
BMP testingFruit, vegetables and their residues
Tropical tubers (sweet potato, Chinese yam) — BMP: 2 studies, weighted mean 280 m³ CH₄/t VS
The tropical tubers in the dataset are sweet potatoes and Chinese yam; starchy roots from several studies are characterised by high degradability and low lignin content.
rating: goodCH₄ ≈ 52 % (estimate)
Photo Llez / Wikimedia Commons, licence CC BY-SA 3.0, source file; changes: cropping
- Weighted mean
- 280m³ CH₄/t VS
- Range
- 214–345m³ CH₄/t VS
- Records
- 2studies
- Publications
- 2sources
- Temperatures
- 37 °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 1.3 % 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 (95 m³ CH₄/t); process risk: acidification. No additional handling requirements.
Why? Rating factors
Potential per tonne +2
- +2potential 95 m³ CH₄/t fresh matter (BMP 280 × DM 35.5 % × VS 95.4 %)
Process stability −0.5
- −0.5acidification: rapid degradation / acidic pH, risk of VFA accumulation, needs buffering
Handling and costs 0
- 0no factors
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 (280); 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 |
|---|---|---|---|---|
| Yan et al. (2021) DOI | 214 | — | Chinese yam (Dioscorea polystachya) – Whole | end point (model curve) |
| Ge et al. (2014) DOI | 345 | 37 °C · mesophilic | sweet Potato | end point (model curve) |
| Weighted mean | 280 | arithmetic mean 280, SD 93 | ||
Typical composition
- Dry matter (DM)
- 35.5% (range 35.5–35.5)
- Volatile solids (VS)
- 95.4 % DM (range 93.1–97.6)
- Nitrogen
- 1.3 % DM
- C/N ratio
- 34.9
Median and range of the determinations reported in the publications behind this substrate's BMP records (read from: BCBPD, MY-D); dry matter: 1 determination, volatile solids: 2 determinations. C/N was calculated as the ratio of C and N content (% DM) from the same source. DM from a single determination – indicative value.
Sources: Yan et al. (2021); Ge et al. (2014).
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.
- easily degradable
- sugars, starch, glycerol → fast hydrolysis and acidification (VFA), needs buffering
- carbon-rich
- high C/N → nitrogen deficiency; combine well with nitrogen-rich substrates
- low in nitrogen
- high C/N → nitrogen deficiency; combine well with nitrogen-rich substrates
- poor in trace elements
- poor in trace elements — mono-digestion requires supplementation
- seasonal
- seasonal availability — requires storage
Co-digestion — what to combine it with, what to watch out for
- combines well
substrates: nitrogen-rich — e.g. Pig slurry, Poultry manure, Waste activated sludge (secondary sludge), Chlorella vulgaris, Nannochloropsis salina
A nitrogen-rich co-substrate balances the low C/N of fruit and vegetable waste (Bouallagui et al. 2009).[1]
- combines well
substrates: high alkalinity (buffer) — e.g. Cattle manure, Pig slurry, Cattle slurry, Duck slurry, Rumen and digestive tract content
Co-digestion of easily degradable substrates with dairy slurry increased the methane yield relative to slurry alone.[2]
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).
Sources of the process data
- Improvement of fruit and vegetable waste anaerobic digestion performance and stability with co-substrates addition
- Biochemical methane potential and biodegradability of complex organic substrates
- Compositional components and methane production potential of typical vegetable wastes
- Biogas energy production from tropical biomass wastes by anaerobic digestion
- Lab-scale anaerobic digestion of cassava peels: the first step of energy recovery from cassava waste and water hyacinth
- Effects of size and thermophilic pre-hydrolysis of banana peel during anaerobic digestion, and biomethanation potential of key tropical fruit wastes
- Effect of particle size on biogas generation from biomass residues
The co-digestion calculator will assess a specific mixture containing this substrate.
What it is and where it comes from
Sweet potatoes (Ipomoea batatas) and Chinese yam (Dioscorea polystachya) are plants grown for their tubers, eaten as vegetables or processed. In a biogas plant they may appear as waste from processing or sorting, or as a product that does not meet commercial standards. In Poland these are niche crops and imported goods, so this is rather an occasional stream.
Properties relevant to digestion
Tubers contain mainly starch and sugars and little lignin and fibre, so they hydrolyse readily. A high rate of degradation means a risk of sudden fatty acid production, so dosing should be gradual. Raw tubers have a compact structure, but the soft tissues size-reduce well. The protein content is moderate, which reduces the risk of excess ammonia.
How to read the spread of results
The entry describes two different species from several studies, so the differences do not result from measurement error. The results are affected by the variety (starch content), the degree of ripeness, the share of peel, size reduction, the test conditions and the method of conversion to volatile solids. In one record the temperature is not stated in the compilation, which makes it harder to assess comparability.
In biogas plant practice
Tropical tubers rarely form a regular stream. If waste does appear, it is used as an energy additive to the mix, in the same way as potatoes. Size reduction, pH control and a gradual increase in dose must be remembered. Spoiled tubers may be contaminated with soil, which increases the amount of sediment in the tank.
From a planning perspective, it is worth remembering that tubers have a high feed and food value, so using them as an energy substrate generally concerns only waste or batches that do not meet quality standards. A small number of records is too few to determine a typical value for the whole group, so in practice a BMP test on the specific batch and monitoring of the rate of digester acidification are needed.
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 = 0.245 d−1 was assumed (median of rate constants k reported in the sources and/or fitted to the mean measured curves).
The statistics describe the spread of published results — a descriptive compilation, not a meta-analysis or a guarantee of plant yield.
Bibliography
- Yan, H.; Cai, F.; Wang, L.; Chen, C.; Liu, G. (2021). Compositional components and methane production potential of typical vegetable wastes. Environmental Science and Pollution Research 28(38), 54177–54186. DOI: 10.1007/s11356-021-15798-y DOI
- Ge, X.; Matsumoto, T.; Keith, L.; Li, Y. (2014). Biogas energy production from tropical biomass wastes by anaerobic digestion. Bioresource Technology 169, 38–44. DOI: 10.1016/j.biortech.2014.06.067 DOI
All sources of the site: bibliography.





