AgroTechnologyATLAS - Organic household waste

Organic household waste

Organic household waste includes source-separated organic fractions from households suitable for biological treatment.

DATASETS

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	Biomass Name	Dry matter (DM) content, %	Total nitrogen (N), kg per ton	Total phosphorus (calculated as pure P) , kg per ton	Potassium (calculated as pure K) , kg per ton	Organic matter, % of DM	VS % DM (Volitile Solids)	m3 CH4 Pr Ton VS	CO2e reduc. ton pr ton VS	Reference
	Pretreatment unknown	30,0					85,00	400,00	0,69	1
	Heat + enzymes (Renescience)	25,0					88,00	400,00	0,69	2
	Pulper (cellwood, Sweden)	7,0					88,00	400,00	0,69	3
	Drum sieve	28,0					88,00	400,00	0,69	4
	Screw press	25,0					88,00	400,00	0,69	5
	Kitchen Waste EM incubated, dried, pelleted	95,0	34,18	1,51	8,48	93,7	93,72			30
	Kitchen Waste Digested	16,5	42,82	1,51	8,48	95,0	95,00			31
	Kitchen waste 1 × dose EM-incubated	95,0	33,83	1,51	8,48	91,4	91,42			32
	Kitchen waste decayed, 2 × dose EM-incubated	95,0	30,04	1,51	8,48	89,3	89,30			33
	Kitchen waste decayed, sterilised, 1 × dose EM-incubated	95,0	32,18	1,51	8,48	89,3	89,30			34
	Kitchen waste decayed, sterilized	95,0	36,11	1,51	8,48	92,4	92,37			35
	Kitchen waste sterilized, digested	95,0	42,67	1,51	8,48	89,5	89,53			36
Average:		58,46	35,98	1,51	8,48	91,51	89,80	400,00	0,69	20,50

REFERENCES AND COMMENTS

References are incicated by: 'Reference number: Reference; Comment'

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).
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).
3: 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).
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).
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).
30: Kuligowski, K.; Konkol, I.; Swierczek, L.; Chojnacka, K.; Cenian, A.; Szufa, S. Evaluation of Kitchen Waste Recycling as Organic N-Fertiliser for Sustainable Agriculture under Cool and Warm Seasons. Sustainability 2023, 15, 7997. https://doi.org/10.3390/su15107997 Model kitchen waste based on mixing various grocery products - not obtained from the source seggregation
31: Kuligowski, K.; Konkol, I.; Swierczek, L.; Chojnacka, K.; Cenian, A.; Szufa, S. Evaluation of Kitchen Waste Recycling as Organic N-Fertiliser for Sustainable Agriculture under Cool and Warm Seasons. Sustainability 2023, 15, 7997. https://doi.org/10.3390/su15107997 Model kitchen waste based on mixing various grocery products - not obtained from the source seggregation
32: Kuligowski, K.; Konkol, I.; Swierczek, L.; Wozniak, A.; Cenian, A. Conversion of KitchenWaste into Sustainable Fertilizers: Comparative Effectiveness of Biological, Microbial, and Thermal Treatments in a Ryegrass Growth Trial. Appl. Sci. 2025, 15, 5281. https://doi.org/10.3390/app15105281
33: Kuligowski, K.; Konkol, I.; Swierczek, L.; Wozniak, A.; Cenian, A. Conversion of KitchenWaste into Sustainable Fertilizers: Comparative Effectiveness of Biological, Microbial, and Thermal Treatments in a Ryegrass Growth Trial. Appl. Sci. 2025, 15, 5281. https://doi.org/10.3390/app15105281
34: Kuligowski, K.; Konkol, I.; Swierczek, L.; Wozniak, A.; Cenian, A. Conversion of KitchenWaste into Sustainable Fertilizers: Comparative Effectiveness of Biological, Microbial, and Thermal Treatments in a Ryegrass Growth Trial. Appl. Sci. 2025, 15, 5281. https://doi.org/10.3390/app15105281
35: Kuligowski, K.; Konkol, I.; Swierczek, L.; Wozniak, A.; Cenian, A. Conversion of KitchenWaste into Sustainable Fertilizers: Comparative Effectiveness of Biological, Microbial, and Thermal Treatments in a Ryegrass Growth Trial. Appl. Sci. 2025, 15, 5281. https://doi.org/10.3390/app15105281
36: Kuligowski, K.; Konkol, I.; Swierczek, L.; Wozniak, A.; Cenian, A. Conversion of KitchenWaste into Sustainable Fertilizers: Comparative Effectiveness of Biological, Microbial, and Thermal Treatments in a Ryegrass Growth Trial. Appl. Sci. 2025, 15, 5281. https://doi.org/10.3390/app15105281

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).

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).

3: 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).

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).

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).

30: Kuligowski, K.; Konkol, I.; Swierczek, L.; Chojnacka, K.; Cenian, A.; Szufa, S. Evaluation of Kitchen Waste Recycling as Organic N-Fertiliser for Sustainable Agriculture under Cool and Warm Seasons. Sustainability 2023, 15, 7997. https://doi.org/10.3390/su15107997 Model kitchen waste based on mixing various grocery products - not obtained from the source seggregation

31: Kuligowski, K.; Konkol, I.; Swierczek, L.; Chojnacka, K.; Cenian, A.; Szufa, S. Evaluation of Kitchen Waste Recycling as Organic N-Fertiliser for Sustainable Agriculture under Cool and Warm Seasons. Sustainability 2023, 15, 7997. https://doi.org/10.3390/su15107997 Model kitchen waste based on mixing various grocery products - not obtained from the source seggregation

32: Kuligowski, K.; Konkol, I.; Swierczek, L.; Wozniak, A.; Cenian, A. Conversion of KitchenWaste into Sustainable Fertilizers: Comparative Effectiveness of Biological, Microbial, and Thermal Treatments in a Ryegrass Growth Trial. Appl. Sci. 2025, 15, 5281. https://doi.org/10.3390/app15105281

33: Kuligowski, K.; Konkol, I.; Swierczek, L.; Wozniak, A.; Cenian, A. Conversion of KitchenWaste into Sustainable Fertilizers: Comparative Effectiveness of Biological, Microbial, and Thermal Treatments in a Ryegrass Growth Trial. Appl. Sci. 2025, 15, 5281. https://doi.org/10.3390/app15105281

34: Kuligowski, K.; Konkol, I.; Swierczek, L.; Wozniak, A.; Cenian, A. Conversion of KitchenWaste into Sustainable Fertilizers: Comparative Effectiveness of Biological, Microbial, and Thermal Treatments in a Ryegrass Growth Trial. Appl. Sci. 2025, 15, 5281. https://doi.org/10.3390/app15105281

35: Kuligowski, K.; Konkol, I.; Swierczek, L.; Wozniak, A.; Cenian, A. Conversion of KitchenWaste into Sustainable Fertilizers: Comparative Effectiveness of Biological, Microbial, and Thermal Treatments in a Ryegrass Growth Trial. Appl. Sci. 2025, 15, 5281. https://doi.org/10.3390/app15105281

36: Kuligowski, K.; Konkol, I.; Swierczek, L.; Wozniak, A.; Cenian, A. Conversion of KitchenWaste into Sustainable Fertilizers: Comparative Effectiveness of Biological, Microbial, and Thermal Treatments in a Ryegrass Growth Trial. Appl. Sci. 2025, 15, 5281. https://doi.org/10.3390/app15105281