BMP testingBy-products of the agri-food industry

Soapstock — BMP: 3 studies, weighted mean 516 m³ CH₄/t VS

Soapstock is a sediment from the alkaline refining of oils, containing soaps, free fatty acids and phospholipids; very rich in lipids, but difficult to dose.

CH₄ ≈ 63 % (estimate)

Published Updated 3 min readFeedstockData Editorial Team

Illustration: FeedstockData (AI, Google Gemini)

Weighted mean
516m³ CH₄/t VS
Range
283–705m³ CH₄/t VS
Records
3studies
Publications
2sources
Temperatures
35 °Cof the test

Methane in biogas

High methane content · ≈ 6.3 kWh/m³ of biogas

estimate from the substrate type The collected studies contain no measurement. The interval follows from the approximate composition (carbohydrate-dominated (no protein or fat characteristics); fat-rich (process classification)) and the yields of compound groups according to FNR.

How we calculate it and what the zones mean

Rating for biogas plants

not rated — editorial rating for biogas plants

Not rated: no dry matter or volatile solids in the data. We calculate the rating when the dry matter and volatile solids of the material are known.

Editorial rating per the methodology

Add to the co-digestion calculator CSV data

BMP curves from 3 studies

Weighted mean Individual records

BMP curves: SoapstockCumulative methane production over time for 3 records and the weighted mean of 516 m³ CH₄/t VS. 3 of the curves are model curves (first-order kinetics).02004006008000510152025303540time [d]m³ CH₄/t VSBorowski i Cieciura-Włoch (2021): 538 m³ CH₄/t VS (model curve)Kouas et al. (2017) · 1: 283 m³ CH₄/t VS (model curve)Kouas et al. (2017) · 2: 705 m³ CH₄/t VS (model curve)mean516

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 (516); 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
SourceBMP
m³ CH₄/t VS
TemperatureSampleCurve
Borowski i Cieciura-Włoch (2021) DOI538—Interphase from soapstock splitting, no enzymeend point (model curve)
Kouas et al. (2017) · 1 DOI28335 °C · mesophilicoilend point (model curve)
Kouas et al. (2017) · 2 DOI70535 °C · mesophilicoilend point (model curve)
Weighted mean516arithmetic mean 509, SD 212

Process properties

  • fat-rich
  • saline
  • tendency to foam
  • forms a floating layer
  • low in nitrogen
  • editorial classification

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 516.0 m³ CH₄/t VS (SD 212.5; 3 records, 2 sources).
  • Very high lipid concentration in DM (Long et al. 2012).

Drawbacks and risks

  • Sodium/calcium soaps and LCFA inhibit methanogenesis; sodium raises salinity (Chen et al. 2008; Long et al. 2012).
  • Foams on contact with water.
  • Dense - difficult to pump.

Co-digestion — what to combine it with, what to watch out for

Dosing

No source-based threshold; the most cautious dosing among lipids.

Introduce gradually, starting with a small dose and monitoring the process (e.g. FOS/TAC, pH, gas composition).

The co-digestion calculator will assess a specific mixture containing this substrate.

What it is and where it comes from

Soapstock, i.e. soap sediment, arises during the chemical refining of vegetable oils, when free fatty acids are neutralised with lye. The mixture of soaps, phospholipids, neutral oils and water is separated as a distinct fraction. It is often processed further: split with acid into fatty acids, which are sold as a technical raw material. In Poland the processing of rapeseed oil is significant, so soapstock arises in refineries, but it is usually utilised in industry.

Properties relevant to digestion

Soapstock contains in its dry matter a very high share of lipids in the form of soaps, fatty acids and glycerides, and of phospholipids. This gives the largest methane potential among typical wastes, but at the same time the greatest risk of inhibition: the accumulation of long-chain fatty acids and of calcium and sodium salts can inhibit methanogenesis. A high sodium content from neutralisation can increase the salinity of the digester. The material is dense and difficult to pump, and foams on contact with water. The low nitrogen content requires balancing with other feedstocks.

How to read the spread of results

The dataset contains several records from several sources: soapstock from rapeseed and sunflower oil and an intermediate phase from the splitting of soapstock. The differences arise from the type of oil, the refining process, the pH and water in the waste and the degree of splitting. In addition, the way the sample is introduced into the test (suspension, emulsion) and the adaptation of the inoculum to lipids are of great importance, because without it the result in a short test is underestimated.

In biogas plant practice

Soapstock is used only in a small, stable share and introduced gradually, preferably together with slurry. It requires heating for pumping, control of volatile acids and observation of foam. Its use is sometimes limited by competition from the chemical and fuel industries. As an industrial waste it is subject to waste regulations, and if it contains raw materials of animal origin, also to additional requirements.

Because of the high risk to the process, soapstock is rather a material for specialised disposal plants than for a typical agricultural biogas plant. The share should be established in stages, observing the volatile acids and the methane content of the biogas over at least several retention-time cycles.

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.

Full methodology and correction policy

Bibliography

  1. Borowski, S.; Cieciura-Włoch, W. (2021). Enzymatic Pretreatment of Byproducts from Soapstock Splitting and Glycerol Processing for Improvement of Biogas Production. Molecules 26(22), 6782. DOI: 10.3390/molecules26226782 DOI
  2. Kouas, M.; Torrijos, M.; Sousbie, P.; Steyer, J.P.; Sayadi, S.; Harmand, J. (2017). Robust assessment of both biochemical methane potential and degradation kinetics of solid residues in successive batches. Waste Management 70, 59–70. DOI: 10.1016/j.wasman.2017.09.001 DOI

All sources of the site: bibliography.