
BMP testingBy-products of the agri-food industry
Hemp hurds and dust — BMP: 2 studies, weighted mean 212 m³ CH₄/t VS
Hemp shives and dust are woody residues of hemp fibre, rich in lignin and cellulose; digestion is slow and requires size reduction or pretreatment.
rating: goodCH₄ ≈ 52 % (estimate)
Photo Florian Gerlach (Nawaro) / Wikimedia Commons, licence CC BY-SA 3.0, source file; changes: cropping
- Weighted mean
- 212m³ CH₄/t VS
- Range
- 184–239m³ CH₄/t VS
- Records
- 2studies
- Publications
- 2sources
- Temperatures
- 38 °Cof the test
Methane in biogas
Medium methane content · ≈ 5.2 kWh/m³ of biogas
estimate from the substrate type The collected studies contain no measurement. The interval follows from the approximate composition (protein from total nitrogen (N 0.8 % DM × 6.25)) and the yields of compound groups according to FNR.
Rating for biogas plants
good — editorial rating for biogas plantsStable, usually accepted without a fee
Potential per tonne of fresh matter: very high (145 m³ CH₄/t); no particular threats to stability. Handling costs: fibres, floating layer, slow degradation.
Why? Rating factors
Potential per tonne +3
- +3potential 145 m³ CH₄/t fresh matter (BMP 212 × DM 88.1 % × VS 78 %)
Process stability 0
- 0no factors
Handling and costs −1
- −0.5fibres, floating layer — shredding and intensive mixing
- −0.5slow degradation — long retention time
Total points: 2 · thresholds: ≥ 2.5 very good, ≥ 1 good, below — neutral; negative with cumulative process risk.
Add to the co-digestion calculator CSV data
BMP curves from 2 studies
Weighted mean Individual records
Dashed lines are a model curve (first-order kinetics, B(t) = B₀·(1 − e−kt)); the end point comes from the publication. All curves are model curves.
Cumulative methane production over the test [m³ CH₄/t VS]. The thick line is the weighted mean of all records (212); dots mark the end values given in the publications. Point at the chart to read values; click a legend item to hide or show a record.
Records and sources
Download CSV| Source | BMP m³ CH₄/t VS | Temperature | Sample | Curve |
|---|---|---|---|---|
| Lallement et al. (2023) DOI | 184 | 38 °C · mesophilic | hemp dust | end point (model curve) |
| Matassa et al. (2020) DOI | 239 | — | Unretted hurds | end point (model curve) |
| Weighted mean | 212 | arithmetic mean 212, SD 39 | ||
Typical composition
- Dry matter (DM)
- 88.1% (range 88.1–88.1)
- Volatile solids (VS)
- 78 % DM (range 78–78)
- Nitrogen
- 0.8 % DM
- C/N ratio
- 49.5
Median and range of the determinations reported in the publications behind this substrate's BMP records (read from: MY-D); dry matter: 1 determination, volatile solids: 1 determination. C/N was calculated as the ratio of C and N content (% DM) from the same source. Samples were tested dried/air-dry – the DM refers to the material in the test, not to fresh material.
Sources: Lallement et al. (2023).
The composition of the raw material varies between batches — for plant calculations use an analysis of your own sample. The calculator inserts typical values automatically.
Process properties
Low confidence: the description is based on general characteristics of the substrate group, not on studies of this material. Treat it as a hint to be verified.
Advantages
- Methane potential in the Substraty.pl BMP dataset: weighted mean 211.7 m³ CH₄/t VS (SD 38.6; 2 records, 2 sources).
- Hemp shives: a dry, durable material, no risk of acidification - does not burden the VFA system (Hendriks and Zeeman 2009).
Drawbacks and risks
- Dust - risk of dust generation (a physical property of the material).
Co-digestion — what to combine it with, what to watch out for
- combines well
substrates: high alkalinity (buffer) — e.g. Cattle manure, Pig slurry, Cattle slurry, Duck slurry, Rumen and digestive tract content
Slurry supplies N and alkalinity, balancing the high C/N of the material.[1][2]
- combines well
substrates: protein-rich — e.g. Food waste, Municipal sewage sludge (mixed), Poultry manure, Organic fraction of municipal solid waste, Grass clippings
The high C/N of the material balances protein substrates, limiting the ammonia risk.[1][3]
Dosing
No source limits on the dose for this substrate.
Introduce gradually, starting with a small dose and monitoring the process (e.g. FOS/TAC, pH, gas composition).
Practical requirements
- Shred: shredding increases the surface available for degradation and speeds it up, but does not necessarily raise the final gas yield (FNR 2010, Ch. 3 “Triturado”).
- Control floating crust and sediment: when solids are fed directly into the digester, the risk of their formation depends on the substrate (FNR 2010, Ch. 3).
Sources of the process data
- Hagos et al. (2017). Anaerobic co-digestion process for biogas production: progress, challenges and perspectives. Renew. Sustain. Energy Rev.
- Weiland (2010). Biogas production: current state and perspectives. Appl. Microbiol. Biotechnol.
- Rajagopal, Masse, Singh (2013). A critical review on inhibition of anaerobic digestion process by excess ammonia. Bioresour. Technol.
- Hendriks, Zeeman (2009). Pretreatments to enhance the digestibility of lignocellulosic biomass. Bioresour. Technol.
- FNR (2010). Guía sobre el Biogás – Desde la producción hasta el uso (hiszp. wydanie „Leitfaden Biogas”, GIZ 2013)
The co-digestion calculator will assess a specific mixture containing this substrate.
What it is and where it comes from
Fibre hemp (Cannabis sativa) is grown for fibre and seeds. During stem processing the bast fibre is separated from the woody core, that is, the shives, and dust also arises on this occasion. Shives are used as bedding, insulation material (hempcrete) or briquettes, so at a biogas plant they occur as a waste or a product of low commercial value. In Poland fibre hemp is grown on a limited scale, so the stream is small.
Properties relevant to digestion
Shives are a lignocellulosic material with a high lignin and cellulose content and a low content of soluble sugars and protein. The structure is compact and poorly accessible to enzymes, which causes slow hydrolysis and a low share of rapidly degradable fraction. Unlike sugar-rich materials there is no risk of acidification, but the gas potential depends on size reduction and pretreatment. Dust is finer and may contain more bast fibre particles. A high C/N ratio means the material combines well with slurry as a source of nitrogen and buffer. Dry dust poses a dust hazard.
How to read the spread of results
The dataset contains several records from several sources: hemp dust under mesophilic conditions and non-retted shives from a second source. Differences result from the hemp variety, harvest date, decortication method, degree of size reduction and the duration of the test, which for woody materials must be long. Retting, that is, partial biological decomposition of the stems in the field, changes the composition, so the result for retted and non-retted shives is not interchangeable.
In biogas plant practice
Shives can be added at a small share to co-digestion, after milling, together with materials that degrade quickly. Without pretreatment (steam, alkaline, mechanical) utilisation is partial. The material stores well if it is dry, and its low bulk density raises transport costs. Competition from other uses often decides that it does not go to a biogas plant. The legal status depends on the origin: waste from processing is subject to the waste rules.
An additional barrier is the low bulk density of shives, which makes transport and feeding to the digester difficult. It is usually necessary to briquette them, mill them or mix them with a liquid feed, which raises costs and limits the cost-effectiveness of using this material.
Methodology in brief
BMP is the amount of methane obtained from volatile solids (VS) in a batch test, given in m³ CH₄ per tonne of VS (numerically the same as NmL CH₄/g VS in the publications) and converted to normal conditions (0 °C, 101.325 kPa). The weighted mean gives each publication a total weight of 1, split equally between its results for the substrate — a paper testing twenty varieties does not outweigh a paper with a single sample. In inter-laboratory programmes the unit is the laboratory (total weight 1), and within it the weight of a test grows with the number of bottles (replicates). Results after pretreatment (e.g. thermal, chemical, enzymatic) are shown separately and are not included in the mean.
Solid lines are curves measured in the tests. Where a publication gives only the final result, we draw a first-order kinetic model, B(t) = B₀·(1 − e−kt): only the end point comes from the publication, and the shape of the curve serves purely as visualisation — do not read the production on a particular day from it. For this substrate k = 0.091 d−1 was assumed (no kinetic data for the group – the median of all available rate constants k (93 values) was used).
The statistics describe the spread of published results — a descriptive compilation, not a meta-analysis or a guarantee of plant yield.
Bibliography
- Lallement, A.; Peyrelasse, C.; Lagnet, C.; Barakat, A.; Schraauwers, B.; Maunas, S.; Monlau, F. (2023). A Detailed Database of the Chemical Properties and Methane Potential of Biomasses Covering a Large Range of Common Agricultural Biogas Plant Feedstocks. Waste 1(1), 195–227. DOI: 10.3390/waste1010014 DOI
- Matassa, S.; Esposito, G.; Pirozzi, F.; Papirio, S. (2020). Exploring the Biomethane Potential of Different Industrial Hemp (Cannabis sativa L.) Biomass Residues. Energies 13(13), 3361. DOI: 10.3390/en13133361 DOI
All sources of the site: bibliography.





