BioEngine Research Team on Green Process Engineering and Biorefineries, Department of Chemical Engineering, Université Laval, 1065 Avenue de La Médecine, Québec, QC, G1V 0A6, Canada; CentrEau Water Research Center, 1065 Avenue de La Médecine, Québec, QC, G1V 0A6, Canada.
BioEngine Research Team on Green Process Engineering and Biorefineries, Department of Chemical Engineering, Université Laval, 1065 Avenue de La Médecine, Québec, QC, G1V 0A6, Canada; CentrEau Water Research Center, 1065 Avenue de La Médecine, Québec, QC, G1V 0A6, Canada.
J Environ Manage. 2024 Feb 14;352:119964. doi: 10.1016/j.jenvman.2023.119964. Epub 2024 Jan 15.
The application of sewage sludge to agricultural land is facing increasing restrictions due to concerns about various micropollutants, including polycyclic aromatic hydrocarbons (PAHs), dioxins and furans (PCDD/Fs), polychlorinated biphenyls (PCBs), per- and poly-fluoroalkyl substances (PFAS), and heavy metals (HMs). As an alternative approach to manage this residue, the use of pyrolysis, a process that transforms sludge into biochar, a carbon-rich solid material, is being explored. Despite the potential benefits of pyrolysis, there is limited data on its effectiveness in removing micropollutants and the potential presence of harmful elements in the resulting biochar. This study aims to evaluate the impact of the temperature and the use of a carrier gas (N) during a two-stage pyrolysis and cooling on micropollutant removal. Pilot-scale tests showed that a higher temperature (650 °C) and the use of a carrier gas (0.4 L/min N) during the pyrolysis and the cooling process led to a reduction of PAHs, PCDD/Fs, PCBs and PFAS below their detection limits. As such, the generated biochar aligns with the guidelines set by the International Biochar Initiative (IBI) and the European Biochar Certificate (EBC) for all micropollutants, except for zinc and copper. Additional investigation is required to determine whether the micropollutants undergo destruction or transition into other pyrolysis end-products, such as the gas or liquid phase.
由于担心各种微量污染物,包括多环芳烃(PAHs)、二恶英和呋喃(PCDD/Fs)、多氯联苯(PCBs)、全氟和多氟烷基物质(PFAS)和重金属(HMs),将污水污泥施用于农业用地的应用正面临越来越多的限制。作为管理这种残留物的替代方法,正在探索使用热解的方法,即将污泥转化为生物炭,一种富含碳的固体材料。尽管热解有潜在的好处,但关于其去除微量污染物的有效性以及在产生的生物炭中存在有害元素的有限数据。本研究旨在评估在两段式热解和冷却过程中温度和使用载气(N)的影响对去除微量污染物的影响。中试表明,在热解和冷却过程中使用较高的温度(650°C)和载气(0.4 L/min N)导致 PAHs、PCDD/Fs、PCBs 和 PFAS 减少到检测限以下。因此,所产生的生物炭符合国际生物炭倡议(IBI)和欧洲生物炭证书(EBC)为所有微量污染物设定的指南,除锌和铜外。需要进一步调查以确定微量污染物是否经历了破坏或转化为其他热解终产物,例如气体或液相。