Institute of Resources, Ecosystem and Environment of Agriculture, Nanjing Agricultural University, 1 Weigang, Nanjing, 210095, China; Jiangsu Collaborative Innovation Center for Solid Organic Waste Resource Utilization, China.
Institute of Resources, Ecosystem and Environment of Agriculture, Nanjing Agricultural University, 1 Weigang, Nanjing, 210095, China; Jiangsu Collaborative Innovation Center for Solid Organic Waste Resource Utilization, China; School of Materials Science and Engineering, University of New South Wales, Sydney, NSW, 2052, Australia.
J Environ Manage. 2024 Nov;370:122848. doi: 10.1016/j.jenvman.2024.122848. Epub 2024 Oct 11.
Iron (Fe) modified biochar has been widely used for cadmium (Cd) contaminated soil remediation. However, the accompanying anions introduced during the modification process potentially affect the behavior of Cd in soil. In this study, we investigated the distinct Cd immobilization mechanisms by Fe(SO) modified biochar (FSBC) and Fe(NO) modified biochar (FNBC) in a two-year pot experiment. Results showed that both FSBC and FNBC significantly reduced Cd concentrations in rice grains by 23%-42% and 30%-37% compared to pristine biochar (BC). Specifically, NFBC promoted the formation of amorphous Fe oxides by enhancing the NO-reducing Fe(II) oxidation process, which significantly increased Fe/Mn oxide-bound Cd and decreased soil CaCl-extractable Cd. For FSBC, the introduction of SO significantly promoted the formation of Fe plaques by enhancing the Fe(III) reduction process, which blocked the Cd transfer from the soil to the rice roots. More importantly, after two years of biochar application, an organo-mineral complex layer is formed on the biochar surface, which immobilized a large amount of Cd. The Cd immobilization on the surface of aged biochar could be due to the fixation by the secondary Fe oxides within the organo-mineral layer and the complexation by the surface functional groups. The result of laser ablation inductively coupled plasma mass spectrometry showed that the Cd content on aged FNBC and FSBC was 5.9 and 2.6 times higher than on aged BC. This might be attributed to the Fe-modified biochar's higher electron exchange capability (EEC), which promoted the development of organo-mineral complexes. Notably, the EEC of biochar was maintained during its aging process, which may keep the biochar surface active and facilitate continual Cd immobilization. This study revealed the complex mechanisms of soil Cd immobilization with Fe-modified biochar, providing new insights into sustainable biochar environmental remediation.
铁(Fe)改性生物炭已广泛用于修复镉(Cd)污染土壤。然而,改性过程中引入的伴随阴离子可能会影响土壤中 Cd 的行为。在这项为期两年的盆栽实验中,我们研究了 Fe(SO)改性生物炭(FSBC)和 Fe(NO)改性生物炭(FNBC)的独特 Cd 固定机制。结果表明,与原始生物炭(BC)相比,FSBC 和 FNBC 分别将稻米中 Cd 浓度降低了 23%-42%和 30%-37%。具体而言,FNBC 通过促进 NO 还原的 Fe(II)氧化过程促进了无定形 Fe 氧化物的形成,这显著增加了 Fe/Mn 氧化物结合态 Cd,减少了土壤 CaCl 提取态 Cd。对于 FSBC,SO 的引入通过增强 Fe(III)还原过程促进了 Fe 斑块的形成,从而阻止了 Cd 从土壤向水稻根系的转移。更重要的是,经过两年的生物炭应用后,在生物炭表面形成了一个有机-矿物复合层,固定了大量的 Cd。老化生物炭表面对 Cd 的固定可能是由于有机-矿物层内的次生 Fe 氧化物的固定和表面官能团的络合作用。激光烧蚀电感耦合等离子体质谱的结果表明,老化 FNBC 和 FSBC 上的 Cd 含量分别比老化 BC 高 5.9 和 2.6 倍。这可能归因于 Fe 改性生物炭更高的电子交换能力(EEC),促进了有机-矿物复合物的发展。值得注意的是,生物炭在老化过程中的 EEC 得以维持,这可能使生物炭表面保持活性并促进持续的 Cd 固定。本研究揭示了 Fe 改性生物炭固定土壤 Cd 的复杂机制,为可持续的生物炭环境修复提供了新的见解。