Arsenic and antimony co-contamination influences on soil microbial community composition and functions: Relevance to arsenic resistance and carbon, nitrogen, and sulfur cycling

Microorganisms can mediate arsenic (As) and antimony (Sb) transformation and thus change the As and Sb toxicity and mobility. The influence of As and Sb on the innate microbiome has been extensively characterized. However, how microbial metabolic potentials are influenced by the As and Sb co-contami...

Full description

Bibliographic Details
Main Authors: Yongbin Li, Miaomiao Zhang, Rui Xu, Hanzhi Lin, Xiaoxu Sun, Fuqing Xu, Pin Gao, Tianle Kong, Enzong Xiao, Nie Yang, Weimin Sun
Format: Article
Language:English
Published: Elsevier 2021-08-01
Series:Environment International
Subjects:
Online Access:http://www.sciencedirect.com/science/article/pii/S0160412021001471
_version_ 1819101166361903104
author Yongbin Li
Miaomiao Zhang
Rui Xu
Hanzhi Lin
Xiaoxu Sun
Fuqing Xu
Pin Gao
Tianle Kong
Enzong Xiao
Nie Yang
Weimin Sun
author_facet Yongbin Li
Miaomiao Zhang
Rui Xu
Hanzhi Lin
Xiaoxu Sun
Fuqing Xu
Pin Gao
Tianle Kong
Enzong Xiao
Nie Yang
Weimin Sun
author_sort Yongbin Li
collection DOAJ
description Microorganisms can mediate arsenic (As) and antimony (Sb) transformation and thus change the As and Sb toxicity and mobility. The influence of As and Sb on the innate microbiome has been extensively characterized. However, how microbial metabolic potentials are influenced by the As and Sb co-contamination is still ambiguous. In this study, we selected two contrasting sites located in the Shimen realgar mine, the largest realgar mine in Asia, to explore the adaptability and response of the soil microbiome to As and Sb co-contamination and the impact of co-contamination on microbial metabolic potentials. It is observed that the geochemical parameters, including the As and Sb fractions, were the driving forces that reshaped the community composition and metabolic potentials. Bacteria associated with Bradyrhizobium, Nocardioides, Sphingomonas, Burkholderia, and Streptomyces were predicted to be tolerant to high concentrations of As and Sb. Co-occurrence network analysis revealed that the genes related to C fixation, nitrate/nitrite reduction, N fixation, and sulfate reduction were positively correlated with the As and Sb fractions, suggesting that As and Sb biogeochemical cycling may interact with and benefit from C, N, and S cycling. The results suggest that As and Sb co-contamination not only influences As-related genes, but also influences other genes correlated with microbial C, N, and S cycling.
first_indexed 2024-12-22T01:14:21Z
format Article
id doaj.art-4cbe9c3f80f24f92bbd2686920d535b0
institution Directory Open Access Journal
issn 0160-4120
language English
last_indexed 2024-12-22T01:14:21Z
publishDate 2021-08-01
publisher Elsevier
record_format Article
series Environment International
spelling doaj.art-4cbe9c3f80f24f92bbd2686920d535b02022-12-21T18:43:54ZengElsevierEnvironment International0160-41202021-08-01153106522Arsenic and antimony co-contamination influences on soil microbial community composition and functions: Relevance to arsenic resistance and carbon, nitrogen, and sulfur cyclingYongbin Li0Miaomiao Zhang1Rui Xu2Hanzhi Lin3Xiaoxu Sun4Fuqing Xu5Pin Gao6Tianle Kong7Enzong Xiao8Nie Yang9Weimin Sun10National-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, ChinaNational-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, ChinaNational-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, ChinaNational-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, ChinaNational-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, ChinaNational-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, ChinaNational-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, China; College of Environmental Science and Engineering, Textile Pollution Controlling Engineering Center of Ministry of Environmental Protection, Donghua University, Shanghai 201620, ChinaNational-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, ChinaInnovation Center and Key Laboratory of Waters Safety & Protection in the Pearl River Delta, Ministry of Education, Guangzhou University, Guangzhou 510006, ChinaNational-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, ChinaNational-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, China; Corresponding author at: 808 Tianyuan Road, Guangzhou, Guangdong, China.Microorganisms can mediate arsenic (As) and antimony (Sb) transformation and thus change the As and Sb toxicity and mobility. The influence of As and Sb on the innate microbiome has been extensively characterized. However, how microbial metabolic potentials are influenced by the As and Sb co-contamination is still ambiguous. In this study, we selected two contrasting sites located in the Shimen realgar mine, the largest realgar mine in Asia, to explore the adaptability and response of the soil microbiome to As and Sb co-contamination and the impact of co-contamination on microbial metabolic potentials. It is observed that the geochemical parameters, including the As and Sb fractions, were the driving forces that reshaped the community composition and metabolic potentials. Bacteria associated with Bradyrhizobium, Nocardioides, Sphingomonas, Burkholderia, and Streptomyces were predicted to be tolerant to high concentrations of As and Sb. Co-occurrence network analysis revealed that the genes related to C fixation, nitrate/nitrite reduction, N fixation, and sulfate reduction were positively correlated with the As and Sb fractions, suggesting that As and Sb biogeochemical cycling may interact with and benefit from C, N, and S cycling. The results suggest that As and Sb co-contamination not only influences As-related genes, but also influences other genes correlated with microbial C, N, and S cycling.http://www.sciencedirect.com/science/article/pii/S0160412021001471Metabolic potentialsRealgar oreCo-occurrence networkMining pollutionRandom forest
spellingShingle Yongbin Li
Miaomiao Zhang
Rui Xu
Hanzhi Lin
Xiaoxu Sun
Fuqing Xu
Pin Gao
Tianle Kong
Enzong Xiao
Nie Yang
Weimin Sun
Arsenic and antimony co-contamination influences on soil microbial community composition and functions: Relevance to arsenic resistance and carbon, nitrogen, and sulfur cycling
Environment International
Metabolic potentials
Realgar ore
Co-occurrence network
Mining pollution
Random forest
title Arsenic and antimony co-contamination influences on soil microbial community composition and functions: Relevance to arsenic resistance and carbon, nitrogen, and sulfur cycling
title_full Arsenic and antimony co-contamination influences on soil microbial community composition and functions: Relevance to arsenic resistance and carbon, nitrogen, and sulfur cycling
title_fullStr Arsenic and antimony co-contamination influences on soil microbial community composition and functions: Relevance to arsenic resistance and carbon, nitrogen, and sulfur cycling
title_full_unstemmed Arsenic and antimony co-contamination influences on soil microbial community composition and functions: Relevance to arsenic resistance and carbon, nitrogen, and sulfur cycling
title_short Arsenic and antimony co-contamination influences on soil microbial community composition and functions: Relevance to arsenic resistance and carbon, nitrogen, and sulfur cycling
title_sort arsenic and antimony co contamination influences on soil microbial community composition and functions relevance to arsenic resistance and carbon nitrogen and sulfur cycling
topic Metabolic potentials
Realgar ore
Co-occurrence network
Mining pollution
Random forest
url http://www.sciencedirect.com/science/article/pii/S0160412021001471
work_keys_str_mv AT yongbinli arsenicandantimonycocontaminationinfluencesonsoilmicrobialcommunitycompositionandfunctionsrelevancetoarsenicresistanceandcarbonnitrogenandsulfurcycling
AT miaomiaozhang arsenicandantimonycocontaminationinfluencesonsoilmicrobialcommunitycompositionandfunctionsrelevancetoarsenicresistanceandcarbonnitrogenandsulfurcycling
AT ruixu arsenicandantimonycocontaminationinfluencesonsoilmicrobialcommunitycompositionandfunctionsrelevancetoarsenicresistanceandcarbonnitrogenandsulfurcycling
AT hanzhilin arsenicandantimonycocontaminationinfluencesonsoilmicrobialcommunitycompositionandfunctionsrelevancetoarsenicresistanceandcarbonnitrogenandsulfurcycling
AT xiaoxusun arsenicandantimonycocontaminationinfluencesonsoilmicrobialcommunitycompositionandfunctionsrelevancetoarsenicresistanceandcarbonnitrogenandsulfurcycling
AT fuqingxu arsenicandantimonycocontaminationinfluencesonsoilmicrobialcommunitycompositionandfunctionsrelevancetoarsenicresistanceandcarbonnitrogenandsulfurcycling
AT pingao arsenicandantimonycocontaminationinfluencesonsoilmicrobialcommunitycompositionandfunctionsrelevancetoarsenicresistanceandcarbonnitrogenandsulfurcycling
AT tianlekong arsenicandantimonycocontaminationinfluencesonsoilmicrobialcommunitycompositionandfunctionsrelevancetoarsenicresistanceandcarbonnitrogenandsulfurcycling
AT enzongxiao arsenicandantimonycocontaminationinfluencesonsoilmicrobialcommunitycompositionandfunctionsrelevancetoarsenicresistanceandcarbonnitrogenandsulfurcycling
AT nieyang arsenicandantimonycocontaminationinfluencesonsoilmicrobialcommunitycompositionandfunctionsrelevancetoarsenicresistanceandcarbonnitrogenandsulfurcycling
AT weiminsun arsenicandantimonycocontaminationinfluencesonsoilmicrobialcommunitycompositionandfunctionsrelevancetoarsenicresistanceandcarbonnitrogenandsulfurcycling