Wu Weidong, Li Jianhong, Niazi Nabeel Khan, Müller Karin, Chu Yingchao, Zhang Lingling, Yuan Guodong, Lu Kouping, Song Zhaoliang, Wang Hailong
Ministry of Education Key Laboratory of Protection and Development Utilization of Tropical Crop Germplasm Resources, Hainan University, Haikou, 570228, China.
Key Laboratory of Soil Contamination Bioremediation of Zhejiang Province, Zhejiang A & F University, Lin'an, Hangzhou, 311300, China.
Environ Sci Pollut Res Int. 2016 Nov;23(22):22890-22896. doi: 10.1007/s11356-016-7428-0. Epub 2016 Aug 29.
Biochar has received widespread attention as an eco-friendly and efficient material for immobilization of toxic heavy metals in aqueous environments. In the present study, three types of coconut fiber-derived biochars were obtained by pyrolyzing at three temperatures, i.e., 300, 500, and 700 °C. In addition, nine types of biochars were prepared by chemical modification with ammonia, hydrogen peroxide, and nitric acid, respectively, which were used to investigate changes in physico-chemical properties by inter alia, Fourier transformation infrared spectrophotometry (FTIR), scanning electron microscope (SEM), and BET specific surface area analysis. Batch sorption experiments were carried out to determine the sorption capacity of the biochars for lead (Pb) in aqueous solutions. Results showed that the cation exchange capacity of biochar pyrolyzed at 300 °C and modified with nitric acid increased threefold compared to the control. Loosely corrugated carbon surface and uneven carbon surface of the biochar pyrolyzed at 300 °C were produced during ammonia and nitric acid modifications. Removal rate of Pb by the coconut biochar pyrolyzed at 300 °C and modified with ammonia was increased from 71.8 to 99.6 % compared to the untreated biochar in aqueous solutions containing 100 mg L Pb. However, chemical modification did not enhance adsorption of Pb of the biochars pyrolyzed at higher temperatures (e.g., 500 or 700 °C), indicating that resistance of biochars to chemical treatment increased with pyrolysis temperature.
生物炭作为一种在水环境中固定有毒重金属的环保高效材料受到了广泛关注。在本研究中,通过在300、500和700℃三个温度下热解获得了三种椰壳纤维衍生生物炭。此外,分别用氨、过氧化氢和硝酸进行化学改性制备了九种生物炭,通过傅里叶变换红外光谱法(FTIR)、扫描电子显微镜(SEM)和BET比表面积分析等方法研究其物理化学性质的变化。进行了批量吸附实验以测定生物炭对水溶液中铅(Pb)的吸附容量。结果表明,在300℃下热解并用硝酸改性的生物炭的阳离子交换容量比对照增加了两倍。在氨和硝酸改性过程中,产生了在300℃下热解的生物炭的松散波纹状碳表面和不均匀碳表面。在含有100 mg/L Pb的水溶液中,与未处理的生物炭相比,在300℃下热解并用氨改性的椰壳生物炭对Pb的去除率从71.8%提高到了99.6%。然而,化学改性并没有增强在较高温度(如500或700℃)下热解的生物炭对Pb的吸附,这表明生物炭对化学处理的抗性随着热解温度的升高而增加。