Urbanwastes

Urban wastes are unprocessed, discarded solid and liquid materials from daily life in cities and towns, mainly comprising household garbage, commercial refuse, and public space trash.

DATASETS

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 Biomass NameDry matter (DM) content, %Total nitrogen (N), kg per tonNH4-N, kg per tonTotal phosphorus (calculated as pure P) , kg per tonPotassium (calculated as pure K) , kg per tonOrganic matter, % of DMMagnesium (Mg), kg per tonCalcium (Ca), kg per tonSodium (Na), kg per tonCupper (Cu), gram per tonZinc (Zn), gram per tonVS % DM (Volitile Solids)m3 CH4 Pr Ton VSCO2e reduc. ton pr ton VSPrice pr. ton (€)Reference 
Source sorted biowaste15,012,6010,650,38 59,0     59,00   14
Human urine1,15,905,100,261,7061,8     61,82   13
Kitchen waste sterilized, digested95,042,67 1,518,4889,5     89,53   12
Kitchen waste decayed, sterilized95,036,11 1,518,4892,4     92,37   11
Kitchen waste decayed, sterilised, 1 × dose EM-incubated95,032,18 1,518,4889,3     89,30   10
Kitchen waste decayed, 2 × dose EM-incubated95,030,04 1,518,4889,3     89,30   9
Kitchen waste 1 × dose EM-incubated95,033,83 1,518,4891,4     91,42   8
Kitchen Waste Digested16,542,82 1,518,4895,0     95,00   7
Kitchen Waste EM incubated, dried, pelleted95,034,18 1,518,4893,7     93,72   6
Screw pressed organic household waste25,0          88,00400,000,69 5
Drum sieved organic household waste28,0          88,00400,000,69 4
Pulper (cellwood, Sweden)7,0          88,00400,000,69 3
Heat + enzymes (Renescience)25,0          88,00400,000,69 2
Pretreatment unknown30,0          85,00400,000,69 1
Average:  51,2630,047,881,257,6384,60     85,60400,000,69 7,50 

REFERENCES AND COMMENTS

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

  • 14: 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.
  • 13: 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.
  • 12: 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
  • 11: 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
  • 10: 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
  • 9: 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
  • 8: 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
  • 7: 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
  • 6: 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
  • 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).
  • 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).
  • 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).
  • 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).
  • 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).