Li Binbin, Ding Songxiong, Fan Haihong, Ren Yu
College of Materials Science and Engineering, Xi'an University of Architecture and Technology, Xi'an 710055, China.
Department of Civil Engineering, Faculty of Science and Engineering, University of Agder, N4879 Grimstad, Norway.
Materials (Basel). 2021 Jan 18;14(2):447. doi: 10.3390/ma14020447.
Experimental investigations were carried out to study the effect of pyrolysis temperature on the characteristics, structure and total heavy metal contents of sewage sludge biochar (SSB). The changes in chemical forms of the heavy metals (Zn, Cu, Cr, Ni, Pb and Cd) caused by pyrolysis were analyzed, and the potential ecological risk of heavy metals in biochar (SSB) was evaluated. The conversion of sewage sludge into biochar by pyrolysis reduced the H/C and O/C ratios considerably, resulting in stronger carbonization and a higher degree of aromatic condensation in biochar. Measurement results showed that the pH and specific surface area of biochar increased as the pyrolysis temperature increased. It was found that elements Zn, Cu, Cr and Ni were enriched and confined in biochar SSB with increasing pyrolysis temperature from 300-700 °C; however, the residual rates of Pb and Cd in biochar SSB decreased significantly when the temperature was increased from 600 °C to 700 °C. Measurement with the BCR sequential extraction method revealed that the pyrolysis of sewage sludge at a suitable temperature transferred its bioavailable/degradable heavy metals into a more stable oxidizable/residual form in biochar SSB. Toxicity of heavy metals in biochar SSB could be reduced about four times if sewage sludge was pyrolyzed at a proper temperature; heavy metals confined in sludge SSB pyrolyzed at about 600 °C could be assessed as being low in ecological toxicity.
开展了实验研究,以考察热解温度对污泥生物炭(SSB)特性、结构及重金属总含量的影响。分析了热解导致的重金属(锌、铜、铬、镍、铅和镉)化学形态变化,并评估了生物炭(SSB)中重金属的潜在生态风险。通过热解将污泥转化为生物炭,显著降低了H/C和O/C比,使得生物炭的碳化作用增强,芳环缩合程度更高。测量结果表明,生物炭的pH值和比表面积随热解温度升高而增加。研究发现,随着热解温度从300℃升高至700℃,锌、铜、铬和镍元素在生物炭SSB中富集并固定;然而,当温度从600℃升高至700℃时,生物炭SSB中铅和镉的残留率显著下降。采用BCR连续萃取法测量发现,在合适温度下对污泥进行热解,可将其生物可利用/可降解的重金属转化为生物炭SSB中更稳定的可氧化/残留形态。如果在适当温度下对污泥进行热解,生物炭SSB中重金属的毒性可降低约四倍;在约600℃下热解的污泥SSB中所含重金属的生态毒性可评估为较低。