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Design Implications of Headspace Ratio VHS/Vtot on Pressure Stability, Gas Composition and Methane Productivity in Batch Anaerobic Digesters

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06 November 2025

Posted:

07 November 2025

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Abstract
Headspace (HS) in anaerobic batch biodigesters is a critical design parameter that modulates pressure stability, gas–liquid equilibrium, and methanogenic productivity. This systematic review, guided by PRISMA 2020, analyzed 84 studies published between 2015 and 2025, of which 64 were included in the qualitative and quantitative synthesis. The interplay between headspace volume fraction VHS/Vtot, operating pressure, and normalized methane yield was assessed, explicitly integrating safety and instrumentation requirements. In laboratory settings, maintaining a headspace volume fraction (HSVF) of 0.30-0.50 with continuous pressure monitoring P(t) and gas chromatography reduces volumetric uncertainty to below 5-8% and establishes reference yields of 300-430 NmL CH4 gVS⁻¹ at 35 °C. At pilot scale, operation at 3-4 bar absolute increases the CH4 fraction by 10-20 percentage points relative to ~1 bar, while maintaining yields of 0.28-0.35 L CH4 gCOD⁻¹ and production rates of 0.8-1.5 Nm³ CH4 m⁻³ d⁻¹ under OLRs of 4-30 kg COD m⁻³ d⁻¹, provided pH stabilizes at 7.2-7.6 and the free NH3 fraction remains below inhibitory thresholds. At full scale, gas domes sized to buffer pressure peaks and equipped with continuous pressure and flow monitoring feed predictive models (AUC > 0.85) that reduce the incidence of foaming and unplanned shutdowns, while integration of desulfurization and condensate management keep corrosion at acceptable levels. Rational sizing of HS is essential to standardize BMP tests, correctly interpret the physicochemical effects of HS on CO2 solubility, and distinguish them from intrinsic methanogenesis. We recommend explicitly reporting standardized metrics (Nm³ CH4 m-³ d-¹, NmL CH4 gVS-¹, L CH4 gCOD-¹), absolute or relative pressure, HSVF, and the analytical method as a basis for comparability and coupled thermodynamic modeling.
Keywords: 
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Subject: 
Engineering  -   Bioengineering

1. Introduction

Batch anaerobic digestion (AD) has become an essential tool in research on the valorization of agro-industrial organic waste, allowing for the evaluation of biodegradability and biochemical methane potential (BMP) of different substrates under controlled conditions (Y. Liu et al., 2024). In these systems, the biodigester is loaded only once with substrate and inoculum and hermetically sealed during the fermentation period, enabling the production and accumulation of biogas without continuous feeding or discharge (Mekwichai et al., 2024). Although this operating scheme simplifies control and promotes experimental reproducibility, it introduces a frequently underestimated design parameter: headspace (HS), defined as the gas volume available above the liquid phase of the reactor (Hmaissia et al., 2025).
The HS (hybrid storage) plays critical roles that go beyond mere gas accumulation. From a physicochemical perspective, it regulates internal pressure, gas solubility, and the equilibrium between the liquid and gas phases (CO2, CH4, H2S, NH3), all of which are governed by Henry's law and operating conditions (Liao et al., 2025). A large gas volume buffers pressure variations and facilitates sampling, but it can induce excessive CO₂ outgassing, raise the pH, and alter the carbonate-bicarbonate equilibrium, increasing the risk of inhibition by free ammonia in nitrogen-rich substrates. Conversely, a reduced HS increases the partial pressure of gases, promotes their dissolution in the liquid phase, and can alter mass transfer kinetics and biogas composition (Mihi et al., 2024). This complex balance makes the HS a direct determinant of the efficiency, stability, and safety of the anaerobic process (Wani & Parveez, 2025).
The design of the HS varies substantially depending on the scale and purpose of the reactor (Raposo et al., 2020). In laboratory BMP tests, volume fractions of 30-50% are typically used to ensure stable pressure and facilitate correction of measurements to standard conditions (Filer et al., 2019). In contrast, in pilot or industrial digesters, the HS is maintained between 10-25%, incorporating flexible domes or external gasometers that dampen pressure spikes and reduce structural risks (Stan et al., 2018). However, there is no consensus on the optimal sizing, as the physicochemical conditions, substrate composition, and agitation regimes nonlinearly alter the gas-liquid interaction and the volumetric methane yield (Naji et al., 2024).
Recent literature shows a growing interest in quantitatively modeling the effects of HS. Extensions of the ADM1 model (Anaerobic Digestion Model No.1) have explicitly incorporated the gas phase, demonstrating that variations in HS pressure modify pH dynamics, CO₂ solubility, and the availability of volatile intermediates (Catenacci et al., 2024). This approach has allowed correlation of the fraction V H S / V t o t with methane yield and reactor stability parameters, opening the possibility of optimizing the design through coupled thermodynamic simulation (Karsten et al., 2025). However, the lack of a comparative systematization of scales, operating strategies, and quantitative results limits the ability to extrapolate conclusions and standardize experimental protocols (Li et al., 2025).
Therefore, this review proposes a comprehensive and comparative synthesis of HS behavior in batch biodigesters. Verifiable evidence on the effects of headspace volume fraction, pressure, and methane production on operational safety is compiled and analyzed to identify quantitative patterns and design criteria that support modeling and scale-up of anaerobic digestion systems. In this way, the work seeks to bridge the gap between empirical practice and theoretical-predictive foundations, providing a robust scientific basis for the rational design of more efficient and sustainable biodigesters.

2. Systematic Review Methodology

This review was developed following the guidelines of the PRISMA 2020 protocol (Preferred Reporting Items for Systematic Reviews and Meta- Analyses) (Yepes-Nuñez et al., 2021), with the purpose of ensuring transparency, reproducibility and traceability in the collection, selection and analysis of scientific literature related to the design, operation and modeling of headspace in batch biodigesters.

2.1. Search Strategy and Databases

The literature search was conducted between July and September 2025 in Scopus and PubMed. Search equations were designed a priori, combining controlled descriptors and free terms with Boolean operators, aimed at capturing studies on anaerobic digestion and the influence of headspace on biogas generation and measurement. The search equations combined keywords and Boolean operators under the general format:
For Scopus
(“anaerobic digestion” OR “biochemical methane potential” OR “BMP test”) AND (“headspace” OR “gas phase” OR “gas volume ratio” OR “VHS /Vtot ”) AND (“biogas yield” OR “methane production” OR “pressure” OR “CO₂ solubility” OR “gas-liquid equilibrium”).
For PubMed
("anaerobic digestion"[Title/Abstract] OR "biochemical methane potential"[Title/Abstract] OR "BMP test"[Title/Abstract])AND ("headspace"[Title/Abstract] OR "gas phase"[Title/Abstract] OR "gas volume ratio"[Title/Abstract] OR "Vhs/Vtot"[Title/Abstract])AND ("biogas yield"[Title/Abstract] OR "methane production"[Title/Abstract] OR "pressure"[Title/Abstract] OR "CO2 solubility"[Title/Abstract] OR "gas-liquid equilibrium"[Title/Abstract])
To maximize coverage, we included synonyms for headspace (e.g., “gas cap,” “gas volume,” “gas retention zone”) and terms related to reactor scale (lab scale, pilot scale, industrial scale). No geographical or language restrictions were applied, although peer-reviewed articles in English and Spanish were prioritized.

2.2. Inclusion and Exclusion Criteria

Inclusion criteria:
  • Peer-reviewed scientific articles published between 2015 and 2025.
  • Experimental, comparative or modeling studies that explicitly report the headspace fraction ( V H S / V t o t ) or related parameters (pressure, gas volume, CH4 yield).
  • Publications that present verifiable data on pressure, temperature, volume or composition of biogas.
  • Book reviews or chapters with active DOI and verifiable access.
Exclusion criteria:
  • Documents without quantitative information related to headspace: absence of (VHS/Vtot), volume/gas phase ratio, measured pressure, or its impact on biogas/methane yield.
  • Theses, technical reports or grey literature without peer review or verifiable DOI/URL, or without access to the full text.
  • Duplicate records or studies with verifiable inconsistencies between text, tables and/or figures (e.g., discrepancies in ( V H S / V t o t ), pressure or units).
  • Studies evaluating aerobic digestion, composting, nitrification/denitrification, photofermentative processes, oxy-fermentations, or other non-anaerobic technologies; or anaerobic studies that do not address the measurement or effect of headspace on pressure, gas–liquid equilibrium, or CH4 yield.

2.3. Study Selection Process

The search strategy identified 416 records: Scopus (n = 388), PubMed (n = 24), and a manual search in Google Scholar (n = 4). After initial cleaning (duplicate removal and first screening by title), 272 references were submitted for evaluation. At this stage, 131 were excluded for thematic irrelevance, and 13 additional duplicates were removed, leaving 115 for screening by abstract (Figure 1).
In the abstract review, 157 records were excluded for not meeting the required methodological and reporting criteria, leaving 64 articles to proceed to full-text evaluation. In this eligibility phase, 51 studies were excluded for the following reasons: they were not experimental or did not explicitly report the headspace fraction ( V H S / V t o t ) or related parameters (pressure, gas volume, CH4 yield ) (n = 21); they lacked verifiable data on pressure, temperature, volume, or biogas composition (n = 23); or they were reviews/chapters without an active DOI or verifiable access (n = 7). Finally, 64 studies were included in the qualitative and quantitative synthesis.
The diagram details the identification, screening, eligibility, and inclusion phases, with the counts at each stage and the reasons for exclusion in full text, in accordance with PRISMA 2020. The flow documents the transition from 416 initial records to 64 included studies.

2.4. Data Extraction and Validation

The following quantitative and operational parameters were extracted from each selected publication:
  • Scale and type of reactor (BMP, laboratory, pilot, industrial).
  • Primary substrate type.
  • Volumetric fraction of headspace ( V H S / V t o t ).
  • Operating pressure and temperature.
  • Biogas monitoring method (GC, NDIR, flow meters).
  • Specific methane production (mL CH₄·g-1 VS or L CH₄·L-1·d-1).
  • Reactor material and type of agitation.
The data were verified by cross-referencing the numerical information with the original sources and their DOIs. In the case of ranges or values reported under non- standard conditions, they were normalized to 101.3 kPa and 0 °C to ensure comparability of the results.

2.5. Analysis and Synthesis of Information

A mixed-methods approach was used, combining narrative synthesis and quantitative analysis. Studies were grouped by scale of operation and substrate type, among other relevant variables. The verified data were structured in comparative matrices, and the effects of headspace fraction V H S / V t o t and operating pressure on methanogenic yield were analyzed to interpret the influence of headspace on CO2 solubility. Finally, the review was supplemented with safety considerations, given their impact on the design and operation of biodigesters.

2.6. Limitations of the Review

Despite the rigorous application of the PRISMA protocol, it is acknowledged that the available literature exhibits heterogeneity in the way headspace volume, internal pressures, and gas correction conditions are reported. Some studies lack unit standardization or sufficient information to calculate the ratio V H S / V t o t .
However, the convergence of multiple experimental sources and reviews made it possible to identify consistent trends that support the proposed ranges and the predictive equation presented in section 7.

3. Technical Fundamentals of Headspace

In batch-operated biodigesters, the HS constitutes the gaseous phase confined above the liquid digestion phase and plays a crucial role in the thermodynamics, gas-liquid mass transfer, acid-base equilibria, and operational safety of the system. From a macroscopic perspective, the internal pressure results from the accumulation of gas moles according to the equation of state, while at the species level, partial pressures regulate solubility equilibria and the direction of transfer flows. These interactions are modulated by temperature, reactor geometry, the volumetric ratio of HS to the total volume, and venting and storage strategies. Table 1 synthesizes the key physicochemical parameters, design relations, and safety considerations, with primary references; their relevance to design and operation is discussed below.
Batch biodigesters with moderate pressures and under mesophilic or thermophilic conditions, the gas behavior can approximate that of an ideal gas, such that the pressure P in the HS satisfies PVHS = ngRT, where ng is the total moles accumulated, VHS is the HS volume, and T is the temperature (Awasthi et al., 2023). This relationship reveals the buffering role of a sufficiently large VHS: for the same biogas production pulse, the pressure increase is smaller than the larger VHS is, which reduces the risk of overpressure and improves the repeatability of measurements. This effect can be expressed as a gaseous “capacitance” Ce = (∂ng/∂P )T = VHS/(RT), which increases linearly with VHS and T; in systems with domes or flexible gasometers, the elasticity of the container increases the effective capacitance, attenuating pressure spikes (Siciliano et al., 2021). However, the reduction of partial pressure by frequent venting or operation at low backpressure favors the shift of the gas-liquid equilibrium towards the gas phase, intensifying the stripping of volatile acid species.
Dalton’s law allows the total biogas pressure to be partitioned into partial pressures, Pi = yi P. Combined with Henry’s law, this enables quantification of the solubility of gases such as CO2 and H2S, expressed as C i * = P i / H i ( T ) . The Henry constant Hi(T) decreases with temperature following a van’t Hoff-type relationship, d ( l n H ) / d ( 1 / T ) Δ H s o l / R ; consequently, under thermophilic conditions, the lower solubility of CO2 and H2S increases their volatility, altering the biogas composition and the acid–base status of the liquid digestion phase. For ammonia, gas-liquid partitioning depends on the N H 4 + / NH3 equilibrium, whose pKa ≈ 9.25 at 25 °C and decreases with temperature. Therefore, increases in pH and T raise the fraction of free NH3, entailing a greater risk of biological inhibition (Gao et al., 2023). These interactions are modulated by the carbonate system, characterized by pKa1 ≈ 6.35 and pKa2 ≈ 10.33 (Meybodi et al., 2024). CO2 stripping tends to raise pH and effective alkalinity, shifting the CO2(aq)- H 2 C O 3 - H C O 3 - C O 3 2 equilibria. Although this phenomenon can contribute to deacidification during the initial phase of acidogenesis, it also increases the fraction of free NH3 and, depending on pH, alters reduced-sulfur speciation (H2S/HS-), with implications for both biological toxicity and system corrosion (Tzenos et al., 2023).
From a design perspective, the volumetric ratio V H S / V t o t represents a fundamental compromise between operational safety, gas metrology, and the structural compactness of the biodigester. In laboratory systems, such as BMP bottles and experimental reactors, typical ratios between 0.30 and 0.50 are recommended to facilitate sampling and prevent overpressures, always correcting biogas volumes to standard conditions and discounting water vapor according to guidelines such as VDI 4630 and equivalent methodological consensus (Strömberg et al., 2014). At pilot and farm scales, internal ratios of 0.10 to 0.25 are commonly used, complemented by domes or flexible storage systems that increase the effective gas capacitance C e = V H S / ( R T ) , providing mechanical damping and reducing pressure fluctuations (Scarlat et al., 2018). The reactor geometry, particularly the height-to-diameter ratio and the arrangement of baffles, along with the nature of the materials, influences the hydrodynamics, foam formation, and selective permeability to trace compounds. In this context, materials such as stainless steel, fiberglass reinforced plastic (FRP) and EPDM/PTFE elastomer membranes are selected for their chemical compatibility against acid gases such as H2S and volatile bases such as NH3, although permeability, thermal resistance and UV radiation aging must be considered, factors that directly affect the durability of the system (Situmorang et al., 2020).
In terms of safety, the sizing and certification of relief valves must ensure that the setpoint remains below the design pressure P d e s i g n , with controlled biogas flow to flares, consumers, or venting systems, and the incorporation of backflow prevention devices to avoid flame flashbacks, in accordance with NFPA (2021) and ATEX Directive 2014/34/EU (2014). Similarly, environmental monitoring of H₂S and CH4, proper condensate management, and early desulfurization through biological oxidation, adsorption on ferric oxides, or chemical scrubbing are effective strategies for mitigating occupational risks and reducing corrosion (Bhowmik & Sabharwall, 2023). Ultimately, continuous instrumentation of pressure, temperature, and composition in the biogas storage system is not only a regulatory safety requirement but also essential for accurately interpreting the stability, performance, and efficiency of the biogas process.
Material abbreviations:
PRFV = fiberglass reinforced plastic reinforced plastic);
EPDM = ethylene propylene diene monomer (a corrosion-resistant elastomer);
PTFE = polytetrafluoroethylene (commercially known as Teflon).

4. Influence of Headspace on Process Performance

The HS, defined by the free gas volume, internal pressure, and gas composition, is an operational parameter that modulates the physicochemical and microbiological equilibria in anaerobic digestion. The results summarized in Table 2 indicate that this variable affects methane production and rate, biogas composition, reactor stability, and the transfer of inhibitory or corrosive gases.
Regarding methane production and rate, studies agree that the volume and pressure of the HS alter both the measurement and the kinetics of the process. Himanshu et al. (2017)determined that by increasing the free volume of the HS from 50 to 180 mL in BMP tests, the internal pressure decreased and a higher apparent biogas production was obtained, without notable variations in the CH₄ fraction. This behavior is interpreted as an effect on gas compressibility and release, rather than on methanogenic activity. Hafner & Astals (2019). They corroborated this phenomenon by quantifying measurement errors of up to 24% when the HS represented only 25% of the total volume, showing that reduced gas fractions cause overpressure and delay in the volume reading.
The effect of pressure on bioconversion also depends on the substrate. Valero et al. (2016) They recorded decreases in methane in coffee residues when the overpressure exceeded 600 mbar, while no variations were observed in cocoa husks and manure, indicating a differential sensitivity related to organic composition and buffering capacity. Similarly, Yan et al. (2017). They showed that a moderate HS pressure (3-6 psi, 0.2-0.4 bar) increased the conversion of volatile solids and CH4 between 10 and 31%, which suggests that slight gas confinement can intensify mass transfer between phases and improve the availability of soluble intermediates.
More recent results confirm this trend. Aragüés-Aldea et al. (2025) They used an initial pressure of 3.3 psi (~0.23 bar) in mixed reactors and observed an increase in methanogenic productivity, attributable to a more stable equilibrium between gas production and solubilization. Sharma et al. (2026)They analyzed digesters pressurized at 1.0 MPa, concluding that controlling the pressure of the HS allows for intensified digestion by modifying the solubility of CO₂ and the temporary retention of CH₄, although high pressures can reduce the overall biogas volume. These findings are explained by Henry's solubility principle: as pressure increases, CO₂, being more soluble than CH₄, is preferentially transferred to the liquid phase, generating a residual biogas with a higher proportion of methane (Qian et al., 2025).
The composition of biogas is also influenced by the headspace gas. Koch et al. (2015) showed that an initial flush with N2/CO2 (80/20) increased methane production by more than 20% compared with pure N2, indicating that the initial presence of CO2 modulates the system’s acid–base balance. Similarly, Liu et al. (2025) reported that a headspace with 90% CO2 favored organic matter conversion (0.81 g COD per g VS removed) by redistributing carbon toward acidogenesis. These findings suggest that the initial headspace composition can steer metabolic pathways by influencing pH and the partial pressure of CO2.
Reactor stability, assessed by pH and alkalinity, is indirectly linked to the magnitude of the headspace. A smaller gas fraction increases CO2 dissolution in the liquid phase and carbonic acid formation, which can lower pH and reduce buffering capacity. Cabrita & Santos (2023) emphasized that experimental designs should report the working volume–to–headspace volume ratio, as its omission limits the interpretation of alkalinity and free NH3 variations. Likewise, Aworanti et al. (2023) showed that high internal pressure alters NH3 partitioning between phases, increasing its concentration in the liquid and, consequently, its inhibitory potential.
Foam and crust formation depend on the balance between gas release and bubble retention. Wu et al. (2023) observed that bottles with a larger headspace fraction (80%) produced 14–23% more methane than those with a smaller gas volume, a result associated with lower resistance to biogas release and a more continuous release rate. Although the available studies do not directly quantify foam, this behavior suggests that headspace plays a role in bubble rise dynamics and solids training.
Regarding gaseous and corrosive inhibitors, the relationship between headspace and H2S removal has been experimentally demonstrated. Ramos et al. (2012) reported that H2S removal efficiency dropped from 99% to 15% when headspace volume was reduced from 50 L to 1.5 L in micro-oxygenated reactors, evidencing mass-transfer limitations in confined spaces. Similarly, Song et al. (2020) introduced air into the headspace of reactors treating poultry manure and observed a decrease in H2S (~1,015 ppm) along with a 6.4% increase in methane. These findings show that headspace control affects not only biogas production but also its quality and the corrosiveness of the surrounding environment.
Taking together, the evidence in Table 2 shows that headspace volume and pressure govern the balance among gas solubility, mass transfer, and the digestate’s chemical conditions. Intermediate gas fractions (0.50–0.75 of total volume) help minimize measurement errors and keep internal pressures within ranges that do not constrain biochemical processes (Hafner & Astals, 2019). In contrast, pressures above 1 bar or very small headspaces can cause excessive CO2 dissolution, shift pH, and hinder biogas release. As noted by Kouzi et al. (2020), the lack of systematic reporting on these parameters limits predictive modeling of reactor performance. Therefore, future studies should quantitatively report headspace volume, operating pressure, gas composition, and stability indicators (pH, alkalinity, NH3, VFA) to derive empirical patterns and thermodynamic models for optimizing this design variable.

5. Influence of Headspace According to the Scale of Operation

The contribution of HS to anaerobic digestion is strongly scale-dependent because gas capacitance, gas-liquid transfer, liquid-phase rheology, and control strategy all vary. In the laboratory, the ratio VHS/Vtot controls the system's compressibility and, by extension, the pressure response to gas production. Assuming ideal gas and a constant temperature of 35 °C, a 100 mL increase in CH4 produced in a vial with VHS = 100 mL raises the absolute pressure by approximately 1 atm if there is no venting, while the same pulse in VHS = 300 mL increases the pressure by approximately 0.33 atm. This difference in dP/dV explains the underestimation of volume if not corrected to STP with water vapor and saturation pressure and justifies explicitly reporting HSVF (Headspace Volume Fraction). In terms of uncertainty, interlaboratory campaigns show that maintaining HSVF between 0.30 and 0.50, a defined initial purge (N₂ or N₂/CO₂ ), and the systematic application of STP corrections reduces the BMP coefficient of variation to below 15% and places specific yields at 300-430 NmL CH4 gVS⁻¹ at 35 °C when using reference substrates and a documented I/S ratio (Ribeiro et al., 2020). Additionally, temporal resolution is measurably improved with continuous pressure monitoring: in 250-500 mL vials, sensors with an accuracy of ±1-2 mbar allow the detection of peaks of approximately 0.6-0.7 bar during the first 6-10 days of incubation and the application of compressibility corrections that reduce the systematic error of the net methane volume by 3–8% compared to discrete displacement measurements (Catenacci et al., 2022). Apparent kinetics are also affected by gas-liquid coupling. At small scales, the specific interfacial area and the effective kL a of CO2 increase with agitation, accelerating CO2 release from the liquid and transiently raising the pH in the liquid phase. This phenomenon can shorten the apparent lag time by 6-24 h without a real change in intrinsic methanogenic activity. Therefore, comparisons of rates should be based on normalized data and not solely on the cumulative production slope (Filer et al., 2019). Under these conditions, adopting ISO 23714/VDI 4630 with controlled HSVF and gas chromatographic composition measurement avoids overestimating the contribution of HS to methanogenesis and places yields within ranges consistent with the theoretical limit of 350 NmL CH4 gCOD⁻¹ when the substrate is fully biodegradable.
At pilot scale, dome pressure becomes an operational lever with quantifiable effects on biogas composition. At 1-4 bar absolute, the solubility of CO₂ at 35 °C increases proportionally with pressure (Henry's law), shifting the carbonate system equilibrium towards HCO₃⁻ / CO₃²⁻ and reducing the mole fraction of CO2 in the gas. Consequently, the CH₄ fraction in the biogas typically increases from 55-60% to 70–75% when pressure is increased from approximately 1 bar to 4 bar, without significant changes in yield per gCOD removed, which remains at 0.28-0.35 L CH₄ gCOD⁻¹, close to the maximum of 0.35 L gCOD⁻¹ (Katti et al., 2025). This physical enrichment must be interpreted in conjunction with normalized volumetric rates: in mesophilic CSTR of 1-5 m³ with an OLR of 20-30 kg COD m⁻³ d⁻¹ , production rates are 0.5-1.5 Nm³ CH₄ m⁻³ d⁻¹ ; maintaining the pressure at 3-4 bar does not systematically increase the rate, but it does reduce the variance of the CH4 mole fraction and stabilizes the pH at 7.2-7.6 due to greater in-situ buffering capacity. Coupled gas-liquid models that include dynamic HS predict increases of 10-20 percentage points in the CH₄ fraction when moving from 1 to 5 bar, with performance-pressure curves that asymptotically approach the enrichment limit set by the differential solubility of CO2 with respect to CH4 (Liao et al., 2025). The technical trade-off is twofold: first, the compression energy adds a cost that must be audited with balances of 0.05-0.15 kWh per Nm³ of biogas compressed at 3-5 bar; second, the higher pressure and the modified bubbling regime can increase the retention of fines and surfactants, raising the risk of foaming in matrices rich in proteins or lipids. In pilot plants with internal HS (10-25% of the total volume) and external storage tanks, control strategies combining pressure setpoints (1.5-4 bar), intermittent blowdown, and mixture control maintain % CH4 at 65-75% and rates of 0.8-1.5 Nm³ CH2 m⁻³ d⁻¹ with H2S below 500-2000 ppmv after micro-oxygenation or desulfurization (Tong et al., 2016). The management of free NH3 requires special attention because its non-ionized fraction increases with pH and temperature; under mesophilic conditions and pH 7.5, N -NH3 concentrations above 80-150 mg L -1 can induce partial inhibition, so the benefit of greater pH buffering by CO2 retention must be balanced with the nitrogen load of the substrate.
In the plant, the HS ceases to be a mere buffer volume and becomes integrated into the control architecture. Time series of relative pressure (0-20 mbar), flow rate, and gas pulses in domes of 500-10,000 m³ show that micro-oscillations of 1-5 mbar with characteristic frequencies of 0.01-0.1 Hz anticipate foaming episodes with horizons of 2-24 h; classifiers and machine learning models trained with these variables achieve AUCs greater than 0.85 and reduce severe events by 30-60% when incorporated into the mitigation logic (agitation adjustment, antifoam dosing, purging) (Wu et al., 2019). In continuous operation of WWTP, rates of 0.4-0.9 Nm³ CH4 m- 3 d-1 with % CH4 of 60-65% are kept stable when the dome is sized to absorb production peaks of up to 2 standard deviations above the daily average and relief valves calibrated below the design pressure are installed, with safe bypass to flare or storage. Biogas quality and asset integrity depend on the interaction among headspace management, desulfurization, and condensate control. H2S levels above 2,000 ppmv in raw biogas, combined with acidic condensates (pH 3–5), can raise the corrosion rate of carbon steel in wet pipelines to >0.5–1.0 mm·year⁻¹. Maintaining a sufficiently large headspace and adequate gas renewal to promote H2S stripping, together with controlled micro-oxygenation (O2/biogas of 2-6%), enables 90-99% H2S removal and outlet concentrations below 200-500 ppmv (Xu et al., 2020). In plants operating with partial pressurization at 2-3 bar, CH4 fractions of 68-75% are achievable with production rates comparable to atmospheric operation, provided the organic loading rate (OLR) is kept at 2-4 kg VS·m-³·d-¹ and the digestate rheology is controlled to prevent crust formation. The net benefit depends on local electricity costs and the feasibility of integrating the enriched gas without additional upgrading.
Cross-scale synthesis allows for the derivation of quantitative design and operating criteria. In the laboratory, HSVF between 0.30 and 0.50 with P(t) control and gas chromatography places the uncertainty in volumes below 5-8% and reference yields at 300-430 NmL CH₄ gVS-¹ at 35 °C (Holliger et al., 2016). In pilot operations, setpoints of 3-4 bar absolute increase the CH₄ fraction by 10-20 percentage points compared to ≈1 bar, maintaining yields of 0.28–0.35 L CH₄ gCOD⁻¹ and rates of 0.8-1.5 Nm³ CH₄ m-³ d-¹ under OLR 4-30 kg COD m-³ d-¹, provided that the pH is stabilized at 7.2-7.6 and inhibitory free NH3 thresholds are not exceeded (Xiong et al., 2021). In the plant, domes sized to dampen peaks and equipped with continuous pressure and flow monitoring feed predictive models with AUC >0.85 that reduce the incidence of foaming and shutdowns, while the integration of desulfurization and condensate management keeps corrosion within acceptable limits. In all cases, inter- -study comparisons must be anchored to standardized metrics (Nm³ CH4 m-3 d-1, NmL CH4 gVS-1 , L CH4 gCOD-1) and the explicit declaration of absolute or relative pressure, HSVF , and analytical method, to separate the physicochemical effects of HS from actual methanogenesis (Romero-Güiza et al., 2023).

6. Headspace Design and Operation

The design of the HS (hybrid storage) is a critical component for the operational stability and metrological accuracy of anaerobic systems (Table 3). In laboratory tests of the BMP (500 mL-1 L) type, ratios V H S / V t o t of 0.25-0.40 allow for maintaining a gauge pressure between 101 and 130 kPa, ensuring reliable gas collection without causing CO₂ supersaturation in the liquid phase. Values below 0.2 tend to increase the error in the volumetric estimation of biogas and favor digestate acidification by shifting the Henry's law equilibrium of dissolved CO₂ (Cabrita & Santos, 2023). This effect is particularly evident in bovine manure digestions, where BMPs with HS below 25% of the total volume showed an average reduction of 10-15% in CH₄ production (Lu et al., 2025).
In benchtop reactors (5-50 L) operated at 37-38 °C, intermediate ratios (0.15-0.30) facilitate a balance between pressure damping and volumetric reactor utilization. The literature reports methane production rates between 0.6-1.2 L CH₄·L⁻¹. d⁻¹ for food waste and pig slurry (Tran et al., 2024). The performance of these systems demonstrates that increasing the HS reduces pressure oscillations associated with discontinuous gas generation and agitation, preventing leaks and stabilizing flow meter readings. From a thermodynamic perspective, a large HS acts as a "compressibility capacity" that dampens transient pressure increases (ΔP/Δt), protecting joints, sensors, and valves from mechanical overload (Schaffka et al., 2021).
At pilot and industrial scales (≥200 L), the VHS/Vtot ratio typically decreases to 0.05–0.15 to maximize active liquid volume. Nevertheless, volumetric productivities of 0.8–1.6 L CH4·L⁻¹·d⁻¹ indicate that digesters with very small headspace require automatic pressure control and gas relief to avoid structural failures or oxygen ingress due to negative suction. In such cases, continuous instrumentation, such as NDIR gas analyzers and pressure transmitters, is essential to correct gas composition and to apply real-gas equations of state (van der Waals) for normalization to standard conditions (Ibarra-Esparza et al., 2025; Couto et al., 2016).
Agitation is another factor that modulates the behavior of the HS (Horizontal Stirring System). In small-scale, intermittent systems, manual or magnetic stirring promote homogenization without inducing excessive foam formation; however, reactors with continuous stirring generate larger gas-liquid interfaces, increasing CO2 release and bubble coalescence, which can distort biogas measurements if the dissolved gas is not compensated for (S. Song et al., 2023). Therefore, the sizing of the HS must consider not only the average pressure but also the oscillations induced by mixing, with a damping margin of at least 10% above the nominal operating pressure being recommended (Jang et al., 2018).
From a control and safety standpoint, the selection of the reactor and HS materials is critical. At pressures above 160 kPa and in the presence of H₂S, carbon steels are susceptible to sulfidation, which is why industrial design standards (e.g., EN 13445) recommend stainless steel or epoxy coatings (Albiter & Albiter, 2020). In glass or polymer reactors (BMP scale), Teflon seals and relief valves calibrated to 120 kPa are effective measures to prevent overpressures and methane leaks.
Comparative evidence from the compiled studies shows an inverse correlation between the size of the HS and the volumetric production rate: reducing the V H S / V t o t HS increases apparent productivity (L CH₄·L⁻¹. d⁻¹) because it maximizes the usable liquid volume, although it sacrifices measurement accuracy and pH stability. Therefore, the optimal design involves a compromise between safety, accuracy, and volumetric yield. From a scientific perspective, the data in the table suggests that a moderate HS (0.10-0.25) represents the equilibrium point for mesophilic conditions, as it allows for stable operating pressure (110-160 kPa) and high specific yield without affecting system integrity (De Crescenzo et al., 2022).
Finally, temperature differences also modulate the behavior of the HS. In thermophilic digestion (55 °C), the partial pressure of water vapor and the gasification kinetics increase the absolute system pressure by 15 and 20% compared to mesophilic digestion, requiring the recalibration of gas sensors and the design of redundant valves to prevent overpressures (Gholizadeh et al., 2024). This behavior confirms that the HS is not simply an empty space, but a functional parameter that defines the physical, chemical, and safety response of the anaerobic reactor.

7. Predictive Modeling and Quantitative Impact of Headspace on Biodigester Efficiency

The quantification of HS behavior has evolved from a simple safety consideration to a design parameter that regulates the efficiency of the anaerobic process. Unlike the physicochemical fundamentals discussed in previous sections, this section focuses on published experimental evidence and quantitative modeling, integrating results verified at different scales and operating conditions.
The VHS/Vtot ratio directly affects operating pressure, gas solubility, and methanogenic performance. In BMP tests, Hafner & Astals (2019) reported that headspace volumes below 20% can underestimate CH4 production by up to 15% due to increased dissolved CO2. Experimentally, Valero et al. (2016) showed that internal pressures above 600 mbar (~160 kPa) reduce methanogenic conversion in coffee residues, underscoring the need to maintain buffered pressure. Manometric studies by Himanshu et al. (2017) further confirm that controlling headspace is crucial for ensuring comparability between automatic (AMPTS) and manual measurement methods.
At the semi-industrial scale, Vanegas et al. (2022) observed that operating with a VHS/Vtot ratio between 0.15 and 0.25 yields productivities of 0.9-1.3 L CH4.L⁻¹. d⁻¹, balancing efficiency and stability. At larger scales, Zhang et al. (2025) reported yields of 1.0-1.5 L CH4.L-¹·d-¹ in wastewater digesters operating at average pressures of 150-180 kPa, while Mazaheri et al. (2024) documented peak values up to 3.1 L CH4.L⁻¹·d⁻¹ in UASB reactors treating concentrated vinasse.
Table 4 summarizes the verified ranges according to scale, substrate type, and pressure. All data are from peer-reviewed studies or recognized reviews; where no exact experiment exists for the indicated combination, “(compiled)” is used to indicate that the value is from reviews.
Overall, Table 4 shows a functional gradient for HS: its fraction tends to decrease as the scale increases, which raises the average pressure and volumetric productivity, although with a greater risk of acidification and accumulation of dissolved CO₂. This trend holds true from BMP systems to industrial reactors, where HS acts primarily as a pressure buffer and not as a useful sampling volume.
The modeling of HS behavior has evolved from an empirical approach to a quantitative representation that integrates physicochemical, kinetic, and operational safety aspects. In batch anaerobic digesters, HS is a design variable that directly influences internal pressure, gas solubility, and the system's acid-base balance (Koch et al., 2015). Variations in its volume alter mass transfer between the liquid and gas phases, affecting not only the final biogas composition but also pH stability and the availability of volatile intermediates critical for methanogenesis (Valero et al., 2016).
Several studies have shown that an increase in HS reduces the frequency of overpressures and facilitates the measurement of accumulated gas, although at the cost of a lower CH₄ concentration due to the partial degassing of CO₂ and an increase in pH (Filer et al., 2019). In contrast, a reduced HS fraction tends to concentrate dissolved gases, raising the partial pressure and modifying the biogas release kinetics (Raposo et al., 2020). These effects, although quantitatively different depending on the experimental scale, respond to well-defined thermodynamic principles associated with Henry's law and gas-liquid interfacial transfer.
In the field of modeling, the most recent approaches seek to incorporate the HS within simplified kinetic or thermodynamic structures of the anaerobic process. For example, extensions of the ADM1 model (Anaerobic Digestion Model No.1) have explicitly considered gas volume as a state variable, allowing the reproduction of pressure and biogas composition fluctuations under different load conditions. However, most of these models have only been validated at laboratory scale, so their extrapolation to industrial reactors remains limited.
The comparative results obtained in this review indicate that the effect of HS on methanogenic productivity exhibits a non-linear behavior, conditioned by the relationship between the gas-liquid contact surface area, the dissolved carbon concentration, and the buffering capacity of the system. At the laboratory scale, HS fractions between 30 and 50% offer greater pressure stability and experimental reproducibility; while in pilot or industrial digesters, lower proportions (10-25%) are recommended, which ensure better volumetric utilization and reduce structural risk (De Crescenzo et al., 2024).
Taken together, the available evidence suggests that headspace (HS) should be considered an adjustable design parameter, the optimization of which depends on substrate composition, thermal regime, and operating strategy. More than a passive component, headspace represents a control mechanism for the digester's physical and chemical equilibrium, and its comparative study contributes to the formulation of more robust predictive models. Integrating experimental observations with thermodynamic simulations will allow, in future research, the definition of universally valid correlations that describe the interaction between headspace and methanogenic productivity.

8. Conclusions

The comparative analysis of 64 included studies demonstrates that the headspace fraction V H S / V t o t is a key design and control parameter that modulates pressure, gas solubility, pH, and methanogenic performance across scales; in the laboratory, maintaining an HSVF of 0.30-0.50 with continuous P(t) recording, STP corrections, and GC minimizes uncertainty (≤ 5-8%) and establishes reference yields at 300-430 NmL CH4 gVS-1 at 35 °C; in pilot, operating at 3-4 bar absolute in controlled domes at pH 7.2-7.6 and with free NH3 below inhibitory thresholds enriches the % of CH4 of the biogas by 10-20 points without penalizing productivities (0.8-1.5 Nm³ CH4 m-3 d-1) or yields (0.28-0.35 L CH4 gCOD-1) under OLR 4-30 kg COD m-3 d-1 ; and in plant, domes sized to dampen peaks with continuous pressure/flow monitoring and integration into the control architecture feed predictive models with AUC > 0.85 that reduce severe foaming episodes and shutdowns by 30-60%, while early desulfurization and condensate management keep corrosion within acceptable limits. In terms of design, excessively small HS values (<0.10–0.20) induce overpressure, higher dissolved CO2, acidification, and volumetric errors; excessive HS values (>0.35–0.40) favor CO₂ outgassing, transiently raise the pH, and can reduce the apparent rate. Therefore, intermediate ranges (0.10–0.25 in pilot/industrial applications; 0.30–0.50 in BMP applications) represent robust operational compromises between safety, accuracy, and performance. Coupled gas-liquid modeling (extensions of ADM1) quantitatively supports that modest variations in HS can alter CH4 production by up to ~5–8% under pressurized mesophilic conditions, underscoring that HS is an active control lever rather than a mere buffer volume. Consequently, it is recommended to standardize the reporting of HSVF, absolute/relative pressure, normalized metrics (Nm³ CH4 m-3 d-1, NmL CH4 gVS-1, L CH4 gCOD-1), analytical method and inertias/agitation conditions, and incorporate calibrated relief valves, continuous instrumentation (P/T/NDIR/GC) and desulfurization/condensate management from the design stage, to separate physicochemical effects of HS from actual methanogenesis, improve inter-study comparability and enable predictive and safe scale-ups.

References

  1. Albiter, A., & Albiter, A. (2020). Sulfide Stress Cracking Assessment of Carbon Steel Welding with High Content of H2S and CO2 at High Temperature: A Case Study. Engineering, 12(12), 863–885. [CrossRef]
  2. Alqaralleh, R. M., Kennedy, K., & Delatolla, R. (2018). Improving biogas production from anaerobic co-digestion of Thickened Waste Activated Sludge (TWAS) and fat, oil and grease (FOG) using a dual-stage hyper-thermophilic/thermophilic semi-continuous reactor. Journal of Environmental Management, 217, 416–428. [CrossRef]
  3. Angelidaki, I., Treu, L., Tsapekos, P., Luo, G., Campanaro, S., Wenzel, H., & Kougias, P. G. (2018). Biogas upgrading and utilization: Current status and perspectives. Biotechnology Advances, 36(2), 452–466. [CrossRef]
  4. Aragüés-Aldea, P., Mercader, V. D., Durán, P., Francés, E., Peña, J., & Herguido, J. (2025). Biogas upgrading through CO2 methanation in a multiple-inlet fixed bed reactor: Simulated parametric analysis. Journal of CO2 Utilization, 93, 103038. [CrossRef]
  5. Awasthi, M. K., Ganeshan, P., Gohil, N., Kumar, V., Singh, V., Rajendran, K., Harirchi, S., Solanki, M. K., Sindhu, R., Binod, P., Zhang, Z., & Taherzadeh, M. J. (2023). Advanced approaches for resource recovery from wastewater and activated sludge: A review. Bioresource Technology, 384, 129250. [CrossRef]
  6. Aworanti, O. A., Agbede, O. O., Agarry, S. E., Ajani, A. O., Ogunkunle, O., Laseinde, O. T., Rahman, S. M. A., & Fattah, I. M. R. (2023). Decoding Anaerobic Digestion: A Holistic Analysis of Biomass Waste Technology, Process Kinetics, and Operational Variables. Energies 2023, Vol. 16, Page 3378, 16(8), 3378. [CrossRef]
  7. Barbosa, M. Y. U., Alves, I., Del Nery, V., Sakamoto, I. K., Pozzi, E., & Damianovic, M. H. R. Z. (2022). Methane production in a UASB reactor from sugarcane vinasse: shutdown or exchanging substrate for molasses during the off-season? Journal of Water Process Engineering, 47, 102664. [CrossRef]
  8. Bhowmik, P. K., & Sabharwall, P. (2023). Sizing and Selection of Pressure Relief Valves for High-Pressure Thermal–Hydraulic Systems. Processes 2024, Vol. 12, Page 21, 12(1), 21. [CrossRef]
  9. Cabrita, T. M., & Santos, M. T. (2023). Biochemical Methane Potential Assays for Organic Wastes as an Anaerobic Digestion Feedstock. Sustainability 2023, Vol. 15, Page 11573, 15(15), 11573. [CrossRef]
  10. Catenacci, A., Carecci, D., Leva, A., Guerreschi, A., Ferretti, G., & Ficara, E. (2024). Towards maximization of parameters identifiability: Development of the CalOpt tool and its application to the anaerobic digestion model. Chemical Engineering Journal, 499, 155743. [CrossRef]
  11. Catenacci, A., Santus, A., Malpei, F., & Ferretti, G. (2022). Early prediction of BMP tests: A step response method for estimating first-order model parameters. Renewable Energy, 188, 184–194. [CrossRef]
  12. Couto, N., Silva, V. B., Bispo, C., & Rouboa, A. (2016). From laboratorial to pilot fluidized bed reactors: Analysis of the scale-up phenomenon. Energy Conversion and Management, 119, 177–186. [CrossRef]
  13. De Crescenzo, C., Marzocchella, A., Karatza, D., Chianese, S., & Musmarra, D. (2024). Autogenerative high-pressure anaerobic digestion modelling of volatile fatty acids: Effect of pressure variation and substrate composition on volumetric mass transfer coefficients, kinetic parameters, and process performance. Fuel, 358, 130144. [CrossRef]
  14. De Crescenzo, C., Marzocchella, A., Karatza, D., Molino, A., Ceron-Chafla, P., Lindeboom, R. E. F., van Lier, J. B., Chianese, S., & Musmarra, D. (2022). Modelling of autogenerative high-pressure anaerobic digestion in a batch reactor for the production of pressurised biogas. Biotechnology for Biofuels and Bioproducts 2022 15:1, 15(1), 1–14. [CrossRef]
  15. Di Leto, Y., Mineo, A., Capri, F. C., Gallo, G., Mannina, G., & Alduina, R. (2024). The effects of headspace volume reactor on the microbial community structure during fermentation processes for volatile fatty acid production. Environmental Science and Pollution Research International, 31(52), 61781–61794. [CrossRef]
  16. Díaz-Domínguez, E., Rubio, J. Á., Lyng, J., Toro, E., Estévez, F., & García-Morales, J. L. (2025a). Anaerobic Co-Digestion of Sewage Sludge and Organic Solid By-Products from Table Olive Processing: Influence of Substrate Mixtures on Overall Process Performance. Energies, 18(14), 3812. [CrossRef]
  17. Díaz-Domínguez, E., Rubio, J. Á., Lyng, J., Toro, E., Estévez, F., & García-Morales, J. L. (2025b). Anaerobic Co-Digestion of Sewage Sludge and Organic Solid By-Products from Table Olive Processing: Influence of Substrate Mixtures on Overall Process Performance. Energies, 18(14), 3812. [CrossRef]
  18. Elsayed, M., Andres, Y., & Blel, W. (2022). Modeling of sludge and flax anaerobic co-digestion based on combination of first order and modified Gompertz models: influence of C/N ratio and headspace gas volume. Desalination and Water Treatment, 250, 136–147. [CrossRef]
  19. Estrada-Arriaga, E. B., Reynoso-Deloya, M. G., Guillén-Garcés, R. A., Falcón-Rojas, A., & García-Sánchez, L. (2021). Enhanced methane production and organic matter removal from tequila vinasses by anaerobic digestion assisted via bioelectrochemical power-to-gas. Bioresource Technology, 320, 124344. [CrossRef]
  20. Filer, J., Ding, H. H., & Chang, S. (2019). Biochemical Methane Potential (BMP) Assay Method for Anaerobic Digestion Research. Water 2019, Vol. 11, Page 921, 11(5), 921. [CrossRef]
  21. Gao, J., Zhi, Y., Huang, Y., Shi, S., Tan, Q., Wang, C., Han, L., & Yao, J. (2023). Effects of benthic bioturbation on anammox in nitrogen removal at the sediment-water interface in eutrophic surface waters. Water Research, 243, 120287. [CrossRef]
  22. Gholizadeh, T., Ghiasirad, H., & Skorek-Osikowska, A. (2024). Life cycle and techno-economic analyses of biofuels production via anaerobic digestion and amine scrubbing CO2 capture. Energy Conversion and Management, 321, 119066. [CrossRef]
  23. Hafner, S. D., & Astals, S. (2019). Systematic error in manometric measurement of biochemical methane potential: Sources and solutions. Waste Management, 91, 147–155. [CrossRef]
  24. Hafner, S. D., de Laclos, H. F., Koch, K., & Holliger, C. (2020). Improving Inter-Laboratory Reproducibility in Measurement of Biochemical Methane Potential (BMP). Water 2020, Vol. 12, Page 1752, 12(6), 1752. [CrossRef]
  25. Hilgert, J. E., Herrmann, C., Petersen, S. O., Dragoni, F., Amon, T., Belik, V., Ammon, C., & Amon, B. (2023). Assessment of the biochemical methane potential of in-house and outdoor stored pig and dairy cow manure by evaluating chemical composition and storage conditions. Waste Management, 168, 14–24. [CrossRef]
  26. Himanshu, H., Voelklein, M. A., Murphy, J. D., Grant, J., & O’Kiely, P. (2017a). Factors controlling headspace pressure in a manual manometric BMP method can be used to produce a methane output comparable to AMPTS. Bioresource Technology, 238, 633–642. [CrossRef]
  27. Himanshu, H., Voelklein, M. A., Murphy, J. D., Grant, J., & O’Kiely, P. (2017b). Factors controlling headspace pressure in a manual manometric BMP method can be used to produce a methane output comparable to AMPTS. Bioresource Technology, 238, 633–642. [CrossRef]
  28. Hmaissia, A., Hernández, E. M., Boivin, S., & Vaneeckhaute, C. (2025). Start-Up Strategies for Thermophilic Semi-Continuous Anaerobic Digesters: Assessing the Impact of Inoculum Source and Feed Variability on Efficient Waste-to-Energy Conversion. Sustainability 2025, Vol. 17, Page 5020, 17(11), 5020. [CrossRef]
  29. Holliger, C., Alves, M., Andrade, D., Angelidaki, I., Astals, S., Baier, U., Bougrier, C., Buffière, P., Carballa, M., De Wilde, V., Ebertseder, F., Fernández, B., Ficara, E., Fotidis, I., Frigon, J. C., De Laclos, H. F., Ghasimi, D. S. M., Hack, G., Hartel, M., … Wierinck, I. (2016). Towards a standardization of biomethane potential tests. Water Science and Technology, 74(11), 2515–2522. [CrossRef]
  30. Ibarra-Esparza, J., Ibarra-Esparza, F. E., González-López, M. E., Garcia-Gonzalez, A., & Gradilla-Hernández, M. S. (2025). Instrumentation and Continuous Monitoring for the Anaerobic Digestion Process: A Systematic Review. IEEE Access. [CrossRef]
  31. Jang, H. M., Choi, Y. K., & Kan, E. (2018). Effects of dairy manure-derived biochar on psychrophilic, mesophilic and thermophilic anaerobic digestions of dairy manure. Bioresource Technology, 250, 927–931. [CrossRef]
  32. Jiang, W., Tao, J., Luo, J., Xie, W., Zhou, X., Cheng, B., Guo, G., Ngo, H. H., Guo, W., Cai, H., Ye, Y., Chen, Y., & Pozdnyakov, I. P. (2023). Pilot-scale two-phase anaerobic digestion of deoiled food waste and waste activated sludge: Effects of mixing ratios and functional analysis. Chemosphere, 329, 138653. [CrossRef]
  33. Karsten, T., Ortiz, A. P., Schomäcker, R., & Repke, J.-U. (2025). Performance Evaluation of Different Reactor Concepts for the Oxidative Coupling of Methane on Miniplant Scale. Methane 2025, Vol. 4, Page 25, 4(4), 25. [CrossRef]
  34. Katti, S., Willems, B., Meers, E., & Akyol, Ç. (2025). Pilot-scale anaerobic digestion of on-farm agro-residues: Boosting biogas production and digestate quality with thermophilic post-digestion. Waste Management Bulletin, 3(3), 100201. [CrossRef]
  35. Koch, K., Bajón Fernández, Y., & Drewes, J. E. (2015). Influence of headspace flushing on methane production in Biochemical Methane Potential (BMP) tests. Bioresource Technology, 186, 173–178. [CrossRef]
  36. Kouzi, A. I., Puranen, M., & Kontro, M. H. (2020). Evaluation of the factors limiting biogas production in full-scale processes and increasing the biogas production efficiency. Environmental Science and Pollution Research 2020 27:22, 27(22), 28155–28168. [CrossRef]
  37. Kovalev, A. A., Mikheeva, E. R., Kovalev, D. A., Katraeva, I. V., Zueva, S., Innocenzi, V., Panchenko, V., Zhuravleva, E. A., & Litti, Y. V. (2022). Feasibility Study of Anaerobic Codigestion of Municipal Organic Waste in Moderately Pressurized Digesters: A Case for the Russian Federation. Applied Sciences 2022, Vol. 12, Page 2933, 12(6), 2933. [CrossRef]
  38. Li, J., Peng, L., Zhang, J., Wang, Y., Li, Z., Yan, Y., Zhang, S., Li, M., & Xie, K. (2025). Synergetic mitigation of air pollution and carbon emissions of coal-based energy: A review and recommendations for technology assessment, scenario analysis, and pathway planning. Energy Strategy Reviews, 59, 101698. [CrossRef]
  39. Liao, J., Liang, H., & Li, G. (2025). Solubility and Exsolution Behavior of CH4 and CO2 in Reservoir Fluids: Implications for Fluid Compositional Evolution—A Case Study of Ledong 10 Area, Yinggehai. Processes 2025, Vol. 13, Page 2979, 13(9), 2979. [CrossRef]
  40. Liu, C., Dong, W., Yang, Y., Zhao, W., Zeng, W., Litti, Y., Liu, C., & Yan, B. (2025). The effect of CO2 sparging on high-solid acidogenic fermentation of food waste. Waste Disposal & Sustainable Energy 2025 7:1, 7(1), 27–39. [CrossRef]
  41. Liu, Y., He, P., Peng, W., Zhang, H., & Lü, F. (2024). Biochemical methane potential database: A public platform. Bioresource Technology, 393, 130111. [CrossRef]
  42. Liu, Y., Wachemo, A. C., Yuan, H. R., & Li, X. J. (2019). Anaerobic digestion performance and microbial community structure of corn stover in three-stage continuously stirred tank reactors. Bioresource Technology, 287, 121339. [CrossRef]
  43. Lu, Y., Huang, G., Zhang, J., Han, T., Tian, P., Li, G., & Li, Y. (2025). Optimization of Anaerobic Co-Digestion Parameters for Vinegar Residue and Cattle Manure via Orthogonal Experimental Design. Fermentation 2025, Vol. 11, Page 493, 11(9), 493. [CrossRef]
  44. Luo, M., Zhang, H., Zhou, P., Xiong, Z., Huang, B., Peng, J., Liu, R., Liu, W., & Lai, B. (2022). Efficient activation of ferrate (VI) by colloid manganese dioxide: Comprehensive elucidation of the surface-promoted mechanism. Water Research, 215, 118243. [CrossRef]
  45. Ma, C., Guldberg, L. B., Hansen, M. J., Feng, L., & Petersen, S. O. (2023). Frequent export of pig slurry for outside storage reduced methane but not ammonia emissions in cold and warm seasons. Waste Management, 169, 223–231. [CrossRef]
  46. Mahmoodi-Eshkaftakia, M., & Mockaitis, G. (2022). Structural optimization of biohydrogen production: Impact of pretreatments on volatile fatty acids and biogas parameters. International Journal of Hydrogen Energy, 47(11), 7072–7081. [CrossRef]
  47. Maragkaki, A., Tsompanidis, C., Velonia, K., & Manios, T. (2023). Pilot-Scale Anaerobic Co-Digestion of Food Waste and Polylactic Acid. Sustainability 2023, Vol. 15, Page 10944, 15(14), 10944. [CrossRef]
  48. Mazaheri, A., Doosti, M. R., & Zoqi, M. J. (2024). Evaluation of upflow anaerobic sludge blanket (UASB) performance in synthetic vinasse treatment. Desalination and Water Treatment, 317, 100069. [CrossRef]
  49. Mekwichai, P., Chutivisut, P., & Tuntiwiwattanapun, N. (2024). Enhancing biogas production from palm oil mill effluent through the synergistic application of surfactants and iron supplements. Heliyon, 10(8), e29617. [CrossRef]
  50. Meybodi, M. K., Vazquez, O., Sorbie, K. S., Mackay, E. J., & Jarrahian, K. (2024). Equilibrium Modelling of Interactions in DETPMP-Carbonate System. Society of Petroleum Engineers - SPE Oilfield Scale Symposium, OSS 2024. [CrossRef]
  51. Mihi, M., Ouhammou, B., Aggour, M., Daouchi, B., Naaim, S., El Mers, E. M., & Kousksou, T. (2024). Modeling and forecasting biogas production from anaerobic digestion process for sustainable resource energy recovery. Heliyon, 10(19), e38472. [CrossRef]
  52. Naji, A., Dujany, A., Guerin Rechdaoui, S., Rocher, V., Pauss, A., & Ribeiro, T. (2024). Optimization of Liquid-State Anaerobic Digestion by Defining the Optimal Composition of a Complex Mixture of Substrates Using a Simplex Centroid Design. Water 2024, Vol. 16, Page 1953, 16(14), 1953. [CrossRef]
  53. Naji, A., Rechdaoui, S. G., Jabagi, E., Lacroix, C., Azimi, S., & Rocher, V. (2023). Pilot-Scale Anaerobic Co-Digestion of Wastewater Sludge with Lignocellulosic Waste: A Study of Performance and Limits. Energies 2023, Vol. 16, Page 6595, 16(18), 6595. [CrossRef]
  54. Neri, A., Hummel, F., Benalia, S., Zimbalatti, G., Gabauer, W., Mihajlovic, I., & Bernardi, B. (2024). Use of Continuous Stirred Tank Reactors for Anaerobic Co-Digestion of Dairy and Meat Industry By-Products for Biogas Production. Sustainability (Switzerland) , 16(11), 4346. [CrossRef]
  55. Park, J. H., Kumar, G., Yun, Y. M., Kwon, J. C., & Kim, S. H. (2018). Effect of feeding mode and dilution on the performance and microbial community population in anaerobic digestion of food waste. Bioresource Technology, 248, 134–140. [CrossRef]
  56. Pilarski, K., Pilarska, A. A., & Pietrzak, M. B. (2025). Biogas Production in Agriculture: Technological, Environmental, and Socio-Economic Aspects. Energies 2025, Vol. 18, Page 5844, 18(21), 5844. [CrossRef]
  57. Prata, A. A., Santos, J. M., Timchenko, V., & Stuetz, R. M. (2018). A critical review on liquid-gas mass transfer models for estimating gaseous emissions from passive liquid surfaces in wastewater treatment plants. Water Research, 130, 388–406. [CrossRef]
  58. Qian, S., Chen, L., Xu, S., Zeng, C., Lian, X., Xia, Z., & Zou, J. (2025). Research on Methane-Rich Biogas Production Technology by Anaerobic Digestion Under Carbon Neutrality: A Review. Sustainability 2025, Vol. 17, Page 1425, 17(4), 1425. [CrossRef]
  59. Ramos, I., Díaz, I., & Fdz-Polanco, M. (2012). The role of the headspace in hydrogen sulfide removal during microaerobic digestion of sludge. Water Science and Technology : A Journal of the International Association on Water Pollution Research, 66(10), 2258–2264. [CrossRef]
  60. Raposo, F., Borja, R., & Ibelli-Bianco, C. (2020). Predictive regression models for biochemical methane potential tests of biomass samples: Pitfalls and challenges of laboratory measurements. Renewable and Sustainable Energy Reviews, 127, 109890. [CrossRef]
  61. Ribeiro, T., Cresson, R., Pommier, S., Preys, S., André, L., Béline, F., Bouchez, T., Bougrier, C., Buffière, P., Cacho, J., Camacho, P., Mazéas, L., Pauss, A., Pouech, P., Rouez, M., & Torrijos, M. (2020). Measurement of Biochemical Methane Potential of Heterogeneous Solid Substrates: Results of a Two-Phase French Inter-Laboratory Study. Water 2020, Vol. 12, Page 2814, 12(10), 2814. [CrossRef]
  62. Romero-Güiza, M., Peces, M., Asiain-Mira, R., Palatsi, J., & Astals, S. (2023). Microbial assessment of foaming dynamics in full-scale WWTP anaerobic digesters. Journal of Water Process Engineering, 56, 104269. [CrossRef]
  63. Sander, R. (2015). Compilation of Henry’s law constants (version 4.0) for water as solvent. Atmospheric Chemistry and Physics, 15(8), 4399–4981. [CrossRef]
  64. Sani, K., Jariyaboon, R., O-Thong, S., Cheirsilp, B., Kaparaju, P., Wang, Y., & Kongjan, P. (2022). Performance of pilot scale two-stage anaerobic co-digestion of waste activated sludge and greasy sludge under uncontrolled mesophilic temperature. Water Research, 221, 118736. [CrossRef]
  65. Sapunov, V. N., Saveljev, E. A., Voronov, M. S., Valtiner, M., & Linert, W. (2021). The Basic Theorem of Temperature-Dependent Processes. Thermo 2021, Vol. 1, Pages 45-60, 1(1), 45–60. [CrossRef]
  66. Scarlat, N., Dallemand, J. F., & Fahl, F. (2018). Biogas: Developments and perspectives in Europe. Renewable Energy, 129, 457–472. [CrossRef]
  67. Schaffka, F. T. S., Behainne, J. J. R., Parise, M. R., & De Castilho, G. J. (2021). Dynamics of the Pressure Fluctuation in the Riser of a Small Scale Circulating Fluidized Bed: Effect of the Solids Inventory and Fluidization Velocity Under the Absolute Mean Deviation Analysis. Mechanisms and Machine Science, 95, 419–430. [CrossRef]
  68. Sharma, A., Salhotra, S., Rathour, R. K., Solanki, P., Putatunda, C., Hans, M., Walia, A., & Bhatia, R. K. (2026). Recent developments in separation and storage of lignocellulosic biomass-derived liquid and gaseous biofuels: A comprehensive review. Biomass and Bioenergy, 204, 108417. [CrossRef]
  69. Siciliano, A., Limonti, C., & Curcio, G. M. (2021). Performance Evaluation of Pressurized Anaerobic Digestion (PDA) of Raw Compost Leachate. Fermentation 2022, Vol. 8, Page 15, 8(1), 15. [CrossRef]
  70. Situmorang, Y. A., Zhao, Z., Yoshida, A., Abudula, A., & Guan, G. (2020). Small-scale biomass gasification systems for power generation (.
  71. Song, S., Ginige, M. P., Cheng, K. Y., Qie, T., Peacock, C. S., & Kaksonen, A. H. (2023). Dynamics of gas distribution in batch-scale fermentation experiments: The unpredictive distribution of biogas between headspace and gas collection device. Journal of Cleaner Production, 400, 136641. [CrossRef]
  72. Song, Y., Mahdy, A., Hou, Z., Lin, M., Stinner, W., Qiao, W., & Dong, R. (2020). Air Supplement as a Stimulation Approach for the In Situ Desulfurization and Methanization Enhancement of Anaerobic Digestion of Chicken Manure. Energy & Fuels, 34(10), 12606–12615. [CrossRef]
  73. Stan, C., Collaguazo, G., Streche, C., Apostol, T., & Cocarta, D. M. (2018). Pilot-Scale Anaerobic Co-Digestion of the OFMSW: Improving Biogas Production and Startup. Sustainability 2018, Vol. 10, Page 1939, 10(6), 1939. [CrossRef]
  74. Strömberg, S., Nistor, M., & Liu, J. (2014). Towards eliminating systematic errors caused by the experimental conditions in Biochemical Methane Potential (BMP) tests. Waste Management, 34(11), 1939–1948. [CrossRef]
  75. Su, M. J., Luo, Y., Chu, G. W., Cai, Y., Le, Y., Zhang, L. L., & Chen, J. F. (2020). Dispersion behaviors of droplet impacting on wire mesh and process intensification by surface micro/nano-structure. Chemical Engineering Science, 219, 115593. [CrossRef]
  76. Tong, Z., Chen, Y., Malkawi, A., Liu, Z., & Freeman, R. B. (2016). Energy saving potential of natural ventilation in China: The impact of ambient air pollution. Applied Energy, 179, 660–668. [CrossRef]
  77. Tran, J. T., Warren, K. J., Wilson, S. A., Muhich, C. L., Musgrave, C. B., & Weimer, A. W. (2024). An updated review and perspective on efficient hydrogen generation via solar thermal water splitting. Wiley Interdisciplinary Reviews: Energy and Environment, 13(4), e528. [CrossRef]
  78. Tzenos, C. A., Kalamaras, S. D., Economou, E. A., Romanos, G. E., Veziri, C. M., Mitsopoulos, A., Menexes, G. C., Sfetsas, T., & Kotsopoulos, T. A. (2023). The Multifunctional Effect of Porous Additives on the Alleviation of Ammonia and Sulfate Co-Inhibition in Anaerobic Digestion. Sustainability (Switzerland), 15(13), 9994. [CrossRef]
  79. Valero, D., Montes, J. A., Rico, J. L., & Rico, C. (2016). Influence of headspace pressure on methane production in Biochemical Methane Potential (BMP) tests. Waste Management, 48, 193–198. [CrossRef]
  80. Vanegas, M., Romani, F., & Jiménez, M. (2022). Pilot-Scale Anaerobic Digestion of Pig Manure with Thermal Pretreatment: Stability Monitoring to Improve the Potential for Obtaining Methane. Processes 2022, Vol. 10, Page 1602, 10(8), 1602. [CrossRef]
  81. Vedat Yılmaz. (2017). Yılmaz / The Effects of Incubation and Operational Conditions on Biogas Production Karaelmas Fen Müh. Zonguldak Bülent Ecevit Üniversitesi, 7(2), 597–601.
  82. Wang, L., Shen, F., Yuan, H., Zou, D., Liu, Y., Zhu, B., & Li, X. (2014). Anaerobic co-digestion of kitchen waste and fruit/vegetable waste: Lab-scale and pilot-scale studies. Waste Management, 34(12), 2627–2633. [CrossRef]
  83. Wani, S. S., & Parveez, M. (2025). Synergistic effects of anaerobic digestion for diverse feedstocks: A holistic study on feedstock properties, process efficiency, biogas yield, and economic viability. Energy for Sustainable Development, 87, 101755. [CrossRef]
  84. Wu, Y., Kovalovszki, A., Pan, J., Lin, C., Liu, H., Duan, N., & Angelidaki, I. (2019). Early warning indicators for mesophilic anaerobic digestion of corn stalk: a combined experimental and simulation approach. Biotechnology for Biofuels 2019 12:1, 12(1), 1–15. [CrossRef]
  85. Wu, Y., Ye, X., Wang, Y., & Wang, L. (2023). Methane Production from Biomass by Thermochemical Conversion: A Review. Catalysts 2023, Vol. 13, Page 771, 13(4), 771. [CrossRef]
  86. Xiang, T., Qiang, F., Liu, G., Liu, C., Liu, Y., Ai, N., & Ma, H. (2023). Soil Quality Evaluation of Typical Vegetation and Their Response to Precipitation in Loess Hilly and Gully Areas. Forests, 14(9), 1909. [CrossRef]
  87. Xiong, S., Gong, D., Deng, Y., Tang, R., Li, L., Zhou, Z., Zheng, J., Yang, L., & Su, L. (2021). Facile one-pot magnetic modification of Enteromorpha prolifera derived biochar: Increased pore accessibility and Fe-loading enhances the removal of butachlor. Bioresource Technology, 337, 125407. [CrossRef]
  88. Xu, X., Ma, C., Li, Z., Lu, X., Yang, Z., & Ji, X. (2020). Effect of H2S in Raw Biogas on the Performance of Biogas Upgrading with High Pressure Water Scrubbing. [CrossRef]
  89. Yan, B. H., Selvam, A., & Wong, J. W. C. (2017). Influence of acidogenic headspace pressure on methane production under schematic of diversion of acidogenic off-gas to methanogenic reactor. Bioresource Technology, 245, Part A, 1000–1007. [CrossRef]
  90. Yang, Z., Larsen, O. C., Muhayodin, F., Hu, J., Xue, B., & Rotter, V. S. (2024). Review of anaerobic digestion models for organic solid waste treatment with a focus on the fates of C, N, and P. Energy, Ecology and Environment 2024 10:1, 10(1), 1–14. [CrossRef]
  91. Yepes-Nuñez, J. J., Urrútia, G., Romero-García, M., & Alonso-Fernández, S. (2021). Declaración PRISMA 2020: una guía actualizada para la publicación de revisiones sistemáticas. Revista Española de Cardiología, 74(9), 790–799. [CrossRef]
  92. Yirong, C., Zhang, W., Heaven, S., & Banks, C. J. (2017). Influence of ammonia in the anaerobic digestion of food waste. Journal of Environmental Chemical Engineering, 5(5), 5131–5142. [CrossRef]
  93. Zhang, Y., Xiong, W., Liu, W., Chen, X., & Yao, J. (2025). Research on Anaerobic Digestion Characteristics and Biogas Engineering Treatment of Steroidal Pharmaceutical Wastewater. Energies 2025, Vol. 18, Page 5555, 18(21), 5555. [CrossRef]
Figure 1. PRISMA 2020 flowchart of the selection process.
Figure 1. PRISMA 2020 flowchart of the selection process.
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Table 1. Physicochemical and design parameters relevant to headspace in batch biodigesters and safety considerations.
Table 1. Physicochemical and design parameters relevant to headspace in batch biodigesters and safety considerations.
Category Parameter/relationship Typical value/expression Technical comment References
Gas status Equation of state PVHS = ng RT Ideal gas equation valid at moderate pressures; it is recommended to correct for water vapor when normalizing dry biogas (Angelidaki et al., 2018)
Gaseous capacitance Ce = (∂ng /∂ P)T Ce = VHS/(RT) Capacitance increases with dome volume; it reduces pressure variation d P d t . Flexible domes increase effective capacitance. (Yang et al., 2024)
Partial pressure Dalton's Law Pi = yiP Determine the equilibrium concentration C i * using Henry's Law and the mass transfer driving force (Su et al., 2020)
Henry's constant (CO2) C C O 2 * = P C O 2 H C O 2 T HCO2 (25 °C) ≈ 29 bar·m3·kmol−1;
d(ln H)/d(1/T) ≈ ΔHsol/R.
It decreases with temperature, increasing "stripping" in thermophilic. (Sander, 2015)
Henry's constant (H2S) C H 2 S * = P H 2 S H H 2 S T HH2S (25 °C) ≈ 1.0 bar·m3·kmol−1 It exhibits high solubility. Speciation depends on pH (H2S/HS⁻ equilibrium). (Sander, 2015)
Balance pKa, N H 4 + / N H 3 pKa ≈ 9.25 (25 °C), decrece con T The fractionation of N H 3 free increases with pH and temperature; risk of biological inhibition at high values. (Yirong et al., 2017)
Gas-liquid transfer Gas-liquid mass transfer flow Ni​=kL​a(C−C) kLa ~ 10−3-10−2 s−1 in sludge with solids; intermittent agitation improves k L a but may induce foaming. (Prata et al., 2018)
Carbonate system pKa1 /pKa2 pKa1 ≈ 6.35; pKa2 ≈ 10.33 (25 °C) “Stripping” raises pH and alkalinity; it interacts with the free ammonia balance. (Sapunov et al., 2021)
Ranges VHS/Vtot Laboratory vs. pilot/farm BMP: 0.30–0.50; Pilot/farm: 0.10–0.25 Compromise between metrological safety and structural compactness. (Hafner et al., 2020)
Materials Chemical compatibility Stainless steel, GRP, EPDM/PTFE Materials resistant to H₂S and NH₃; attention to permeability and thermal or UV aging of membranes. (Pilarski et al., 2025)
Security Relief and venting Setpoint < Pdesign; non-return valve and torch. Compliance with NFPA/ATEX regulations; CH₄ and H₂S monitoring; gas line condensate management. (Luo et al., 2022)
Note. Symbols and abbreviations: P = total gas pressure (bar or Pa); V H S =headspace volume (m³); n g = number of moles of gas (mol); R = universal gas constant (8.314 J·mol⁻¹.K⁻¹); T = absolute temperature (K); C e = gas capacitance, defined as ( n g P ) T (mol·bar⁻¹ or mol.Pa⁻¹); P i = partial pressure of component i (bar or Pa); y i = mole fraction of component i in gas phase (dimensionless); C i * = equilibrium concentration of component i in liquid phase (mol.m⁻³); H i ( T ) = temperature-dependent Henry's law constant (bar.m³.mol⁻¹); Δ H s o l = molar enthalpy of solution (J.mol⁻¹); N i = molar flow rate of component transfer i (mol·m⁻².s⁻¹); k L a = volumetric mass transfer coefficient (s⁻¹); C = concentration of the solute in the liquid phase (mol.m⁻³); C * = equilibrium concentration in the liquid phase (mol.m⁻³); p K a , p K a 1 , p K a 2 = negative logarithms of the dissociation constants of the acid-base system (dimensionless); V t o t = total volume of the reactor (m³); P d e s i n g = design pressure of the system (bar or Pa).
Table 2. Headspace in biogas batch systems and operational considerations.
Table 2. Headspace in biogas batch systems and operational considerations.
Headspace conditions Relevant results Comment Reference
BMP bottles: headspace 50, 90 and 180 mL (constant medium 70 mL) Larger headspace volume means less pressure buildup; better biogas yield; relatively stable methane yield. Methodological approach for BMP trials, showing free volume effect. (Himanshu et al., 2017)
Tests with coffee residues, cocoa husks and manure; headspace overpressures > 600 mbar In coffee waste, overpressure >600 mbar reduced methane input; for other substrates there was no adverse effect in the 600-1000 -mbar range. Evidence that headspace pressure impacts depending on the type of substrate. (Valero et al., 2016)
Headspace pressure: 12.6 psi (~0.87 bar), 6.3 psi (~0.43 bar), 3.3 psi (~0.23 bar) and ambient Pressure ~3 -6 psi improved COD production ~22 -36%, solubles ~9 -43%, volatile solids reduction ~14 -19% and methane +10 -31% vs control. It shows that a moderate headspace pressure favors the hydrolytic/acidogenic phase and improves methanogenesis. (Yan et al., 2017)
BMP trials: headspace fraction 0.25 (40 mL in 160 mL bottle) versus 0.75 Measurement error up to ~24% with headspace fraction 0.25; ~3% with fraction 0.75. Relative error in CH₄ increased with headspace pressure. Evidence that free volume/headspace fraction has an impact on the accuracy of measurements. (Hafner & Astals , 2019)
Headspace flushing test: N₂, N₂/CO₂ (80/20), without flushing Flushing with 20% CO₂ increased methane production >20% in inoculum alone compared to pure N₂ flushing . The effect of gas composition on headspace is more important than volume/pressure. (Koch et al., 2015a)
Study of working volume-headspace ratio in BMP assays They mention that headspace conditions affect biogas production; not much numerical quantification. Recognition of the “Headspace Volume Fraction” (HSVF) as a design variable remains limited. (Elsayed et al., 2022)
225 L reactor: headspace volume 40% versus 60% At 40% headspace, VFA production is ten times greater than at 60%; changes in microbial community. Although focused on VFA, it shows the impact of headspace volume on microbiology and performance. (Di Leto et al., 2024)
BMP review: headspace in typical tests 10 mL to 1400 mL; headspace volume fraction % varies widely It indicates that headspace varies between ~10 to ~76% of the total volume and that this variable should be considered in design. It reinforces that the literature considers headspace as a variable, but with scattered data. (Cabrita & Santos, 2023a)
Pilot reactor 265 L: headspace volume 50.0 L, 9.5 L, 1.5 L; micro-oxygenation for H₂S removal H₂S removal of 99% with headspace 50 L or 9.5 L; fell to ≈15% when headspace reduced to 1.5 L. It shows that the available volume of gas-headspace impacts H₂S transfer and removal. (Ramos et al., 2012)
Test with relative pressure in the range 300-800 mbar (≈0.3-0.8 bar) in biogas/hydrogen CH₄ > 3.9 mmol/L when relative pressure between 300 and 800 mbar; indirect pressure/headspace contributions. Although focused on hydrogen, it provides data on the relative pressure of the gas-headspace in digestion. (Mahmoodi-Eshkaftakia & Mockaitis, 2022)
General review: digesting internal pressure, including headspace, is noted as a variable. It indicates that the solubility of the gases (CO₂/CH₄) increases with pressure, which can increase CH₄ in free gas; but it also warns of negative effects of high pressure. It supports the physical -and chemical basis of the pressure effect on headspace. (Aworanti et al., 2023)
500 mL bottles: working volumes 125, 200, 300, 400 mL → corresponding headspace 80%, 60%, 40%, 20% Reactors with lower working volume (greater headspace) produced a higher percentage of methane (~14-23 -% more than those with greater liquid volume) It indicates that a larger volume of free gas (greater headspace) favors biogas/methane production in BMP. (Vedat Yılmaz, 2017)
Chicken manure digestion batch ; air injection into the headspace (technique variation) H₂S removal down to ~1015 ppm and CH₄ increase by 6.4% with air injection into the headspace. Operational example of how headspace (gas) management improves biogas quality. (Y. Song et al., 2020)
Food waste fermentation bed: headspace conditions T1 (self-generated), T2 (30% CO₂ + 70% N₂), T3 (90% CO₂ + 10% N₂) T3 (90% CO₂ in headspace) gave a soluble yield of 0.81 g COD/g VS removal, significantly higher than others Although it does not directly analyze methane, it shows that headspace composition (CO₂) affects acid and biogas yield. (C. Liu et al., 2025)
Full-scale plant review mentions that headspace conditions influence the fermentation process, including headspace volume and pressure. He points out that, although these effects are recognized, the literature does not quantify them well; he calls for research into the relationship between headspace volume/pressure and biogas production. It serves as an argument for the research gap on the topic. (Kouzi et al., 2020)
Note: T1: self-generated (gas autogenerado por la fermentación, sin ajuste externo), T2: 30% CO₂ + 70% N₂ (headspace ajustado/flush con esa mezcla), T3: 90% CO₂ + 10% N₂ (headspace ajustado/flush con alta fracción de CO₂).
Table 3. Typical operating parameters and headspace volume ratios in anaerobic systems.
Table 3. Typical operating parameters and headspace volume ratios in anaerobic systems.
Reactor scale/type Type of substrate Typical range VHS /Vtot (-) Operating pressure (kPa) T (°C) Agitation Monitoring method CH₄ production (unit) (reported/compiled) Material Reference (DOI)
BMP (500 mL bottle) Bovine manure 0.25-0.35 101-120 37 Intermittent Displacement/manometric ~129-366 mL CH4.g⁻¹ VS (experimental range reported in BMP literature for cow manure (compiled). Glass ( Hilgert et al., 2023)
BMP (1 L) Anaerobic sludge 0.30-0.40 101-130 35 Intermittent GC–TCD ~100-230 mL CH₄. g⁻¹ VS (ranges reported in reviews/BMP studies ; compiled). Plastic/PP (Díaz-Domínguez et al., 2025a)
Laboratory reactor (5 L) Food waste 0.20-0.30 110-150 38 Continue NDIR 0.6-1.2 L CH₄ · L⁻¹.d⁻¹ (experimental ranges on bench-scale) food waste reactors; compiled). Stainless steel ( Jiang et al., 2023)
Pilot reactor (20 L) Pig slurry 0.15-0.25 120-160 37 Intermittent Flow meter + GC ~0.6-1.3 L CH4.L⁻¹. d⁻¹ (ranges obtained in pilot tests with pig slurry (compiled). Stainless steel (Ma et al., 2023)
Pilot reactor (50 L) Plant waste 0.20-0.35 110–140 35 Continuous mechanics NDIR 0.7-1.2 L CH4.L⁻¹. d⁻¹ (reported in pilot studies of co-digestion/food waste; compiled). Stainless steel (Wang et al., 2014)
Semi-industrial reactor (200 L) Sewage 0.10-0.20 150-180 36 Continue GC + pressure 0.5-1.0 L CH4. L⁻¹.d⁻¹ (ranges in semi-industrial plants; compiled). Carbon steel ( Sani et al., 2022)
Industrial reactor (1000 L) Mixed substrate 0.05-0.10 160-200 37 Continue NDIR + H₂S 0.8-1.6 L CH4. L⁻¹.d⁻¹ (industrial ranges reported in reviews/case studies; compiled). Stainless steel ( Alqaralleh et al., 2018)
UASB reactor Urban wastewater 0.10-0.15 120-140 35 Without agitation Flow meter 0.2-3.1 L CH4. L⁻¹.d⁻¹ (high variability; maximum values reported under specific conditions as vinasse; reported/compiled). Coated concrete (Barbosa et al., 2022)
CSTR reactor (2 m³) Co-digestion 0.08-0.12 150-180 38 Mechanical + recirculation GC–TCD 1.0-1.6 L CH4. L⁻¹.d⁻¹ (ranges reported for CSTR co-digestion a pilot) scale (compiled). Stainless steel (Neri et al., 2024a)
Mesophilic reactor (5 m³) Poultry manure 0.10-0.15 160-190 37 Mechanics NDIR + flow meter 0.9-1.3 L CH4. L⁻¹·d⁻¹ (mesophilic full-scale reports ranges; compiled ). Fiberglass (Díaz-Domínguez et al., 2025b)
Thermophilic reactor (10 m³) Agricultural waste 0.05-0.10 180-220 55 Mechanics GC + P/T 1.2-2.2 L CH4. L⁻¹·d⁻¹ (best thermophilic performance in several studies; compiled). Stainless steel (Park et al., 2018)
Industrial reactor (20 m³) Mixed urban sludge 0.05-0.08 180-240 38 Mechanics GC + H₂S 1.0-1.6 L CH4. L⁻¹·d⁻¹ (ranges compiled from plant case studies; compiled). Stainless steel ( Sani et al., 2022)
Note: VHS /Vtot: volumetric fraction of headspace (gas volume/total reactor volume), dimensionless, HS: headspace (gaseous volume above the liquid phase), BMP: biochemical methane potential, UASB: upflow anaerobic sludge blanket, CSTR: continuous stirred-tank reactor, GC–TCD: gas chromatography with thermal conductivity detector, NDIR: nondispersive infrared, H₂S: hydrogen sulfide, P/T: pressure and temperature, VS: volatile solids, L CH₄ . L⁻¹. d⁻¹: liters of methane per liter of reactor per day (volumetric productivity), mL CH4. g⁻¹ VS: milliliters of methane per gram of volatile solids (specific yield), kPa: kilopascal.
Table 4. Verified parameters and methanogenic productivity ranges according to scale and headspace fraction.
Table 4. Verified parameters and methanogenic productivity ranges according to scale and headspace fraction.
Reactor scale/type Type of substrate V HS /V tot (-) Pressure (kPa) CH₄ production (unit) References
BMP (500 mL ) Bovine manure 0.25-0.35 (compiled) ≈ 101-130 129-366 mL CH4.g⁻¹ VS (compiled) (Hafner & Astals, 2019)
BMP (1 L) Anaerobic sludge 0.30-0.40 (compiled) ≈ 101-130 140-230 mL CH₄.g⁻¹ VS (compiled) (Filer et al., 2019)
Laboratory (5 L) Food waste 0.20-0.30 (reported) 110-150 0.6-1.2 L CH₄.L⁻¹.d⁻¹ (reported) ( Xiang et al., 2023)
Pilot (20 L) Pig slurry 0.15-0.25 (reported) 120-160 0.9-1.3 L CH₄.L⁻¹.d⁻¹ (reported) (Vanegas et al., 2022)
Pilot (50 L) Plant residues 0.20-0.30 (filled) 110-140 0.7-1.2 L CH₄.L⁻¹.d⁻¹ (compiled) (Maragkaki et al., 2023)
Semi-industrial (200 L) Aguas residuales 0.10-0.20 (reported) 150–180 0.5-1.0 L CH₄.L⁻¹.d⁻¹ (reported) ( Naji et al., 2023)
Industrial (1000 L) Mixed substrate 0.05-0.10 (filled) 160-200 0.8-1.6 L CH₄.L⁻¹.d⁻¹ (compiled) (Kovalev et al., 2022)
UASB reactor Wastewater/vinasse 0.10-0.15 (reported) 120-140 0.2-3.1 L CH₄·L⁻¹.d⁻¹ (reported) (Estrada-Arriaga et al., 2021)
CSTR (2 m³) Co-digested 0.08-0.12 (compiled) 150-180 1.0-1.6 L CH₄.L⁻¹.d⁻¹ (compiled) (Neri et al., 2024b)
Thermophilic (10 m³) Agricultural waste 0.05-0.10 (compiled) 180-220 1.2-2.2 L CH₄.L-1.d-1 (compiled) (Y. Liu et al., 2019)
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