WFRF:(Zhang Wennan)
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| Fältnamn | Indikatorer | Metadata |
|---|---|---|
| 000 | 03942naa a2200493 4500 | |
| 001 | oai:gup.ub.gu.se/313648 | |
| 003 | SwePub | |
| 008 | 240910s2022 | |||||||||||000 ||eng| | |
| 009 | oai:DiVA.org:miun-44250 | |
| 024 | 7 | a https://gup.ub.gu.se/publication/3136482 URI |
| 024 | 7 | a https://doi.org/10.3390/ijerph190315812 DOI |
| 024 | 7 | a https://urn.kb.se/resolve?urn=urn:nbn:se:miun:diva-442502 URI |
| 040 | a (SwePub)gud (SwePub)miun | |
| 041 | a eng | |
| 042 | 9 SwePub | |
| 072 | 7 | a ref2 swepub-contenttype |
| 072 | 7 | a art2 swepub-publicationtype |
| 100 | 1 | a Ge, Yaxin,d 1992u Gothenburg University,Göteborgs universitet,Institutionen för kemi och molekylärbiologi,Department of Chemistry and Molecular Biology4 aut0 (Swepub:gu)xgeyar |
| 245 | 1 0 | a Emission Characteristics of NOx and SO2 during the Combustion of Antibiotic Mycelial Residue |
| 264 | c 2022-01-29 | |
| 264 | 1 | b MDPI AG,c 2022 |
| 520 | a The antibiotic mycelial residue (AMR) generated from cephalosporin C production is a haz-ardous organic waste, which is usually disposed of by landfilling that causes potential secondary environmental pollution. AMR combustion can be an effective method to treat AMR. In order to develop clean combustion technologies for safe disposal and energy recovery from various AMRs, the emission characteristics of NOx and SO2 from AMR combustion were studied experimentally in this work. It was found that the fuel-N is constituted by 85% protein nitrogen and 15% inorganic nitrogen, and the fuel-S by 78% inorganic sulfur and 22% organic sulfur. Nitrogen oxide emissions mainly occur at the volatile combustion stage when the temperature rises to 400◦C, while the primary sulfur oxide emission appears at the char combustion stage above 400◦C. Increasing the combustion temperature and airflow cause higher NOx emissions. High moisture content in AMR can significantly reduce the NOx emission by lowering the combustion temperature and generating more reducing gases such as CO. For the SO2 emission, the combustion temperature (700 to 900◦C), airflow and AMR water content do not seem to exhibit obvious effects. The presence of CaO significantly inhibits SO2 emission, especially for the SO2 produced during the AMR char combustion because of the good control effect on the direct emission of inorganic SO2. Employing air/fuel staging technologies in combination with in-situ desulfurization by calcium oxide/salts added in the combustor with operation temperatures lower than 900◦C should be a potential technology for the clean disposal of AMRs. © 2022 by the authors. Licensee MDPI, Basel, Switzerland. | |
| 650 | 7 | a MEDICIN OCH HÄLSOVETENSKAPx Hälsovetenskap0 (SwePub)3032 hsv//swe |
| 650 | 7 | a MEDICAL AND HEALTH SCIENCESx Health Sciences0 (SwePub)3032 hsv//eng |
| 650 | 7 | a TEKNIK OCH TEKNOLOGIERx Maskinteknikx Energiteknik0 (SwePub)203042 hsv//swe |
| 650 | 7 | a ENGINEERING AND TECHNOLOGYx Mechanical Engineeringx Energy Engineering0 (SwePub)203042 hsv//eng |
| 653 | a Antibiotic mycelial residue (AMR) | |
| 653 | a CaO | |
| 653 | a Combustion | |
| 653 | a Desulfurization | |
| 653 | a NOx | |
| 653 | a SO2 | |
| 653 | a Antibiotic mycelial residue (AMR) | |
| 700 | 1 | a Zhang, G.4 aut |
| 700 | 1 | a Zhang, J.4 aut |
| 700 | 1 | a Zhang, Wennanu Mittuniversitetet,Institutionen för kemiteknik4 aut0 (Swepub:miun)wenzha |
| 700 | 1 | a Cui, L.4 aut |
| 710 | 2 | a Göteborgs universitetb Institutionen för kemi och molekylärbiologi4 org |
| 773 | 0 | t International Journal of Environmental Research and Public Healthd : MDPI AGg 19:3q 19:3x 1661-7827x 1660-4601 |
| 856 | 4 | u https://www.mdpi.com/1660-4601/19/3/1581/pdf |
| 856 | 4 | u https://doi.org/10.3390/ijerph19031581y Fulltext |
| 856 | 4 8 | u https://gup.ub.gu.se/publication/313648 |
| 856 | 4 8 | u https://doi.org/10.3390/ijerph19031581 |
| 856 | 4 8 | u https://urn.kb.se/resolve?urn=urn:nbn:se:miun:diva-44250 |
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