Biochar Based on <i>Boehmeria nivea</i> from Arsenic--Contaminated Soil and the Effect on Soil

The utilization of remediating plants is an important factor that restricts phytoremediation.Ramie has good adsorption capacity for various heavy metals and is widely used in plant remediation.To achieve the multi-purpose development of heavy metal-contaminated ramie, research has been conducted on the preparation of biochar for using it as a raw material, and the feasibility of returning the prepared biochar to the soil has been explored.The results indicate that 300 ℃ is the appropriate pyrolysis temperature for preparing ramie biochar.Under these conditions, the biochar yield is 42.90 ± 2.29%, significantly higher than other pyrolysis temperatures, and the arsenic concentration is also lower.Removing arsenic from ramie biochar is crucial for biochar to return to the soil, and 85.62 ± 1.36% of arsenic can be removed through three rounds of 300 mM sodium hydroxide extraction.Adding modified biochar to heavy metalcontaminated soil can increase soil pH and organic matter content but does not significantly increase soil arsenic content.However, adding modified biochar did not significantly alter soil microbial community structure.A feasible plan for preparing reusable biochar using contaminated ramie was proposed in this study.The research results can directly serve the remediation of soil arsenic pollution using ramie and have reference significance for other plants to carry out heavy metal remediation.

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Publication Details

Journal
Polish Journal of Environmental Studies
Published
2024-08-05
DOI
https://doi.org/10.15244/pjoes/186424
Citations
1
Primary Topic
Clay minerals and soil interactions
Type
article
Field-Weighted Citation Impact
0.17
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article

Biochar Based on Boehmeria nivea from Arsenic--Contaminated Soil and the Effect on Soil

Y. Qiu, Shizhi Wen, Lin Yue, Lili Yang et al.
1 citations
Polish Journal of Environmental Studies
Clay minerals and soil interactions
0.17
article

Biochar Based on Boehmeria nivea from Arsenic--Contaminated Soil and the Effect on Soil

Y. Qiu, Shizhi Wen, Lin Yue, Lili Yang, Wenlong Shi, Kaiheng Ma
article en
1 citations

Abstract

The utilization of remediating plants is an important factor that restricts phytoremediation.Ramie has good adsorption capacity for various heavy metals and is widely used in plant remediation.To achieve the multi-purpose development of heavy metal-contaminated ramie, research has been conducted on the preparation of biochar for using it as a raw material, and the feasibility of returning the prepared biochar to the soil has been explored.The results indicate that 300 ℃ is the appropriate pyrolysis temperature for preparing ramie biochar.Under these conditions, the biochar yield is 42.90 ± 2.29%, significantly higher than other pyrolysis temperatures, and the arsenic concentration is also lower.Removing arsenic from ramie biochar is crucial for biochar to return to the soil, and 85.62 ± 1.36% of arsenic can be removed through three rounds of 300 mM sodium hydroxide extraction.Adding modified biochar to heavy metalcontaminated soil can increase soil pH and organic matter content but does not significantly increase soil arsenic content.However, adding modified biochar did not significantly alter soil microbial community structure.A feasible plan for preparing reusable biochar using contaminated ramie was proposed in this study.The research results can directly serve the remediation of soil arsenic pollution using ramie and have reference significance for other plants to carry out heavy metal remediation.

Polish Journal of Environmental StudiesVol. 34(1)
Central South University of Forestry and Technology (CN), Central South University (CN), Hunan Research Academy of Environmental Sciences (CN), Northwest A&F University (CN)
Zero hunger
Openalex Percentile: Top 51%
Clay minerals and soil interactions
0.17
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Biochar Based on <i>Boehmeria nivea</i> from Arsenic--Contaminated Soil and the Effect on Soil — Y. Qiu, Shizhi Wen, et al. · Polish Journal of Environmental Studies (2024) | TGRS Research Map | TGRS