Insight into the Speciation of Heavy Metals in the Contaminated Soil Incubated with Corn Cob-Derived Biochar and Apatite

• Published in: Molecules (Basel, Switzerland) Vol. 28; no. 5; p. 2225
• Main Authors: Vuong, Truong Xuan, Stephen, Joseph, Nguyen, Thi Thu Thuy, Cao, Viet, Pham, Dung Thuy Nguyen
• Format: Journal Article
• Language: English
• Published: Switzerland MDPI AG 27.02.2023; MDPI
• Subjects: Apatite; Apatites; Causes of; Cellulose; Charcoal; Charcoal - chemistry; chemical fraction; Chemical properties; Chemical research; Contamination; Corn; Corn products; Decomposition; Ecosystem; Environmental aspects; Environmental protection; Extraction procedures; Farm buildings; heavy metal pollution; Heavy metals; Lead; Lignin; Manganese; Mass spectroscopy; Metal concentrations; metal remediation; Metals, Heavy - chemistry; Organic matter; Origin of species; Pollution; Sediment pollution; Soil - chemistry; Soil amendment; Soil contamination; Soil Pollutants - analysis; Soil pollution; Soil remediation; Soils; Speciation; Zea mays; Zinc; Vietnam; United States > US; metal remediation; chemical fraction; heavy metal pollution
• ISSN: 1420-3049; 1420-3049
• DOI: 10.3390/molecules28052225

Soil heavy metal contamination is a severe issue. The detrimental impact of contaminated heavy metals on the ecosystem depends on the chemical form of heavy metals. Biochar produced at 400 °C (CB400) and 600 °C (CB600) from corn cob was applied to remediate Pb and Zn in contaminated soil. After a one month amendment with biochar (CB400 and CB600) and apatite (AP) with the ratio of 3%, 5%, 10%, and 3:3% and 5:5% of the weight of biochar and apatite, the untreated and treated soil were extracted using Tessier's sequence extraction procedure. The five chemical fractions of the Tessier procedure were the exchangeable fraction (F1), carbonate fraction (F2), Fe/Mn oxide fraction (F3), organic matter (F4), and residual fraction (F5). The concentration of heavy metals in the five chemical fractions was analyzed using inductively coupled plasma mass spectroscopy (ICP-MS). The results showed that the total concentration of Pb and Zn in the soil was 3023.70 ± 98.60 mg kg and 2034.33 ± 35.41 mg kg , respectively. These figures were 15.12 and 6.78 times higher than the limit standard set by the United States Environmental Protection Agency (U.S. EPA 2010), indicating the high level of contamination of Pb and Zn in the studied soil. The treated soil's pH, OC, and EC increased significantly compared to the untreated soil ( > 0.05). The chemical fraction of Pb and Zn was in the descending sequence of F2 (67%) > F5 (13%) > F1 (10%) > F3 (9%) > F4 (1%) and F2~F3 (28%) > F5 (27%) > F1 (16%) > F4 (0.4%), respectively. The amendment of BC400, BC600, and apatite significantly reduced the exchangeable fraction of Pb and Zn and increased the other stable fractions including F3, F4, and F5, especially at the rate of 10% of biochar and a combination of 5:5% of biochar and apatite. The effects of CB400 and CB600 on the reduction in the exchangeable fraction of Pb and Zn were almost the same ( > 0.05). The results showed that CB400, CB600, and the mixture of these biochars with apatite applied at 5% or 10% ( / ) could immobilize lead and zinc in soil and reduce the threat to the surrounding environment. Therefore, biochar derived from corn cob and apatite could be promising materials for immobilizing heavy metals in multiple-contaminated soil.