School of Resource and Environmental Sciences, Hubei Key Laboratory of Biomass-Resources Chemistry and Environmental Biotechnology, and Hubei International Scientific and Technological Cooperation Base of Sustainable Resource and Energy, Wuhan University, Wuhan, 430079, P.R. China.
Faculty of Technology and Innovation, and Vaasa Energy Institute, University of Vaasa, P.O. Box 700, FI-65101, Vaasa, Finland.
Environ Sci Pollut Res Int. 2021 Jul;28(27):36585-36597. doi: 10.1007/s11356-021-13286-x. Epub 2021 Mar 11.
In this study, biochar was generated from chicken manure by using a tube furnace under different temperatures (300, 500, and 700 °C), and the treatments were noted as J300, J500, and J700, respectively. In comparison, another type of biochar was prepared under 500 °C with a muffle furnace, and the treatment was noted as JM500. Biochar in treatment group J500 was subsequently modified with HNO and NaOH, and the treatments were noted as J500-HNO and J500-NaOH, respectively. The sorption efficiencies of naphthalene by the above six types of biochar were evaluated. Characteristic results showed that the surface pores of the biochar were improved with the increase of temperature, and biochar under the treatments J300, J500, J700, and JM500 experienced a high speed of adsorption within 1 h after the naphthalene adsorption started. The adsorption capacity of naphthalene increased with the increase of the initial concentration of naphthalene. Treatment J700 exhibited the largest adsorption capacity since its biochar surface pore structure was more fully developed with a crystal structure formed, and its specific surface area was increased by about 20 times compared to the original chicken manure. After biochar modification using HNO and NaOH, the infrared spectrum changed, and the adsorption active sites were increased. The biochar modification by HNO had a high naphthalene adsorption efficiency compared to NaOH. The order of adsorption capacity was as follows: J500 ≈ JM500 < J300 < J500-NaOH < J500-HNO < J700.
在这项研究中,鸡粪在不同温度(300、500 和 700°C)下使用管式炉生成生物炭,分别标记为 J300、J500 和 J700。相比之下,另一种生物炭在马弗炉中于 500°C 下制备,标记为 JM500。在 500°C 下用 HNO 和 NaOH 对 J500 中的生物炭进行改性,分别标记为 J500-HNO 和 J500-NaOH。评价了上述六种生物炭对萘的吸附效率。特征结果表明,随着温度的升高,生物炭的表面孔隙得到改善,在萘吸附开始后 1 小时内,J300、J500、J700 和 JM500 处理的生物炭吸附速度较快。萘的吸附容量随萘初始浓度的增加而增加。J700 处理的吸附容量最大,因为其生物炭表面的孔结构得到了更充分的发展,形成了晶体结构,比原始鸡粪的比表面积增加了约 20 倍。用 HNO 和 NaOH 对生物炭进行改性后,红外光谱发生了变化,吸附活性位增加。与 NaOH 相比,HNO 改性的生物炭对萘的吸附效率较高。吸附容量的顺序如下:J500≈JM500<J300<J500-NaOH<J500-HNO<J700。