Wang Yu, Gu Xinfeng, Huang Yue, Ding Zhuhong, Chen Yijun, Hu Xin
School of Environmental Science & Engineering, Nanjing Tech University 30 Puzhu Southern Road Nanjing 211816 PR China
State Key Laboratory of Analytical Chemistry for Life Science, Centre of Materials Analysis and School of Chemistry & Chemical Engineering, Nanjing University 22 Hankou Road Nanjing 210023 PR China.
RSC Adv. 2022 Jul 4;12(30):19318-19326. doi: 10.1039/d2ra03052g. eCollection 2022 Jun 29.
Environmentally persistent free radicals (EPFRs) in biochars have the ability of catalytic formation of reactive oxygen species, which may pose potential oxidative stresses to eco-environment and human health. Therefore, comprehending the formation and characteristics of EPFRs in biochars is important for their further applications. In this study, the woody lignocellulosic biomass (wood chips, pine needle and barks), non-woody lignocellulosic biomass (rice husk, corn stover, and duckweed), and non-lignocellulosic biomass (anaerobically digested sludge) were selected as biomass feedstock to prepare biochars under different pyrolysis temperatures (200-700 °C). The impact of biomass feedstock on formation of biochar-bound EPFRs was systematically compared. Elemental compositions and atomic ratios of H/C and O/C varied greatly among different biomass feedstocks and the subsequently resulting biochars. EPFRs in biochars derived from the studied lignocellulosic biomass have similar levels of spin concentrations (10-10 spins per g) except for lower EPFRs in biochars under 200 and 700 °C; however, sludge-based biochars, a typical non-lignocellulosic-biomass-based biochar, have much lower EPFRs (10 spins per g) than lignocellulosic-biomass-based biochars under all the studied pyrolysis temperatures. Values of factors ranged from 2.0025 to 2.0042 and line width was in the range of 2.15-11.3 for EPFRs in the resulting biochars. Spin concentrations of biochar-bound EPFRs increased with the increasing pyrolysis temperatures from 200 to 500 °C, and then decreased rapidly from 500 to 700 °C and oxygen-centered radicals shifted to carbon-centered radicals with the increasing pyrolysis temperatures from 200 to 700 °C for all the studied biomass feedstock. 300-500 °C was the appropriate pyrolysis temperature range for higher levels of spin concentrations of biochar-bound EPFRs. Moreover, EPFRs' concentrations had significantly positive correlation with C contents and weak or none correlation with contents of transition metals. Overall, different types of biomass feedstock have significant impact on the formation of EPFRs in the resulting biochars.
生物炭中的环境持久性自由基(EPFRs)具有催化形成活性氧物种的能力,这可能会对生态环境和人类健康造成潜在的氧化应激。因此,了解生物炭中EPFRs的形成和特性对于其进一步应用至关重要。在本研究中,选择木质纤维素生物质(木屑、松针和树皮)、非木质纤维素生物质(稻壳、玉米秸秆和浮萍)以及非纤维素生物质(厌氧消化污泥)作为生物质原料,在不同热解温度(200-700°C)下制备生物炭。系统比较了生物质原料对生物炭结合EPFRs形成的影响。不同生物质原料及其随后生成的生物炭的元素组成以及H/C和O/C原子比差异很大。除了在200°C和700°C下的生物炭中EPFRs含量较低外,源自所研究的木质纤维素生物质的生物炭中EPFRs的自旋浓度水平相似(每克10-10个自旋);然而,基于污泥的生物炭是一种典型的基于非木质纤维素生物质的生物炭,在所有研究的热解温度下,其EPFRs含量(每克10个自旋)远低于基于木质纤维素生物质的生物炭。所得生物炭中EPFRs的g因子值在2.0025至2.0042之间,线宽在2.15-11.3范围内。对于所有研究的生物质原料,生物炭结合EPFRs的自旋浓度随着热解温度从200°C升高到500°C而增加,然后从500°C迅速下降到700°C,并且随着热解温度从200°C升高到700°C,以氧为中心的自由基转变为以碳为中心的自由基。300-500°C是生物炭结合EPFRs自旋浓度较高的合适热解温度范围。此外,EPFRs的浓度与C含量呈显著正相关,与过渡金属含量呈弱相关或无相关性。总体而言,不同类型的生物质原料对所得生物炭中EPFRs的形成有显著影响。