Effects of antimony on the soil enzymes, microbial, and rhizobial activity of legumes
Leguminous farmland in China is severely polluted by antimony. Here, to explore the effects of antimony stress on rhizobia and soil microorganisms in leguminous plants, mung beans, kidney beans, and peanuts were grown in soil with different concentrations of Sb3+, Sb5+, and Sb3++Sb5+. Antimony had a...
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| Veröffentlicht in: | Environmental pollutants & bioavailability 2024-12, Vol.36 (1) |
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| creator | Yang, Yiran Yang, Zaifu Tian, Xinyue Xu, Jingyao Kan, Simeng |
| description | Leguminous farmland in China is severely polluted by antimony. Here, to explore the effects of antimony stress on rhizobia and soil microorganisms in leguminous plants, mung beans, kidney beans, and peanuts were grown in soil with different concentrations of Sb3+, Sb5+, and Sb3++Sb5+. Antimony had a promotional effect on soil sucrase and catalase activities and an inhibitory effect on urease activity. The effects of Sb3+ on sucrase, catalase, and urease activities were 3.3–11.1, 1.27–1.29, and 1.24–3.05 times those of Sb5+, respectively. Antimony reduced the rhizobial activity by 20.63–57.84%, with the inhibitory effect positively related to the antimony content. Additionally, the inhibitory effect of Sb3+ was 1.10–2.22 times that of Sb5+. This inhibition decreased the total nitrogen and ammonia nitrogen content in the soil. However, the decrease in Sb3+ was 0.46–1.54 times that of Sb5+. Sb3+ significantly altered the microbial activity. |
| doi_str_mv | 10.1080/26395940.2024.2331771 |
| format | Article |
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Here, to explore the effects of antimony stress on rhizobia and soil microorganisms in leguminous plants, mung beans, kidney beans, and peanuts were grown in soil with different concentrations of Sb3+, Sb5+, and Sb3++Sb5+. Antimony had a promotional effect on soil sucrase and catalase activities and an inhibitory effect on urease activity. The effects of Sb3+ on sucrase, catalase, and urease activities were 3.3–11.1, 1.27–1.29, and 1.24–3.05 times those of Sb5+, respectively. Antimony reduced the rhizobial activity by 20.63–57.84%, with the inhibitory effect positively related to the antimony content. Additionally, the inhibitory effect of Sb3+ was 1.10–2.22 times that of Sb5+. This inhibition decreased the total nitrogen and ammonia nitrogen content in the soil. However, the decrease in Sb3+ was 0.46–1.54 times that of Sb5+. Sb3+ significantly altered the microbial activity.</description><identifier>ISSN: 2639-5932</identifier><identifier>EISSN: 2639-5940</identifier><identifier>DOI: 10.1080/26395940.2024.2331771</identifier><language>eng</language><publisher>Abingdon: Taylor & Francis Ltd</publisher><subject>Agricultural land ; Ammonia ; Antimony ; Beans ; Biological activity ; Catalase ; Enzymes ; Heavy metals ; Hydroelectric power ; Kidney beans ; Legumes ; Leguminous plants ; Microbial activity ; Microorganisms ; Nitrogen ; Pollution ; Research methodology ; Seeds ; Soil ; Soil contamination ; Soil microorganisms ; Soil pollution ; Soil stresses ; Soils ; Total nitrogen ; Toxicity ; Urease</subject><ispartof>Environmental pollutants & bioavailability, 2024-12, Vol.36 (1)</ispartof><rights>2024 The Author(s). Published by Informa UK Limited, trading as Taylor & Francis Group. This work is licensed under the Creative Commons Attribution – Non-Commercial License http://creativecommons.org/licenses/by-nc/4.0/ (the “License”). 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Sb3+ significantly altered the microbial activity.</description><subject>Agricultural land</subject><subject>Ammonia</subject><subject>Antimony</subject><subject>Beans</subject><subject>Biological activity</subject><subject>Catalase</subject><subject>Enzymes</subject><subject>Heavy metals</subject><subject>Hydroelectric power</subject><subject>Kidney beans</subject><subject>Legumes</subject><subject>Leguminous plants</subject><subject>Microbial activity</subject><subject>Microorganisms</subject><subject>Nitrogen</subject><subject>Pollution</subject><subject>Research methodology</subject><subject>Seeds</subject><subject>Soil</subject><subject>Soil contamination</subject><subject>Soil microorganisms</subject><subject>Soil pollution</subject><subject>Soil stresses</subject><subject>Soils</subject><subject>Total nitrogen</subject><subject>Toxicity</subject><subject>Urease</subject><issn>2639-5932</issn><issn>2639-5940</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2024</creationdate><recordtype>article</recordtype><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><recordid>eNo9kF1LwzAUhoMoOOZ-ghDwdq3JSdMklzLmBwy8cdehSROX0Y_ZdEL3623d9Op8vC_v4TwI3VOSUiLJI-RMcZWRFAhkKTBGhaBXaDbtk0m4_u8Z3KJFjHtCCFDIgNAZ2q69d7aPuPW4aPpQt82A2wb3O4djGyrsmtNQu7jEdbBda0JRLUdjibtdOP2OuLB9-A79MEVU7vM4uu_QjS-q6BaXOkfb5_XH6jXZvL-8rZ42iQWR9wl1xpZAuTM5s8IQr8oSmLR5pgTQwhkhS8XFqHGrBM9JyZiURlgC1pcG2Bw9nHMPXft1dLHX-_bYNeNJzWjGuFQ5yNHFz67xgRg75_WhC3XRDZoSPUHUfxD1BFFfILIfhy9kMw</recordid><startdate>20241231</startdate><enddate>20241231</enddate><creator>Yang, Yiran</creator><creator>Yang, Zaifu</creator><creator>Tian, Xinyue</creator><creator>Xu, Jingyao</creator><creator>Kan, Simeng</creator><general>Taylor & Francis Ltd</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7QH</scope><scope>7ST</scope><scope>7UA</scope><scope>8FE</scope><scope>8FG</scope><scope>8FH</scope><scope>ABJCF</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>AZQEC</scope><scope>BBNVY</scope><scope>BENPR</scope><scope>BGLVJ</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>D1I</scope><scope>DWQXO</scope><scope>EHMNL</scope><scope>F1W</scope><scope>GNUQQ</scope><scope>H97</scope><scope>HCIFZ</scope><scope>KB.</scope><scope>L.G</scope><scope>LK8</scope><scope>M7P</scope><scope>PDBOC</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PRINS</scope><scope>SOI</scope></search><sort><creationdate>20241231</creationdate><title>Effects of antimony on the soil enzymes, microbial, and rhizobial activity of legumes</title><author>Yang, Yiran ; 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Here, to explore the effects of antimony stress on rhizobia and soil microorganisms in leguminous plants, mung beans, kidney beans, and peanuts were grown in soil with different concentrations of Sb3+, Sb5+, and Sb3++Sb5+. Antimony had a promotional effect on soil sucrase and catalase activities and an inhibitory effect on urease activity. The effects of Sb3+ on sucrase, catalase, and urease activities were 3.3–11.1, 1.27–1.29, and 1.24–3.05 times those of Sb5+, respectively. Antimony reduced the rhizobial activity by 20.63–57.84%, with the inhibitory effect positively related to the antimony content. Additionally, the inhibitory effect of Sb3+ was 1.10–2.22 times that of Sb5+. This inhibition decreased the total nitrogen and ammonia nitrogen content in the soil. However, the decrease in Sb3+ was 0.46–1.54 times that of Sb5+. Sb3+ significantly altered the microbial activity.</abstract><cop>Abingdon</cop><pub>Taylor & Francis Ltd</pub><doi>10.1080/26395940.2024.2331771</doi><oa>free_for_read</oa></addata></record> |
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| subjects | Agricultural land Ammonia Antimony Beans Biological activity Catalase Enzymes Heavy metals Hydroelectric power Kidney beans Legumes Leguminous plants Microbial activity Microorganisms Nitrogen Pollution Research methodology Seeds Soil Soil contamination Soil microorganisms Soil pollution Soil stresses Soils Total nitrogen Toxicity Urease |
| title | Effects of antimony on the soil enzymes, microbial, and rhizobial activity of legumes |
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