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Structural and functional diversity of microbial communities in ancient mining sites from San Luis Potosí, México
The purpose of this study was to evaluate the effects of potentially toxic elements (PTEs) on soil microbial community functionality and structure. Charcas and Cedral in San Luis Potosí, Mexico, are sites with ancient mining activity. This activity has generated heavy metals (HMs) polluted soils tha...
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Published in: | Land degradation & development 2024-10, Vol.35 (16), p.4841-4852 |
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creator | Martínez‐Toledo, Ángeles Ilizaliturri‐Hernández, César A. Torres‐Dosal, Arturo Briones‐Gallardo, Roberto Tintos‐Gómez, Adrián González‐Mille, Donaji J. |
description | The purpose of this study was to evaluate the effects of potentially toxic elements (PTEs) on soil microbial community functionality and structure. Charcas and Cedral in San Luis Potosí, Mexico, are sites with ancient mining activity. This activity has generated heavy metals (HMs) polluted soils that provoke deleterious effects on microbial community. Sampling was conducted in sites with and without aged mining activity. The parameters analysed were physicochemical properties and PTE concentrations. Functional diversity was evaluated with a community‐level physiological profiling (CLPP) analysis, diversity was evaluated using the richness (S), and the indices of Shannon's diversity (H), Simpson's dominance (D) and Pielou's evenness (J) were for the structure evaluation, based on relative substrate utilisation. CLPP results of set of soils indicated the following substrate utilisation pattern: carbohydrates > polymers (POL) > carboxylic/ketonic acids > amino acids (AmA) > amine/amides (A/A). In Cedral, the AmA utilisation favoured the increase of J value. In addition, it was observed that the utilisation of these compounds decreases at a higher concentration of Al and organic matter (OM) but increases at a higher concentration of Cu, Pb, Zn, Fe, Mn, and Ni, a phenomenon opposite to that was observed in Charcas. The results of set of soil indicated that AmA utilisation increases the values of S, J, D, and H. These results indicate that the microorganisms in soil are resistant to high PTE concentrations, in that condition they need accessible carbon sources as energy and as nutrients, however, they adapted to use complex carbon sources (POL). Furthermore, it presented low OM mineralisation despite high values of H, or J, then some metabolic processes could be compromised. Therefore, an intervention for soil conservation and monitoring is required. |
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Charcas and Cedral in San Luis Potosí, Mexico, are sites with ancient mining activity. This activity has generated heavy metals (HMs) polluted soils that provoke deleterious effects on microbial community. Sampling was conducted in sites with and without aged mining activity. The parameters analysed were physicochemical properties and PTE concentrations. Functional diversity was evaluated with a community‐level physiological profiling (CLPP) analysis, diversity was evaluated using the richness (S), and the indices of Shannon's diversity (H), Simpson's dominance (D) and Pielou's evenness (J) were for the structure evaluation, based on relative substrate utilisation. CLPP results of set of soils indicated the following substrate utilisation pattern: carbohydrates > polymers (POL) > carboxylic/ketonic acids > amino acids (AmA) > amine/amides (A/A). In Cedral, the AmA utilisation favoured the increase of J value. In addition, it was observed that the utilisation of these compounds decreases at a higher concentration of Al and organic matter (OM) but increases at a higher concentration of Cu, Pb, Zn, Fe, Mn, and Ni, a phenomenon opposite to that was observed in Charcas. The results of set of soil indicated that AmA utilisation increases the values of S, J, D, and H. These results indicate that the microorganisms in soil are resistant to high PTE concentrations, in that condition they need accessible carbon sources as energy and as nutrients, however, they adapted to use complex carbon sources (POL). Furthermore, it presented low OM mineralisation despite high values of H, or J, then some metabolic processes could be compromised. Therefore, an intervention for soil conservation and monitoring is required.</description><identifier>ISSN: 1085-3278</identifier><identifier>EISSN: 1099-145X</identifier><identifier>DOI: 10.1002/ldr.5261</identifier><language>eng</language><publisher>Chichester, UK: John Wiley & Sons, Ltd</publisher><subject>Acidic soils ; Amides ; Amino acids ; Carbohydrates ; Carbon ; Carbon sources ; Environmental monitoring ; Heavy metals ; Historic sites ; Historical structures ; Microbial activity ; Microbiomes ; Microorganisms ; Mineralization ; Nutrients ; Organic matter ; Physicochemical properties ; physiological activity ; Physiological effects ; pollution ; Polymers ; potentially toxic element ; Soil analysis ; Soil conservation ; Soil microorganisms ; Soil pollution ; Soil properties ; Soil resistance ; Soil structure ; Structure-function relationships ; substrate diversity</subject><ispartof>Land degradation & development, 2024-10, Vol.35 (16), p.4841-4852</ispartof><rights>2024 John Wiley & Sons Ltd.</rights><rights>2024 John Wiley & Sons, Ltd.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><cites>FETCH-LOGICAL-c1841-4c99c1e99ed396c4914ebc23bbd040495c6bb4e21f1fdcabff96965542eb2cf13</cites><orcidid>0000-0002-0248-6898</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27923,27924</link.rule.ids></links><search><creatorcontrib>Martínez‐Toledo, Ángeles</creatorcontrib><creatorcontrib>Ilizaliturri‐Hernández, César A.</creatorcontrib><creatorcontrib>Torres‐Dosal, Arturo</creatorcontrib><creatorcontrib>Briones‐Gallardo, Roberto</creatorcontrib><creatorcontrib>Tintos‐Gómez, Adrián</creatorcontrib><creatorcontrib>González‐Mille, Donaji J.</creatorcontrib><title>Structural and functional diversity of microbial communities in ancient mining sites from San Luis Potosí, México</title><title>Land degradation & development</title><description>The purpose of this study was to evaluate the effects of potentially toxic elements (PTEs) on soil microbial community functionality and structure. Charcas and Cedral in San Luis Potosí, Mexico, are sites with ancient mining activity. This activity has generated heavy metals (HMs) polluted soils that provoke deleterious effects on microbial community. Sampling was conducted in sites with and without aged mining activity. The parameters analysed were physicochemical properties and PTE concentrations. Functional diversity was evaluated with a community‐level physiological profiling (CLPP) analysis, diversity was evaluated using the richness (S), and the indices of Shannon's diversity (H), Simpson's dominance (D) and Pielou's evenness (J) were for the structure evaluation, based on relative substrate utilisation. CLPP results of set of soils indicated the following substrate utilisation pattern: carbohydrates > polymers (POL) > carboxylic/ketonic acids > amino acids (AmA) > amine/amides (A/A). In Cedral, the AmA utilisation favoured the increase of J value. In addition, it was observed that the utilisation of these compounds decreases at a higher concentration of Al and organic matter (OM) but increases at a higher concentration of Cu, Pb, Zn, Fe, Mn, and Ni, a phenomenon opposite to that was observed in Charcas. The results of set of soil indicated that AmA utilisation increases the values of S, J, D, and H. These results indicate that the microorganisms in soil are resistant to high PTE concentrations, in that condition they need accessible carbon sources as energy and as nutrients, however, they adapted to use complex carbon sources (POL). Furthermore, it presented low OM mineralisation despite high values of H, or J, then some metabolic processes could be compromised. Therefore, an intervention for soil conservation and monitoring is required.</description><subject>Acidic soils</subject><subject>Amides</subject><subject>Amino acids</subject><subject>Carbohydrates</subject><subject>Carbon</subject><subject>Carbon sources</subject><subject>Environmental monitoring</subject><subject>Heavy metals</subject><subject>Historic sites</subject><subject>Historical structures</subject><subject>Microbial activity</subject><subject>Microbiomes</subject><subject>Microorganisms</subject><subject>Mineralization</subject><subject>Nutrients</subject><subject>Organic matter</subject><subject>Physicochemical properties</subject><subject>physiological activity</subject><subject>Physiological effects</subject><subject>pollution</subject><subject>Polymers</subject><subject>potentially toxic element</subject><subject>Soil analysis</subject><subject>Soil conservation</subject><subject>Soil microorganisms</subject><subject>Soil pollution</subject><subject>Soil properties</subject><subject>Soil resistance</subject><subject>Soil structure</subject><subject>Structure-function relationships</subject><subject>substrate diversity</subject><issn>1085-3278</issn><issn>1099-145X</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2024</creationdate><recordtype>article</recordtype><recordid>eNp1kM1KxDAUhYsoOI6CjxBw48KOuW3aTpbiP1QUR8FdaNJEMrTJmKTqPJILn2JezIzj1tW99_DdA-ckySHgCWCcnXatmxRZCVvJCDClKZDiZXu9T4s0z6rpbrLn_RxjDBWpRomfBTeIMLimQ41pkRqMCNqaeLb6XTqvwxJZhXotnOU6ysL2_WB00NIjbeKT0NKECBhtXlHko66c7dGsMagetEcPNli_-j5Bd6uvTy3sfrKjms7Lg785Tp6vLp_Ob9L6_vr2_KxOBUwJpERQKkBSKtucloJQIJKLLOe8xQQTWoiScyIzUKBa0XClaEnLoiCZ5JlQkI-To43vwtm3QfrA5nZwMZpnOUAFVRk9I3W8oWJA751UbOF037glA8zWlbJYKVtXGtF0g37oTi7_5Vh98fjL_wCR9Xse</recordid><startdate>202410</startdate><enddate>202410</enddate><creator>Martínez‐Toledo, Ángeles</creator><creator>Ilizaliturri‐Hernández, César A.</creator><creator>Torres‐Dosal, Arturo</creator><creator>Briones‐Gallardo, Roberto</creator><creator>Tintos‐Gómez, Adrián</creator><creator>González‐Mille, Donaji J.</creator><general>John Wiley & Sons, Ltd</general><general>Wiley Subscription Services, Inc</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7ST</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>KR7</scope><scope>SOI</scope><orcidid>https://orcid.org/0000-0002-0248-6898</orcidid></search><sort><creationdate>202410</creationdate><title>Structural and functional diversity of microbial communities in ancient mining sites from San Luis Potosí, México</title><author>Martínez‐Toledo, Ángeles ; Ilizaliturri‐Hernández, César A. ; Torres‐Dosal, Arturo ; Briones‐Gallardo, Roberto ; Tintos‐Gómez, Adrián ; González‐Mille, Donaji J.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c1841-4c99c1e99ed396c4914ebc23bbd040495c6bb4e21f1fdcabff96965542eb2cf13</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2024</creationdate><topic>Acidic soils</topic><topic>Amides</topic><topic>Amino acids</topic><topic>Carbohydrates</topic><topic>Carbon</topic><topic>Carbon sources</topic><topic>Environmental monitoring</topic><topic>Heavy metals</topic><topic>Historic sites</topic><topic>Historical structures</topic><topic>Microbial activity</topic><topic>Microbiomes</topic><topic>Microorganisms</topic><topic>Mineralization</topic><topic>Nutrients</topic><topic>Organic matter</topic><topic>Physicochemical properties</topic><topic>physiological activity</topic><topic>Physiological effects</topic><topic>pollution</topic><topic>Polymers</topic><topic>potentially toxic element</topic><topic>Soil analysis</topic><topic>Soil conservation</topic><topic>Soil microorganisms</topic><topic>Soil pollution</topic><topic>Soil properties</topic><topic>Soil resistance</topic><topic>Soil structure</topic><topic>Structure-function relationships</topic><topic>substrate diversity</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Martínez‐Toledo, Ángeles</creatorcontrib><creatorcontrib>Ilizaliturri‐Hernández, César A.</creatorcontrib><creatorcontrib>Torres‐Dosal, Arturo</creatorcontrib><creatorcontrib>Briones‐Gallardo, Roberto</creatorcontrib><creatorcontrib>Tintos‐Gómez, Adrián</creatorcontrib><creatorcontrib>González‐Mille, Donaji J.</creatorcontrib><collection>CrossRef</collection><collection>Environment Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><collection>Environment Abstracts</collection><jtitle>Land degradation & development</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Martínez‐Toledo, Ángeles</au><au>Ilizaliturri‐Hernández, César A.</au><au>Torres‐Dosal, Arturo</au><au>Briones‐Gallardo, Roberto</au><au>Tintos‐Gómez, Adrián</au><au>González‐Mille, Donaji J.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Structural and functional diversity of microbial communities in ancient mining sites from San Luis Potosí, México</atitle><jtitle>Land degradation & development</jtitle><date>2024-10</date><risdate>2024</risdate><volume>35</volume><issue>16</issue><spage>4841</spage><epage>4852</epage><pages>4841-4852</pages><issn>1085-3278</issn><eissn>1099-145X</eissn><abstract>The purpose of this study was to evaluate the effects of potentially toxic elements (PTEs) on soil microbial community functionality and structure. Charcas and Cedral in San Luis Potosí, Mexico, are sites with ancient mining activity. This activity has generated heavy metals (HMs) polluted soils that provoke deleterious effects on microbial community. Sampling was conducted in sites with and without aged mining activity. The parameters analysed were physicochemical properties and PTE concentrations. Functional diversity was evaluated with a community‐level physiological profiling (CLPP) analysis, diversity was evaluated using the richness (S), and the indices of Shannon's diversity (H), Simpson's dominance (D) and Pielou's evenness (J) were for the structure evaluation, based on relative substrate utilisation. CLPP results of set of soils indicated the following substrate utilisation pattern: carbohydrates > polymers (POL) > carboxylic/ketonic acids > amino acids (AmA) > amine/amides (A/A). In Cedral, the AmA utilisation favoured the increase of J value. In addition, it was observed that the utilisation of these compounds decreases at a higher concentration of Al and organic matter (OM) but increases at a higher concentration of Cu, Pb, Zn, Fe, Mn, and Ni, a phenomenon opposite to that was observed in Charcas. The results of set of soil indicated that AmA utilisation increases the values of S, J, D, and H. These results indicate that the microorganisms in soil are resistant to high PTE concentrations, in that condition they need accessible carbon sources as energy and as nutrients, however, they adapted to use complex carbon sources (POL). Furthermore, it presented low OM mineralisation despite high values of H, or J, then some metabolic processes could be compromised. Therefore, an intervention for soil conservation and monitoring is required.</abstract><cop>Chichester, UK</cop><pub>John Wiley & Sons, Ltd</pub><doi>10.1002/ldr.5261</doi><tpages>12</tpages><orcidid>https://orcid.org/0000-0002-0248-6898</orcidid></addata></record> |
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subjects | Acidic soils Amides Amino acids Carbohydrates Carbon Carbon sources Environmental monitoring Heavy metals Historic sites Historical structures Microbial activity Microbiomes Microorganisms Mineralization Nutrients Organic matter Physicochemical properties physiological activity Physiological effects pollution Polymers potentially toxic element Soil analysis Soil conservation Soil microorganisms Soil pollution Soil properties Soil resistance Soil structure Structure-function relationships substrate diversity |
title | Structural and functional diversity of microbial communities in ancient mining sites from San Luis Potosí, México |
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