BMP testingWild, invasive and medicinal plantssingle study (2 samples)

Lavender flowers and distillation residues — BMP: 2 studies, weighted mean 186 m³ CH₄/t VS

Lavender flowers and residues after oil distillation are a herb waste of low lignin; essential oils in fresh flowers can inhibit digestion.

CH₄ ≈ 52 % (estimate)

Published Updated 3 min readFeedstockData Editorial Team

Photo John Samuel / Wikimedia Commons, licence CC BY-SA 4.0, source file; changes: cropping

Weighted mean
186m³ CH₄/t VS
Range
171–200m³ CH₄/t VS
Records
2single study (2 samples)
Publications
1source
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 0.9 % DM × 6.25)) 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: the dry matter in the data refers to a sample dried for the test, not to the material as delivered. 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 2 studies

Weighted mean Individual records

BMP curves: Lavender flowers and distillation residuesCumulative methane production over time for 2 records and the weighted mean of 186 m³ CH₄/t VS. 2 of the curves are model curves (first-order kinetics).050100150200250051015202530time [d]m³ CH₄/t VSLallement et al. (2023) · 1: 171 m³ CH₄/t VS (model curve)Lallement et al. (2023) · 2: 200 m³ CH₄/t VS (model curve)mean186

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 (186); 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
Lallement et al. (2023) · 1 DOI17138 °C · mesophilicflower residue lavenderend point (model curve)
Lallement et al. (2023) · 2 DOI20038 °C · mesophilicflower lavenderend point (model curve)
Weighted mean186arithmetic mean 186, SD 21

Typical composition

Dry matter (DM)
85.8% (range 82.8–88.7)
Volatile solids (VS)
93 % DM (range 92–94)
Nitrogen
0.9 % DM
C/N ratio
57.4

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: 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

  • fibrous
  • seasonal
  • variable composition
  • 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 database: weighted mean 186 m³ CH₄/t VS (median 186; range 171-200; 2 records from 1 source).
  • Described in a modern database of the composition and methane potential of biomasses (Lallement 2023).

Drawbacks and risks

  • Spread of results in the database: standard deviation 21 at a mean of 186 m³ CH₄/t VS (2 records from 1 source).

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

Dosing

No dose data; add gradually as a lignocellulosic supplement.

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”).

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

What it is and where it comes from

Lavender (Lavandula angustifolia) is grown for its flowers and essential oil. In Poland the plantations are small, and waste arises after harvest and steam distillation. The residue after distillation, i.e. the spent biomass, is usually composted or burned. The dataset describes both lavender flowers and residues after distillation.

Properties relevant to digestion

Lavender biomass is fibrous in character: it contains cellulose, hemicellulose and lignin, and also protein and small amounts of sugars. Fresh flowers contain an essential oil with linalool and linalyl acetate, which have antimicrobial activity and can lower the activity of methanogens at high concentrations. After distillation most of the oil is removed, which reduces the risk of inhibition. The material is dry or semi-dry, tolerates storage well and is easy to size-reduce.

How to read the spread of results

The dataset contains several records from a single study, under mesophilic conditions at 38 °C: flower residues and lavender flowers. The results are similar. Differences between fresh flowers and residue after distillation depend on the degree of oil removal, the lavender variety, the harvest date, size reduction and the inoculum. A single study does not allow variability between laboratories to be assessed or the result to be applied to other varieties.

In biogas plant practice

Lavender is of marginal significance and can supplement the feed on herb farms that process their own biomass. The residue after distillation is safer for the process than fresh flowers. It should be size-reduced and introduced in a small share with slurry. Waste from herb processing from outside the farm is waste, and residues from the farm's own cultivation are treated as agricultural products.

For producers of lavender oil, digestion of the residue after distillation can be a way of managing the waste without composting. Before implementation, however, the dry matter and residual oil content in the specific batch should be confirmed, because distillation efficiency differs between plants.

If only fresh lavender biomass is available, it is safer to wilt it or ensile it with other green forage, because part of the oil then volatilises and the threat to the microflora decreases.

The value of these results is limited to the range of varieties and the distillation technology used in the study. In the practice of lavender plantations the waste is dispersed and seasonal, so composting on site is usually more cost-effective than transport to a biogas plant.

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 = 0.134 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.

Full methodology and correction policy

Bibliography

  1. 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.