
BMP testingGrasses, green forage and fodder plants
Proso millet, whole crop — BMP: 2 studies, weighted mean 260 m³ CH₄/t VS
Common millet as a whole plant is a thermophilic cereal considered as an energy crop on lighter soils. The compilation describes it with a small number of records from different studies.
rating: goodCH₄ ≈ 52 % (estimate)
Photo Roger Culos / Wikimedia Commons, licence CC BY-SA 4.0, source file; changes: cropping
- Weighted mean
- 260m³ CH₄/t VS
- Range
- 253–268m³ CH₄/t VS
- Records
- 2studies
- Publications
- 2sources
- Temperatures
- 38 °Cof the test
Methane in biogas
Low 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: high (53 m³ CH₄/t); no particular threats to stability. Handling costs: fibres, floating layer.
Why? Rating factors
Potential per tonne +2
- +2potential 53 m³ CH₄/t fresh matter (BMP 260 × DM 22.4 % × VS 91.5 %)
Process stability 0
- 0no factors
Handling and costs −0.5
- −0.5fibres, floating layer — shredding and intensive mixing
Total points: 1.5 · 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 (260); 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 |
|---|---|---|---|---|
| Garcia et al. (2019) DOI | 253 | — | millet - Panicum Miliaceum L. | end point (model curve) |
| Lallement et al. (2023) DOI | 268 | 38 °C · mesophilic | millet | end point (model curve) |
| Weighted mean | 260 | arithmetic mean 260, SD 10 | ||
Typical composition
- Dry matter (DM)
- 22.4% (range 21.8–22.9)
- Volatile solids (VS)
- 91.5 % DM (range 91–92)
- Nitrogen
- 0.8 % DM
- C/N ratio
- 53.4
Median and range of the determinations reported in the publications behind this substrate's BMP records (read from: MY-D); dry matter: 2 determinations, volatile solids: 2 determinations. C/N was calculated as the ratio of C and N content (% DM) from the same source.
Sources: Garcia et al. (2019); 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.
No published process studies
The literature we use does not describe the advantages or drawbacks of digesting this substrate beyond the BMP test results. Below are process characteristics assigned on the basis of the type of material — an editorial classification, not a study result.
- seasonal
- seasonal availability — requires storage
- fibrous
- lignocellulose, long fibres → floating layer, harder mixing, slow degradation
Co-digestion — what to combine it with, what to watch out for
- combines well
group: Animal excreta (slurry, manure, poultry litter)
Co-digestion with excreta (slurry/solid manure) is the standard arrangement for plant biomass: they supply alkalinity and microflora.[1][2]
Dosing
Introduce gradually, starting with a small dose and monitoring the process (e.g. FOS/TAC, pH, gas composition).
Practical requirements
- Ensiling makes it possible to store seasonal biomass; properly ensiled plants (in the study maize, sorghum, forage rye, triticale) can be stored for up to a year without loss of methane production (Herrmann et al. 2011).
Sources of the process data
- Garcia, N.H.; Mattioli, A.; Gil, A.; Frison, N.; Battista, F.; Bolzonella, D. (2019) Evaluation of the methane potential of different agricultural and food processing substrates for improved biogas production in rural areas. Renewable and Sustainable Energy Reviews 112, 1–10
- Weiland, P. (2010) Biogas production: current state and perspectives. Applied Microbiology and Biotechnology
- Hendriks, A.T.W.M.; Zeeman, G. (2009) Pretreatments to enhance the digestibility of lignocellulosic biomass. Bioresource Technology
- 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
- Herrmann et al. (2011). Effects of ensiling, silage additives and storage period on methane formation of biogas crops. Bioresour. Technol.
The co-digestion calculator will assess a specific mixture containing this substrate.
What it is and where it comes from
Common millet (Panicum miliaceum) is an annual grass grown for grain and fodder, with a short growing period and good drought tolerance. In Poland it is grown on a small scale, but because of climate change interest in plants resistant to water shortage is growing. In the biogas context it is studied as a whole plant harvested for green forage or silage. The compilation contains several records from several studies.
Properties relevant to digestion
The green biomass of millet is similar in character to other cultivated grasses: it supplies structural carbohydrates and small amounts of protein. Digestibility depends strongly on the harvest date: before grain formation the biomass is more readily degradable, later the fibre share rises. Ensiling is possible with sufficient dry matter and sugar content. Because of a C-to-N ratio higher than in legumes, mixing with slurry or another nitrogen-rich substrate is beneficial.
How to read the spread of results
The compilation has few records: some from a study in which the test temperature is not given, some from mesophilic conditions. They differ in variety, harvest date, form of the material, sample preparation and test parameters. The year of cultivation and the course of the weather, which determines the proportion of leaves, stems and ears, also have an effect. The small number of measurements does not allow the full variability of the material to be assessed, so the result is treated as indicative.
In biogas plant practice
Millet as a whole plant can be an addition to the mix on farms on poorer soils, as a crop more drought-resistant than maize. It requires harvesting with a forage harvester, ensiling in the manner typical of grasses and quality control. In the ration it behaves like other grass silages. Cost-effectiveness depends on the green mass yield, which should be assessed locally, and on the price of competing substrates. A BMP test is recommended before introduction on a wider scale. In choosing a species for energy cropping it is good to consider not only the gas potential but also yield stability in dry years, cultivation costs and the availability of harvesting equipment, because these determine the final cost of a unit of energy from biogas.
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
- Garcia, N.H.; Mattioli, A.; Gil, A.; Frison, N.; Battista, F.; Bolzonella, D. (2019). Evaluation of the methane potential of different agricultural and food processing substrates for improved biogas production in rural areas. Renewable and Sustainable Energy Reviews 112, 1–10. DOI: 10.1016/j.rser.2019.05.040 DOI
- 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
All sources of the site: bibliography.





