Shanghai Key Laboratory of Atmospheric Particle Pollution and Prevention (LAP(3)), Department of Environmental Science and Engineering, Fudan University, Shanghai, 200433, China.
School of Energy and Power Engineering, Jiangsu University of Science and Technology, Zhenjiang, Jiangsu, 212003, China.
Environ Pollut. 2016 Apr;211:20-7. doi: 10.1016/j.envpol.2015.12.032. Epub 2015 Dec 29.
Antibiotic mycelial fermentation residues (AMFRs), which are emerging solid pollutants, have been recognized as hazardous waste in China since 2008. Nitrogen (N), which is an environmental sensitivity element, is largely retained in AMFR samples derived from fermentation substrates. Pyrolysis is a promising technology for the treatment of solid waste. However, the outcomes of N element during the pyrolysis of AMFRs are still unknown. In this study, the conversion of N element during the pyrolysis of AMFRs was tracked using XPS (X-ray photoelectron spectroscopy) and online TG-FTIR-MS (Thermogravimetry-Fourier transform infrared-Mass spectrometry) technology. In the AMFR sample, organic amine-N, pyrrolic-N, protein-N, pyridinic-N, was the main N-containing species. XPS results indicated that pyrrolic-N and pyridinic-N were retained in the AMFR-derived pyrolysis char. More stable species, such as N-oxide and quaternary-N, were also produced in the char. TG-FTIR-MS results indicated that NH3 and HCN were the main gaseous species, and their contents were closely related to the contents of amine-N and protein-N, and pyrrolic-N and pyridinic-N of AMFRs, respectively. Increases in heating rate enhanced the amounts of NH3 and HCN, but had less of an effect on the degradation degree of AMFRs. N-containing organic compounds, including amine-N, nitrile-N and heterocyclic-N, were discerned from the AMFR pyrolysis process. Their release range was extended with increasing of heating rate and carbon content of AMFR sample. This work will help to take appropriate measure to reduce secondary pollution from the treatment of AMFRs.
抗生素菌丝发酵残留物 (AMFRs) 是一种新兴的固体污染物,自 2008 年以来已被中国认定为危险废物。氮 (N) 是一种环境敏感元素,在发酵基质衍生的 AMFR 样品中大量保留。热解是一种有前途的处理固体废物的技术。然而,AMFR 热解过程中 N 元素的去向仍不清楚。在这项研究中,使用 XPS(X 射线光电子能谱)和在线 TG-FTIR-MS(热重-傅里叶变换红外-质谱联用)技术跟踪了 AMFR 热解过程中 N 元素的转化。在 AMFR 样品中,有机胺-N、吡咯-N、蛋白质-N、吡啶-N 是主要的含 N 物种。XPS 结果表明,吡咯-N 和吡啶-N 残留在 AMFR 衍生的热解焦中。在焦中还产生了更稳定的物质,如 N-氧化物和季铵-N。TG-FTIR-MS 结果表明,NH3 和 HCN 是主要的气态物种,它们的含量与 AMFR 中的胺-N 和蛋白质-N 以及吡咯-N 和吡啶-N 的含量密切相关。升高加热速率会增加 NH3 和 HCN 的含量,但对 AMFR 降解程度的影响较小。在 AMFR 热解过程中,还检测到含 N 的有机化合物,包括胺-N、腈-N 和杂环-N。随着加热速率和 AMFR 样品中碳含量的增加,它们的释放范围扩大。这项工作将有助于采取适当的措施来减少 AMFR 处理过程中的二次污染。