Journal
JOURNAL OF HAZARDOUS MATERIALS
Volume 412, Issue -, Pages -Publisher
ELSEVIER
DOI: 10.1016/j.jhazmat.2021.125213
Keywords
Ca2+ bridging; Intercalated sorption; Bentonite; Goethite; Biochar stability
Categories
Funding
- National Natural Science Foundation of China [41907016, 21537002, U1906225]
- State Key Laboratory of Pollution Control and Resource Reuse Foundation [PCRRF19011]
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This study investigated the effects of soil minerals on the release of dissolvable biochar from biochar particles, with bentonite and goethite selected as model minerals. It was found that the presence of soil minerals and Ca2+ reduced the release of dissolvable biochar and enhanced its stability, reducing both chemical oxidation and biodegradation extents. The interactions between soil minerals and dissolvable biochar play a crucial role in the long-term carbon sequestration capability of biochar.
Biochar has two existing forms in the moist soil environment, free dissolvable biochar (particle size < 0.45 mu m) and undissolvable particles (particle size > 0.45 mu m). The release and decomposition of dissolvable biochar from bulk biochar particles is a primary C loss pathway in biochar-amended soils, which would be reduced by their interactions with soil minerals. Most previous studies focused on the effect of feedstock types and pyrolysis conditions on dissolvable biochar stability, while few studies researched the interaction between dissolvable biochar and soil components, for instance the soil minerals, and its effect on the stability of dissolvable biochar. In this study, bentonite and goethite were selected as model soil minerals because of their differences in structure and surface types: negatively charged 2:1 type phyllosilicate (bentonite) and positively charged crystalline mineral (goethite). Dry-wet cycling was conducted to determine the effect of these two minerals on the release of dissolvable biochar from walnut shell-derived biochar particles. The stability of dissolvable biochar was measured by chemical oxidation and biodegradation. Both soil minerals reduced the release of dissolvable biochar by over 34% with the presence of Ca2+. Mechanisms of Ca2+ bridging, ligand exchange and van der Waals attraction contributed to the formation of dissolvable biochar-bentonite complexes, and Ca2+ promoted dissolvable biochar inserting into bentonite interlayer space, expanding D-spacing from 1.25 nm to 1.55 nm. However, Ca2+ bridging barely formed on goethite because of charge repulsion, indicating that the dissolvable biochar was bound with goethite mainly by van der Waals attraction and ligand exchange. Due to organo-mineral complexes formation, the chemical oxidation extent of dissolvable biochar was reduced by 22.8-36.5%, and the biodegradation extent was reduced by 72.7-85.0%, since the soil minerals are more effective to prevent the dissolvable biochar from being biodegraded. This study proved soil minerals and Ca2+ were beneficial for enhancing biochar stability, these observations assisted in assessing the biochar ability for long-term carbon sequestration.
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