Physicochemical characterisation and dry anaerobic digestion of food and garden waste

Optimising the anaerobic digestion of food and garden waste is traditionally governed by the carbon-to-nitrogen ratio (C:N). However, in high-solids environments, this approach often fails to account for the physical recalcitrance and mass-transfer hurdles of lignocellulosic biomass. This study presents a detailed characterisation of food and garden waste and evaluates their specific biomethane yield through anaerobic mono-digestion (AmoD) and co-digestion (AcoD) across C:N range of 15–45 and total solids content (TS) of >15%. In AcoD, the results showed a synergistic peak at C:N 33, achieving a specific methane yield of 198 NmL/gVS in . In comparison, AmoD of grass (C:N 26.8) yielded 149 NmL/gVS in higher than AcoD at similar C:N. This highlights that digestion performance depends on substrate composition beyond nutrient balance, a key insight not previously reported for AcoD of food and garden wastes. Biodegradability Index proved that FG33 (FG33–stands for food and garden waste with C:N 33) reached 46% of its theoretical biomethane potential, compared to only 23% in the lignin-rich FG39. This difference highlights the lignin sheath as the main factor to sequester carbon in high-solids systems, regardless of available nitrogen. Furthermore, adding food waste and acclimatised inoculum from AmoD to AcoD eliminated the extended lag phase, demonstrating that lignocellulose-adapted microbes can reduce dependence on pretreatments to hydrolyse lignin. This has practical implications for scaling up, where pretreatment may not be feasible due to economic and practical constraints. Optimisng the substrate-to-inoculum ratio with lignocellulose-adapted microbes may further improve biomethane yield and volatile solids reduction in dry AD. • Dry AD of food and garden waste was evaluated across a wide C:N range (15.5-42.9) with C:N 33 identified as optimum. • Co-digestion of food and garden waste (25:75) achieved the maximum specific biomethane yield of 198 NmL/gVS in at C:N 33. • Substrate composition (lignin, cellulose and hemicellulose) influences methane yield more significantly than the stoichiometric C:N ratio. • Higher hemicellulose content of grass was easier to biodegrade than the lignin rich leaves and twigs fractions. • C:N 33 reached biodegradability index of 46%, compared to only 23% for the lignin-rich C:N 39 waste.

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Publication Details

Journal
Biomass and Bioenergy
Published
2026-03-31
DOI
https://doi.org/10.1016/j.biombioe.2026.109345
Primary Topic
Food Waste Reduction and Sustainability
Type
article
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article

Physicochemical characterisation and dry anaerobic digestion of food and garden waste

Dharmappa Hagare, Zuhaib Siddiqui
Biomass and Bioenergy
Food Waste Reduction and Sustainability
article

Physicochemical characterisation and dry anaerobic digestion of food and garden waste

Dharmappa Hagare, Zuhaib Siddiqui
article en

Abstract

Optimising the anaerobic digestion of food and garden waste is traditionally governed by the carbon-to-nitrogen ratio (C:N). However, in high-solids environments, this approach often fails to account for the physical recalcitrance and mass-transfer hurdles of lignocellulosic biomass. This study presents a detailed characterisation of food and garden waste and evaluates their specific biomethane yield through anaerobic mono-digestion (AmoD) and co-digestion (AcoD) across C:N range of 15–45 and total solids content (TS) of >15%. In AcoD, the results showed a synergistic peak at C:N 33, achieving a specific methane yield of 198 NmL/gVS in . In comparison, AmoD of grass (C:N 26.8) yielded 149 NmL/gVS in higher than AcoD at similar C:N. This highlights that digestion performance depends on substrate composition beyond nutrient balance, a key insight not previously reported for AcoD of food and garden wastes. Biodegradability Index proved that FG33 (FG33–stands for food and garden waste with C:N 33) reached 46% of its theoretical biomethane potential, compared to only 23% in the lignin-rich FG39. This difference highlights the lignin sheath as the main factor to sequester carbon in high-solids systems, regardless of available nitrogen. Furthermore, adding food waste and acclimatised inoculum from AmoD to AcoD eliminated the extended lag phase, demonstrating that lignocellulose-adapted microbes can reduce dependence on pretreatments to hydrolyse lignin. This has practical implications for scaling up, where pretreatment may not be feasible due to economic and practical constraints. Optimisng the substrate-to-inoculum ratio with lignocellulose-adapted microbes may further improve biomethane yield and volatile solids reduction in dry AD. • Dry AD of food and garden waste was evaluated across a wide C:N range (15.5-42.9) with C:N 33 identified as optimum. • Co-digestion of food and garden waste (25:75) achieved the maximum specific biomethane yield of 198 NmL/gVS in at C:N 33. • Substrate composition (lignin, cellulose and hemicellulose) influences methane yield more significantly than the stoichiometric C:N ratio. • Higher hemicellulose content of grass was easier to biodegrade than the lignin rich leaves and twigs fractions. • C:N 33 reached biodegradability index of 46%, compared to only 23% for the lignin-rich C:N 39 waste.

Biomass and BioenergyVol. 212
Western Sydney University (AU)
Zero hunger
Openalex Percentile: Top 29%
Food Waste Reduction and Sustainability
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