Industrial wastes are unprocessed wastes and byproducts from the food or feed processing industry,
as well as from rendering plants.
Group of industrial wastes (select):
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Animal food processing wastes are unprocessed, unwanted or leftover materials from slaughterhouses, meat packing, dairy, and fish industries, including blood, bones, tissue, and high-strength wastewater.
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You will after login have possibility to enter your own datasets, and to edit and
delete them. Datasets shown on a purple background are not yet validated. Click the
column header text for sorting ascending or descending.
The shown values are to be considered as examples, alone, that illustrates the chemical
composition for relevant parametres, and as well the variation in the composition. The
references must be consulted in each case in order to clarify for instance the analysis
method.
Where no other references are made, the source for the CO2 reduction coefficient (CO2e reduc. ton pr ton VS) is: Sven G. Sommer, Henrik B. Møller og Søren O. Pedersen. 2001. Reduktion af drivhusgasemission fra gylle og organisk affald ved biogasbehandling (In English: Reduction of green house gas emission from slurry and organic wastes by biogas treatment). Report No. 31 - Animal Production, from DJF (In English: Danish Institute of Agricultural Sciences). 53 pp., Appendix 3, Biogas scenario 2, without subsstitution efftect.
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58:
Michaud, A., et al. “EOM4SOIL - Physico-chemical Characteristics of External Organic Matters (EOMs) Database”. Version 1, Zenodo, 22 Oct. 2024, https://doi.org/10.5281/zenodo.13969793. /
Please check the reference; the figures may be averages of several analyses and there may be more details than presented here.
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39:
Kuligowski, Ksawery, Adam Cenian, Izabela Konkol, Lesław Świerczek, Katarzyna Chojnacka, Grzegorz Izydorczyk, Dawid Skrzypczak, and Paulina Bandrów. 2023. "Application of Leather Waste Fractions and Their Biochars as Organic Fertilisers for Ryegrass Growth: Agri-Environmental Aspects and Plants Response Modelling" Energies 16, no. 9: 3883. https://doi.org/10.3390/en16093883 /
Material provided by BADER Polska LtD.
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38:
Kuligowski, Ksawery, Adam Cenian, Izabela Konkol, Lesław Świerczek, Katarzyna Chojnacka, Grzegorz Izydorczyk, Dawid Skrzypczak, and Paulina Bandrów. 2023. "Application of Leather Waste Fractions and Their Biochars as Organic Fertilisers for Ryegrass Growth: Agri-Environmental Aspects and Plants Response Modelling" Energies 16, no. 9: 3883. https://doi.org/10.3390/en16093883 /
Material provided by BADER Polska LtD.
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37:
Kuligowski, Ksawery, Adam Cenian, Izabela Konkol, Lesław Świerczek, Katarzyna Chojnacka, Grzegorz Izydorczyk, Dawid Skrzypczak, and Paulina Bandrów. 2023. "Application of Leather Waste Fractions and Their Biochars as Organic Fertilisers for Ryegrass Growth: Agri-Environmental Aspects and Plants Response Modelling" Energies 16, no. 9: 3883. https://doi.org/10.3390/en16093883andKonkol, I.; Swierczek, L.; Wrzesinska-Jedrusiak, E.; Czarnecki, M.; Kuligowski, K.; Cenian, A. Enhancing Biogas Yield from Tanned Shavings: A Preliminary Study on Pretreatment Strategies. Sustainability 2025, 17, 11121. https://doi.org/10.3390/su172411121 /
Material provided by BADER Polska LtD.
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36:
Kuligowski, Ksawery, Adam Cenian, Izabela Konkol, Lesław Świerczek, Katarzyna Chojnacka, Grzegorz Izydorczyk, Dawid Skrzypczak, and Paulina Bandrów. 2023. "Application of Leather Waste Fractions and Their Biochars as Organic Fertilisers for Ryegrass Growth: Agri-Environmental Aspects and Plants Response Modelling" Energies 16, no. 9: 3883. https://doi.org/10.3390/en16093883andKonkol, I.; Swierczek, L.; Wrzesinska-Jedrusiak, E.; Czarnecki, M.; Kuligowski, K.; Cenian, A. Enhancing Biogas Yield from Tanned Shavings: A Preliminary Study on Pretreatment Strategies. Sustainability 2025, 17, 11121. https://doi.org/10.3390/su172411121 /
Material provided by BADER Polska LtD.
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33:
Michaud, A., Van Der Smissen, H., Tampio, E., Laakso, J., Levavasseur, F., Barcauskaite, K., Lasorella, V., Criscuoli, I., Asperen, P., Dehaan, J., Jimenez, J., Caradec, L., & Houot, S. (2024). EOM4SOIL - Physico-chemical characteristics of external organic matters (EOMs) database (Version 1) [Data set]. Zenodo. https://doi.org/10.5281/zenodo.13969793 /
The values are averages of 3 analysed samples
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14:
The data source is "Fact sheet for biogas" developed by NIRAS for Energinet.dk in 2012. Aarhus University has validated the data and also provided information about volatile solids and gas potential of the biomasses. The original data can be downloaded from http://implement.nu/wp-content/uploads/2013/06/Biogasdatagrundlaget_regneark.pdf. /
The biogas potential is based on either a mesophilic process (38°C) with 25 days retention time, or thermophilic process (53°C) with 17 days retention time and 10 days in storage tank (10% biogas collected in covered after storage tank).
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The data source is "Fact sheet for biogas" developed by NIRAS for Energinet.dk in 2012. Aarhus University has validated the data and also provided information about volatile solids and gas potential of the biomasses. The original data can be downloaded from http://implement.nu/wp-content/uploads/2013/06/Biogasdatagrundlaget_regneark.pdf. /
The biogas potential is based on either a mesophilic process (38°C) with 25 days retention time, or thermophilic process (53°C) with 17 days retention time and 10 days in storage tank (10% biogas collected in covered after storage tank).
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5:
The data source is "Fact sheet for biogas" developed by NIRAS for Energinet.dk in 2012. Aarhus University has validated the data and also provided information about volatile solids and gas potential of the biomasses. The original data can be downloaded from http://implement.nu/wp-content/uploads/2013/06/Biogasdatagrundlaget_regneark.pdf. /
The biogas potential is based on either a mesophilic process (38°C) with 25 days retention time, or thermophilic process (53°C) with 17 days retention time and 10 days in storage tank (10% biogas collected in covered after storage tank).
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4:
The data source is "Fact sheet for biogas" developed by NIRAS for Energinet.dk in 2012. Aarhus University has validated the data and also provided information about volatile solids and gas potential of the biomasses. The original data can be downloaded from http://implement.nu/wp-content/uploads/2013/06/Biogasdatagrundlaget_regneark.pdf. /
The biogas potential is based on either a mesophilic process (38°C) with 25 days retention time, or thermophilic process (53°C) with 17 days retention time and 10 days in storage tank (10% biogas collected in covered after storage tank).
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2:
The data source is "Fact sheet for biogas" developed by NIRAS for Energinet.dk in 2012. Aarhus University has validated the data and also provided information about volatile solids and gas potential of the biomasses. The original data can be downloaded from http://implement.nu/wp-content/uploads/2013/06/Biogasdatagrundlaget_regneark.pdf. /
The biogas potential is based on either a mesophilic process (38°C) with 25 days retention time, or thermophilic process (53°C) with 17 days retention time and 10 days in storage tank (10% biogas collected in covered after storage tank).
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1:
The data source is "Fact sheet for biogas" developed by NIRAS for Energinet.dk in 2012. Aarhus University has validated the data and also provided information about volatile solids and gas potential of the biomasses. The original data can be downloaded from http://implement.nu/wp-content/uploads/2013/06/Biogasdatagrundlaget_regneark.pdf. /
The biogas potential is based on either a mesophilic process (38°C) with 25 days retention time, or thermophilic process (53°C) with 17 days retention time and 10 days in storage tank (10% biogas collected in covered after storage tank).
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