Effect of blast furnace slag on heavy metal speciation in municipal sludge pyrolysis: experimental and theoretical study

Shijie Zhang, Zhixin Geng, Yangwei Qu, Yangfan Fang, Yunfeng Xu
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Abstract

The presence of unstable heavy metals in sludge restricts its potential for resource utilization, making it crucial to minimize the secondary risk associated with heavy metals during sludge pyrolysis. This study explored the influence of the addition of blast furnace slag (slag), pyrolysis temperature, and residence time on the morphological distributions of Zn, Pb, and Cr in biochar co-pyrolyzed with slag. The slag dosage was consistent at 7.5% for all samples to immobilize different heavy metals. High-temperature pyrolysis (600–700 °C) promoted the immobilization of Cr and Pb, while lower pyrolysis temperatures (400 °C) favored the stabilization of Zn. The appropriate residence time was determined to be 15 min for Zn and Cr, and 60 min for Pb, across all samples. Brunauer–Emmett–Teller (BET) characterization revealed that all the samples exhibited a mesoporous structure dominated by a type IV isothermal profile. Additionally, the biochar demonstrated the largest specific surface area (69.48 m2/g) after pyrolysis at 500 °C. XRD (X-ray diffractometer) characterization indicated that the addition of slag facilitated the formation of crystals composed of Ca–Si-based substances bound to heavy metals. FTIR spectroscopy tests revealed that the addition of slag resulted in a reduction in the intensity of the O–H telescoping vibration peaks, which in turn promoted the formation of aromatic and epoxide structures and enhanced heavy metal stabilization. Density functional theory (DFT) calculations revealed that slag can form covalent bonds with Zn, reducing the volatilization risk of Zn species during pyrolysis. The experimental and simulation findings presented in this paper provide new insights into the management of heavy metals in the sludge pyrolysis process.

Graphical abstract

高炉炉渣对城市污泥热解过程中重金属形态影响的实验与理论研究
污泥中不稳定重金属的存在限制了其资源化利用的潜力,因此在污泥热解过程中尽量减少与重金属相关的二次风险至关重要。本研究探讨了添加高炉渣(渣)、热解温度、停留时间对与渣共热解的生物炭中Zn、Pb、Cr形态分布的影响。矿渣掺量一致,均为7.5%,以固定不同重金属。高温热解(600 ~ 700℃)有利于Cr和Pb的固定化,较低热解温度(400℃)有利于Zn的稳定化。在所有样品中,确定适当的停留时间为Zn和Cr为15 min, Pb为60 min。布鲁诺尔-埃米特-泰勒(BET)表征表明,所有样品都表现出以IV型等温剖面为主的介孔结构。此外,在500℃热解后,生物炭的比表面积最大(69.48 m2/g)。XRD (x射线衍射仪)表征表明,炉渣的加入促进了钙硅基物质与重金属结合形成晶体。FTIR光谱测试表明,渣的加入降低了O-H伸缩振动峰的强度,从而促进了芳烃和环氧化物结构的形成,增强了重金属的稳定性。密度泛函理论(DFT)计算表明,炉渣与Zn形成共价键,降低了Zn在热解过程中的挥发风险。本文的实验和模拟结果为污泥热解过程中重金属的管理提供了新的见解。图形抽象
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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