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Analysis of the Degradation of OCPs Contaminated Soil by the BC/nZVI Combined with Indigenous Microorganisms

Bibliographic Data

ID15479219
AuthorsQun Li (0000-0003-2231-6615, Ministry of Ecology and Environment), Lei Zhang (0000-0003-4889-6486, Ministry of Ecology and Environment), Jinzhong Wan (Ministry of Ecology and Environment), Tingting Fan (0000-0003-0948-2571, Ministry of Ecology and Environment), Shaopo Deng (0000-0001-8185-3854, Ministry of Ecology and Environment), Yan Zhou (0000-0002-3659-5881, Ministry of Ecology and Environment), Yue He (0000-0001-5994-4928, Ministry of Ecology and Environment, corresponding author)
Year2023
Volume20
Issue5
Pages4314-4314
Publication date2023-02-28
Peer ReviewedYes
Open AccessYes
TypeARTICLE
VenueInternational Journal of Environmental Research and Public Health (JOURNAL)
Journal identifiersISSN: 1661-7827 • E-ISSN: 1660-4601
PublisherMultidisciplinary Digital Publishing Institute (PUBLISHER • CH)
DOI10.3390/ijerph20054314
PMID36901323
OpenAlexW4322619391
LanguageEN
References cited24

Organochlorine pesticides (OCPs) were typical persistent organic pollutants that posed great hazards and high risks in soil. In this study, a peanut shell biochar-loaded nano zero-valent iron (BC/nZVI) material was prepared in combination with soil indigenous microorganisms to enhance the degradation of α-hexachlorocyclohexane(α-HCH) and γ-hexachlorocyclohexane(γ-HCH) in water and soil. The effects of BC/nZVI on indigenous microorganisms in soil were investigated based on the changes in redox potential and dehydrogenase activity in the soil. The results showed as follows: (1) The specific surface area of peanut shell biochar loaded with nano-zero-valent iron was large, and the nano-zero-valent iron particles were evenly distributed on the peanut shell biochar; (2) peanut shell BC/nZVI had a good degradation effect on α-HCH and γ-HCH in water, with degradation rates of 64.18% for α-HCH and 91.87% for γ-HCH in 24 h; (3) peanut shell BC/nZVI also had a good degradation effect on α-HCH and γ-HCH in soil, and the degradation rates of α-HCH and γ-HCH in the 1% BC/nZVI reached 55.2% and 85.4%, second only to 1% zero-valent iron. The degradation rate was the fastest from 0 to 7 days, while the soil oxidation-reduction potential (ORP) increased sharply. (4) The addition of BC/nZVI to the soil resulted in a significant increase in dehydrogenase activity, which further promoted the degradation of HCHs; the amount of HCHs degradation was significantly negatively correlated with dehydrogenase activity. This study provides a remediation strategy for HCH-contaminated sites, reducing the human health risk of HCHs in the soil while helping to improve the soil and increase the activity of soil microorganisms

Agronomy · Bacteria · Biochar · Biodegradation · Biology · Contamination · Degradation (telecommunications · Environmental remediation · Hexachlorocyclohexane · Microorganism · Pesticide · Pollutant · Pyrolysis · Soil contamination · Soil Pollutants · Soil water · Zerovalent iron · Advanced oxidation water treatment · Chemistry · Environmental remediation with nanomaterials · Environmental Science · Microbial bioremediation and biosurfactants · Ecology · Environmental Chemistry · Soil Science

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