authors take full responsibility for the scientific content, data integrity, analytical conclusions, and all aspects of the published article.
Conflicts of Interest
The authors declare no conflicts of interest.
Appendix A.
Spatial Autocorrelation: Moran's I Formulation
Global Moran's I was applied to evaluate spatial dependence in the normalized Energy Burden Index (EBI) distribution across North Carolina census tracts. The statistics are defined as:
where n = number of spatial units; = spatial weight between tracts i and j; xi = EBI value for tract i; x̄ = mean EBI; W = sum of spatial weights. A queen contiguity weights matrix was applied, defining spatial neighbors as all tracts sharing a common boundary point or edge. Statistical significance was assessed via z-score under the randomization assumption. The analysis was performed in ArcGIS Pro using the Spatial Autocorrelation (Global Moran's I) tool. Results yielded I = 0.598, z = 65.65, p < 0.001, confirming statistically significant positive spatial clustering of high energy burden tracts across the state.
Figure A1.
Global Moran's I Output: ArcGIS Pro Spatial Autocorrelation Report.

The bell curve output (Figure A1) generated by ArcGIS Pro Spatial Autocorrelation tool shows the observed Moran's Index of 0.598 positioned in the far-right tail of the distribution (z = 65.65, p < 0.001), well beyond the critical threshold of ±2.58. The red-shaded clustered panel confirms that the spatial pattern of high energy burden across North Carolina census tracts is statistically significant and clustered rather than random or dispersed, validating the use of spatially targeted deployment strategies in this study.
Table A1.
Component Technical Specifications and Size Search Space.
| Component | Key Technical Parameters | Size Search Space |
| Solar PV (Generic Flat Plate) | Derating factor: 80%; Fixed tilt: 34.64°; Ground reflectance: 20% |
HOMER Optimizer™ |
| Li-Ion Battery (Generic 1 kWh) | Roundtrip efficiency: 90%; Min SOC: 20%; Initial SOC: 100%; Nominal: 6V, 1 kWh (167 Ah) |
HOMER Optimizer™ |
| PEM Electrolyzer (Generic) | Efficiency: 85%; Min load ratio: 0% | 50; 100; 200; 400; 1,000 kW |
| Compressed H₂ Tank (Generic) | Initial level: 20% of tank size | 500; 1,000; 5,000; 7,000; 2,500, kg |
| PEM Fuel Cell | Fuel: stored hydrogen; LHV: 120 MJ/kg; Intercept: 0.0010 kg/hr/kW; Slope: 0.0600 kg/hr/kW; Effective efficiency: ~49% at rated capacity; Min load ratio: 10% | 50; 100; 200; 400; 1,000 kW |
| Biogas Generator (BIO.GEN) | Fuel: biogas; LHV: 5.5 MJ/kg; Density: 1.18 kg/m³; Intercept: 0.1063 kg/hr/kW; Slope: 1.5199 kg/hr/kW; Peak efficiency: ~40% at rated capacity; Min load ratio: 25%; |
25; 63; 100 kW |
| Converter (System Converter) | Inverter efficiency: 95%; Rectifier efficiency: 95%; Rectifier relative capacity: 80% | HOMER Optimizer™ |
Table A2.
Controller and Dispatch Settings.
| Parameter | Value |
| Cycle Charging (CC) setpoint SOC | 80% |
| Allow generators to operate simultaneously | Enabled |
| Allow generator capacity less than peak load | Enabled |
| Battery lifetime constraint | 15 yr or 3,500 kWh throughput; whichever first |
Table A3.
HOMER Pro Economic and Optimization Parameters.
| Parameter | Value |
| Project lifetime | 25 years |
| Nominal discount rate | Baseline 6.5% (sensitivity: 5%, 8%) |
| Inflation rate | 2.50% |
| Real discount rate | 3.90% |
| Grid electricity price | $0.1381/kWh |
| Dispatch strategy | LF and CC (optimizer-selected) |
| Capacity shortage constraint | 0% (resilience) / 5% (economic) |
| Minimum renewable fraction | 30% |
| Operating reserve | 10% load + 10% PV output |
| Simulation timestep | 60 min (8,760 steps/yr) |
| Biogas generator capacity | 100 kW |
Solar PV, battery, and converter capacities were optimized continuously using the HOMER Optimizer™ algorithm. The biogas generator search space included three options (25, 63, 100 kW); the optimizer selected 100 kW in all biogas-inclusive configurations, consistent with the community-scale feedstock ceiling (Section 2.3.2). The optimal H₂ tank capacity under the resilience constraint (2,500 kg) lies within the search space and does not represent the search ceiling (7,000 kg), confirming the optimizer was not artificially bounded. Fuel cell and electrolyzer efficiencies are derived from HOMER Pro fuel curve parameters, not directly entered. Biogas combustion CO₂ emissions are classified as biogenic under IPCC and EPA accounting conventions and do not affect the 100% renewable fraction reported by HOMER Pro.
Appendix C.
Battery State of Charge Calendar Heatmap of All Scenarios
Figure C1 displays hour of day (vertical axis, 0-24h) versus simulation day (horizontal axis, Days 1-365); color scale indicates SOC (%) from 0% (dark navy) to 100% (light teal). The dark band at Days 355-365 in resilience-constrained panels corresponds to the embedded December solar shortfall period. S1 and S2 are presented under the economic constraint only, as both are infeasible under the zero-shortage constraint.
Figure C1.
Battery State of Charge Calendar Heatmap: All Scenarios, Economic (5% Shortage) and Resilience (0% Shortage).
Figure C1.
Battery State of Charge Calendar Heatmap: All Scenarios, Economic (5% Shortage) and Resilience (0% Shortage).

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Figure 1.
Energy Burden Hotspot Map - Gi Analysis, North Carolina*.

Figure 2.
Technical Suitability Map - Weighted Linear Combination Result, North Carolina.

Figure 3.
Hydrogen Priority Index Map -Census Tract Level, North Carolina.

Figure 4.
(a) Daily, and (b) Seasonal Hourly Community Load Profile for 200 Households, Robeson County.
Figure 4.
(a) Daily, and (b) Seasonal Hourly Community Load Profile for 200 Households, Robeson County.

Figure 5.
Schematic Diagram of the Four Modeled Microgrid Configurations (S1-S4).

Figure 6.
LCOE and NPC Comparison of All Scenarios, Economic vs. Resilience Constraint.

Figure 7.
Monthly Energy Dispatch of S4, (a) economic, and (b) Resilience Constraint.

Figure 8.
25–31 December Solar Stress Event; Panel A: Stored H₂ and Fuel Cell Output, S4; Panel B: Hourly Unmet Load, S1 vs. S4.
Figure 8.
25–31 December Solar Stress Event; Panel A: Stored H₂ and Fuel Cell Output, S4; Panel B: Hourly Unmet Load, S1 vs. S4.

Figure 9.
Battery SOC Monthly Distribution of S3 and S4, resilient case.

Table 1.
MCDA Suitability Criteria, Scoring Logic, Data Sources, and Assigned Weights.
| Criterion | Data Source | Standardization | Suitability Logic | Weight (%) |
| Solar Global Horizontal Irradiance | NSRDB v3 | Continuous → reclassified | Higher irradiance = higher suitability | 35 |
| Distance to Transmission Lines | NC Transmission Lines shapefile | Euclidean distance → reclassified | Closer = higher suitability | 25 |
| Land Cover | NLCD 2019 | Categorical reclassification | Grass/crops/barren = high; forest/urban = low | 15 |
| Distance to Water Bodies | NHD Hydrography | Euclidean distance → reclassified | Farther = higher suitability | 12 |
| Distance to Roads | TIGER/Line Roads | Euclidean distance → reclassified | Closer = higher suitability | 10 |
| Distance to Substations | US Electric Substations shapefile | Euclidean distance → reclassified | Closer = higher suitability | 3 |
| Protected Areas | PAD-US | Binary mask | Excluded from analysis | Masked |
Table 2.
Community Load Parameters - Robeson County, DOE LEAD 2022, ≤60% AMI).
| Parameter | Value |
| Avg annual electricity cost/household | $1,690.89/yr |
| Avg annual consumption/household | 12,243.95 kWh/yr |
| Community daily demand (200 households) | 6,710 kWh/day |
| Peak demand | 829.8 kW |
| Energy burden (≤60% AMI cohort) | 10.78% |
Table 3.
HOMER Pro Component Cost Parameters.
| Component | Capital Cost | Replacement Cost | Fixed O&M* | Lifetime |
| Solar PV | $1,551/kW | $1,551/kW | $21.61/kW-yr | 30 yr |
| Li-Ion Battery (1 kWh) | $484.55/unit | $484.55/unit | $11.06/unit-yr | 15 yr |
| PEM Electrolyzer | $2,000/kW | $1,800/kW | $200/kW-yr | 15 yr |
| Compressed H₂ Tank | $1,500/kg | $1,300/kg | $150/kg-yr | 25 yr |
| PEM Fuel Cell | $3,000/kW | $2,700/kW | $0.034/op.hr | 50,000 hr |
| Biogas Generator | $1,500/kW | $1,350/kW | $0.025/op. hr | 20,000 hr |
| Converter | $985/kW | $887/kW | $98/kW-yr | 20 yr |
* Fuel cell and biogas generator O&M expressed per operating hour consistent with dispatchable generator convention; all other O&M values are fixed annual costs per unit capacity. Full component specifications are provided in Appendix B.
Table 4.
Top Five Counties by Hydrogen Priority Index - North Carolina, USA.
| Rank | County | HPI | EBI | Suitability Score |
| 1 | Robeson | 2.67 | 0.89 | 3 |
| 2 | Johnston | 2.33 | 0.78 | 3 |
| 3 | Scotland | 2.33 | 0.78 | 3 |
| 4 | Cleveland | 2.33 | 0.78 | 3 |
| 5 | Anson | 2.00 | 0.67 | 3 |
HPI = EBI × SS; maximum possible HPI = 3.00 where EBI = 1.0 and Suitability score = 3.
Table 5.
Optimal System Architecture by Scenario at Baseline 6.5% nominal Discount rate.
| Metric | S1 | S2 | S3 | S4 | ||
| Economic 5% C.S. | Economic 5% C.S. | Economic 5% C.S. | Resilient 0% C.S. | Economic 5% C.S. | Resilient 0% C.S. | |
| PV Capacity (kW) | 6,230.63 | 4,888.34 | 6,117.16 | 8,501.35 | 4,373.76 | 6,526.05 |
| Battery (strings) | 11,231 | 5,791 | 11,387 | 16,912 | 6,354 | 11,094 |
| Fuel Cell (kW) | N/A | N/A | 50 | 1000 | 100 | 1000 |
| Electrolyzer (kW) | N/A | N/A | 50 | 1000 | 50 | 200 |
| H₂ Tank (kg) | N/A | N/A | 500 | 2500 | 500 | 2500 |
| Biogas Generator (kW) | N/A | 100 | N/A | N/A | 100 | 100 |
| Converter (kW | 725.85 | 606.03 | 752.42 | 871.76 | 658.07 | 678.58 |
| Dispatch Strategy | CC | LF | LF | LF | LF | LF |
| NPC ($M) | 22.9 | 16.5 | 25.2 | 50.2 | 18.6 | 37.2 |
| LCOE ($/KWh) | 0.620 | 0.444 | 0.684 | 1.301 | 0.503 | 0.962 |
| Operating Cost ($/yr) | 448,047 | 337,711 | 538,375 | 1,220,165 | 431,680 | 867,977 |
| Unmet Load (%) | 4.45 | 4.18 | 4.41 | 0.07 | 4.22 | 0.05 |
| Renewable Fraction (%) | 100 | 100 | 100 | 100 | 100 | 100 |
Economic = 5% capacity shortage; Resilient = 0% capacity shortage. S1 and S2 are infeasible under the 0% shortage constraint. All values at 6.5% nominal discount rate. CC = Cycle Charging; LF = Load Following.
Table 6.
Annual Energy Production by Source of All Scenarios.
| Scenario | Constraint |
PV (MWh/yr) |
Battery discharge (MWh/yr) |
Fuel cell (H2) (MWh/yr) |
Biogas (MWh/yr) |
| S1 | Economic 5% | 4,018.75 | 1,694.58 | - | - |
| S2 | Economic 5% | 3,152.98 | 1,069.00 | - | 618.43 |
| S3 | Economic 5% | 3,945.57 | 1,678.53 | 16.578 | - |
| Resilient 0% | 5,483.37 | 1,595.69 | 190.813 | - | |
| S4 | Economic 5% | 2,821.08 | 1,055.86 | 16.929 | 620.09 |
| Resilient 0% | 4,209.30 | 1,101.90 | 70.522 | 600.82 |
Dashes indicate technologies, absent in that configuration. All values at 6.5% nominal discount rate.
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