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Traces of the past: assessing the impact of potentially toxic elements from an abandoned mine on groundwater and agricultural soil in San Luis Potosí, México
The study was conducted in Cerritos, San Luis Potosí, México, near the Guaxcama mine, focused on environmental contamination (groundwater and agricultural soil) from antimony (Sb), arsenic (As), lead (Pb), cadmium (Cd), and mercury (Hg). In March 2022, 20 agricultural soil and 16 groundwater samples...
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Published in: | Environmental monitoring and assessment 2024-11, Vol.196 (11), p.1015, Article 1015 |
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creator | Silva-Gigante, M. Hinojosa-Reyes, L. Bazzan-Dessuy, M. Rosas-Castor, J. M. Torres-Gaytán, D. E. Quero-Jiménez, P. C. Caballero-Quintero, A. Guzmán-Mar, J. L. |
description | The study was conducted in Cerritos, San Luis Potosí, México, near the Guaxcama mine, focused on environmental contamination (groundwater and agricultural soil) from antimony (Sb), arsenic (As), lead (Pb), cadmium (Cd), and mercury (Hg). In March 2022, 20 agricultural soil and 16 groundwater samples were collected near the historically cinnabar (HgS)- and arsenopyrite (FeAsS)-rich Guaxcama mine. Hydride generation atomic fluorescence spectrometry (HG-AFS) for As, cold vapor atomic fluorescence spectrometry (CV-AFS) for Hg, and inductively coupled plasma optical emission spectrometry (ICP-OES) for Cd, Pb, and Sb were used for the determinations of potentially toxic elements (PTEs). While concentrations of Cd, Hg, Pb, and Sb in groundwater were below detection limits, As levels exhibited a range from 40.9 ± 1.4 to 576.0 ± 1.0 µg/L, exceeding permissible limits for drinking water (10 µg/L). In agricultural soil, As was between 7.67 ± 0.16 and 24.1 ± 0.4 µg/g, Hg ranged from 0.203 ± 0.018 to 2.33 ± 0.19 µg/g, Cd from 2.53 ± 0.90 to 2.78 ± 0.01 µg/g, and Pb from 11.7 ± 1.2 to 34.3 ± 4.1 µg/g. Only one study area surpassed the Mexican As soil limit of 22 µg/g. Sequential extraction (four-step BCR procedure) indicated significant As bioavailability in soil (fractions 1 and 2) ranging from 3.66 to 10.36%, heightening the risk of crop transfer, in contrast to the low bioavailability of Hg, showing that fractions 1, 2, and 3 were below the limit of quantification (LOQ). Crucial physicochemical parameters in soil, including nitrate levels, pH, and organic matter, were pivotal in understanding contamination dynamics. Principal component analysis highlighted the influence of elements like Fe and Ca on phytoavailable As, while Pb and Cd likely originated from a common source. Ecological risk assessments underscored the significant impact of pollution, primarily due to the concentrations of Cd and Hg. Non-cancer and cancer risks to residents through As poisoning via contaminated water ingestion also were found. The hazard index (HI) values varied between 4.0 and 82.2 for adults and children. The total incremental lifetime cancer risk (TILCAR) values for adults ranged from 7.75E − 04 to 1.06E − 02, whereas for children, the values were from 2.47E − 04 to 3.17E − 03. |
doi_str_mv | 10.1007/s10661-024-13081-4 |
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M. ; Torres-Gaytán, D. E. ; Quero-Jiménez, P. C. ; Caballero-Quintero, A. ; Guzmán-Mar, J. L.</creator><creatorcontrib>Silva-Gigante, M. ; Hinojosa-Reyes, L. ; Bazzan-Dessuy, M. ; Rosas-Castor, J. M. ; Torres-Gaytán, D. E. ; Quero-Jiménez, P. C. ; Caballero-Quintero, A. ; Guzmán-Mar, J. L.</creatorcontrib><description>The study was conducted in Cerritos, San Luis Potosí, México, near the Guaxcama mine, focused on environmental contamination (groundwater and agricultural soil) from antimony (Sb), arsenic (As), lead (Pb), cadmium (Cd), and mercury (Hg). In March 2022, 20 agricultural soil and 16 groundwater samples were collected near the historically cinnabar (HgS)- and arsenopyrite (FeAsS)-rich Guaxcama mine. Hydride generation atomic fluorescence spectrometry (HG-AFS) for As, cold vapor atomic fluorescence spectrometry (CV-AFS) for Hg, and inductively coupled plasma optical emission spectrometry (ICP-OES) for Cd, Pb, and Sb were used for the determinations of potentially toxic elements (PTEs). While concentrations of Cd, Hg, Pb, and Sb in groundwater were below detection limits, As levels exhibited a range from 40.9 ± 1.4 to 576.0 ± 1.0 µg/L, exceeding permissible limits for drinking water (10 µg/L). In agricultural soil, As was between 7.67 ± 0.16 and 24.1 ± 0.4 µg/g, Hg ranged from 0.203 ± 0.018 to 2.33 ± 0.19 µg/g, Cd from 2.53 ± 0.90 to 2.78 ± 0.01 µg/g, and Pb from 11.7 ± 1.2 to 34.3 ± 4.1 µg/g. Only one study area surpassed the Mexican As soil limit of 22 µg/g. Sequential extraction (four-step BCR procedure) indicated significant As bioavailability in soil (fractions 1 and 2) ranging from 3.66 to 10.36%, heightening the risk of crop transfer, in contrast to the low bioavailability of Hg, showing that fractions 1, 2, and 3 were below the limit of quantification (LOQ). Crucial physicochemical parameters in soil, including nitrate levels, pH, and organic matter, were pivotal in understanding contamination dynamics. Principal component analysis highlighted the influence of elements like Fe and Ca on phytoavailable As, while Pb and Cd likely originated from a common source. Ecological risk assessments underscored the significant impact of pollution, primarily due to the concentrations of Cd and Hg. Non-cancer and cancer risks to residents through As poisoning via contaminated water ingestion also were found. The hazard index (HI) values varied between 4.0 and 82.2 for adults and children. 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Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.</rights><rights>2024. The Author(s), under exclusive licence to Springer Nature Switzerland AG.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><cites>FETCH-LOGICAL-c256t-6b8834afc3a8fa0b12ad897b37024248237a5e9d63ae972c573b027c09a728193</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27924,27925</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/39365363$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Silva-Gigante, M.</creatorcontrib><creatorcontrib>Hinojosa-Reyes, L.</creatorcontrib><creatorcontrib>Bazzan-Dessuy, M.</creatorcontrib><creatorcontrib>Rosas-Castor, J. M.</creatorcontrib><creatorcontrib>Torres-Gaytán, D. E.</creatorcontrib><creatorcontrib>Quero-Jiménez, P. C.</creatorcontrib><creatorcontrib>Caballero-Quintero, A.</creatorcontrib><creatorcontrib>Guzmán-Mar, J. L.</creatorcontrib><title>Traces of the past: assessing the impact of potentially toxic elements from an abandoned mine on groundwater and agricultural soil in San Luis Potosí, México</title><title>Environmental monitoring and assessment</title><addtitle>Environ Monit Assess</addtitle><addtitle>Environ Monit Assess</addtitle><description>The study was conducted in Cerritos, San Luis Potosí, México, near the Guaxcama mine, focused on environmental contamination (groundwater and agricultural soil) from antimony (Sb), arsenic (As), lead (Pb), cadmium (Cd), and mercury (Hg). In March 2022, 20 agricultural soil and 16 groundwater samples were collected near the historically cinnabar (HgS)- and arsenopyrite (FeAsS)-rich Guaxcama mine. Hydride generation atomic fluorescence spectrometry (HG-AFS) for As, cold vapor atomic fluorescence spectrometry (CV-AFS) for Hg, and inductively coupled plasma optical emission spectrometry (ICP-OES) for Cd, Pb, and Sb were used for the determinations of potentially toxic elements (PTEs). While concentrations of Cd, Hg, Pb, and Sb in groundwater were below detection limits, As levels exhibited a range from 40.9 ± 1.4 to 576.0 ± 1.0 µg/L, exceeding permissible limits for drinking water (10 µg/L). In agricultural soil, As was between 7.67 ± 0.16 and 24.1 ± 0.4 µg/g, Hg ranged from 0.203 ± 0.018 to 2.33 ± 0.19 µg/g, Cd from 2.53 ± 0.90 to 2.78 ± 0.01 µg/g, and Pb from 11.7 ± 1.2 to 34.3 ± 4.1 µg/g. Only one study area surpassed the Mexican As soil limit of 22 µg/g. Sequential extraction (four-step BCR procedure) indicated significant As bioavailability in soil (fractions 1 and 2) ranging from 3.66 to 10.36%, heightening the risk of crop transfer, in contrast to the low bioavailability of Hg, showing that fractions 1, 2, and 3 were below the limit of quantification (LOQ). Crucial physicochemical parameters in soil, including nitrate levels, pH, and organic matter, were pivotal in understanding contamination dynamics. Principal component analysis highlighted the influence of elements like Fe and Ca on phytoavailable As, while Pb and Cd likely originated from a common source. Ecological risk assessments underscored the significant impact of pollution, primarily due to the concentrations of Cd and Hg. Non-cancer and cancer risks to residents through As poisoning via contaminated water ingestion also were found. The hazard index (HI) values varied between 4.0 and 82.2 for adults and children. The total incremental lifetime cancer risk (TILCAR) values for adults ranged from 7.75E − 04 to 1.06E − 02, whereas for children, the values were from 2.47E − 04 to 3.17E − 03.</description><subject>Abandoned mines</subject><subject>Adults</subject><subject>Agricultural land</subject><subject>Agriculture</subject><subject>Antimony</subject><subject>Antimony - analysis</subject><subject>Arsenic</subject><subject>Arsenic - analysis</subject><subject>Arsenopyrite</subject><subject>Atmospheric Protection/Air Quality Control/Air Pollution</subject><subject>Bioavailability</subject><subject>Cadmium</subject><subject>Cadmium - analysis</subject><subject>Cancer</subject><subject>Children</subject><subject>Contamination</subject><subject>Detection limits</subject><subject>Drinking water</subject><subject>Earth and Environmental Science</subject><subject>Ecology</subject><subject>Ecotoxicology</subject><subject>Environment</subject><subject>Environmental impact</subject><subject>Environmental Management</subject><subject>Environmental Monitoring</subject><subject>Fluorescence</subject><subject>Groundwater</subject><subject>Groundwater - chemistry</subject><subject>Groundwater mining</subject><subject>Health risks</subject><subject>Impact analysis</subject><subject>Inductively coupled plasma</subject><subject>Ingestion</subject><subject>Lead</subject><subject>Lead - analysis</subject><subject>Mercury</subject><subject>Mercury (metal)</subject><subject>Mercury - analysis</subject><subject>Metals, Heavy - analysis</subject><subject>Mexico</subject><subject>Mining</subject><subject>Monitoring/Environmental Analysis</subject><subject>Optical emission spectroscopy</subject><subject>Organic matter</subject><subject>Organic soils</subject><subject>Physicochemical processes</subject><subject>Physicochemical properties</subject><subject>Pollution</subject><subject>Principal components analysis</subject><subject>Risk assessment</subject><subject>Scientific imaging</subject><subject>Soil</subject><subject>Soil - chemistry</subject><subject>Soil contamination</subject><subject>Soil Pollutants - analysis</subject><subject>Soil pollution</subject><subject>Soil water</subject><subject>Soils</subject><subject>Spectrometry</subject><subject>Water analysis</subject><subject>Water Pollutants, Chemical - analysis</subject><subject>Water pollution</subject><subject>Water sampling</subject><issn>0167-6369</issn><issn>1573-2959</issn><issn>1573-2959</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2024</creationdate><recordtype>article</recordtype><recordid>eNp9kU2O1DAQhS0EYpqBC7BAltiwIOCfxI7ZjUb8SY1AYlhHFcdpPErs4HIEcxrWLDjFXAx39wASC1YlVX3vVakeIQ85e8YZ08-RM6V4xURdcclaXtW3yIY3WlbCNOY22TCudKWkMifkHuIlY8zo2twlJ9JI1UglN-T7RQLrkMaR5s-OLoD5BQVEh-jD7tDz8wI274klZheyh2m6ojl-85a6yc2lhXRMcaYQKPQQhhjcQGcfHI2B7lJcw_AVsksFGCjskrfrlNcEE8XoJ-oD_Vik29Uj_RBzxOufT-m76x9lQbxP7owwoXtwU0_Jp1cvL87fVNv3r9-en20rKxqVK9W3raxhtBLaEVjPBQyt0b3U5TuiboXU0DgzKAnOaGHLk3omtGUGtGi5kafkydF3SfHL6jB3s0frpgmCiyt2knPRKs60LOjjf9DLuKZQrjtQRmnB6kKJI2VTRExu7JbkZ0hXHWfdPr7uGF9XDuwO8XV70aMb67Wf3fBH8juvAsgjgGUUdi793f0f2180lKfF</recordid><startdate>20241101</startdate><enddate>20241101</enddate><creator>Silva-Gigante, M.</creator><creator>Hinojosa-Reyes, L.</creator><creator>Bazzan-Dessuy, M.</creator><creator>Rosas-Castor, J. 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L.</creator><general>Springer International Publishing</general><general>Springer Nature B.V</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QH</scope><scope>7QL</scope><scope>7SN</scope><scope>7ST</scope><scope>7T7</scope><scope>7TG</scope><scope>7TN</scope><scope>7U7</scope><scope>7UA</scope><scope>8FD</scope><scope>C1K</scope><scope>F1W</scope><scope>FR3</scope><scope>H97</scope><scope>K9.</scope><scope>KL.</scope><scope>L.G</scope><scope>M7N</scope><scope>P64</scope><scope>SOI</scope><scope>7X8</scope></search><sort><creationdate>20241101</creationdate><title>Traces of the past: assessing the impact of potentially toxic elements from an abandoned mine on groundwater and agricultural soil in San Luis Potosí, México</title><author>Silva-Gigante, M. ; Hinojosa-Reyes, L. ; Bazzan-Dessuy, M. ; Rosas-Castor, J. M. ; Torres-Gaytán, D. E. ; Quero-Jiménez, P. C. ; Caballero-Quintero, A. ; Guzmán-Mar, J. L.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c256t-6b8834afc3a8fa0b12ad897b37024248237a5e9d63ae972c573b027c09a728193</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2024</creationdate><topic>Abandoned mines</topic><topic>Adults</topic><topic>Agricultural land</topic><topic>Agriculture</topic><topic>Antimony</topic><topic>Antimony - analysis</topic><topic>Arsenic</topic><topic>Arsenic - analysis</topic><topic>Arsenopyrite</topic><topic>Atmospheric Protection/Air Quality Control/Air Pollution</topic><topic>Bioavailability</topic><topic>Cadmium</topic><topic>Cadmium - analysis</topic><topic>Cancer</topic><topic>Children</topic><topic>Contamination</topic><topic>Detection limits</topic><topic>Drinking water</topic><topic>Earth and Environmental Science</topic><topic>Ecology</topic><topic>Ecotoxicology</topic><topic>Environment</topic><topic>Environmental impact</topic><topic>Environmental Management</topic><topic>Environmental Monitoring</topic><topic>Fluorescence</topic><topic>Groundwater</topic><topic>Groundwater - chemistry</topic><topic>Groundwater mining</topic><topic>Health risks</topic><topic>Impact analysis</topic><topic>Inductively coupled plasma</topic><topic>Ingestion</topic><topic>Lead</topic><topic>Lead - analysis</topic><topic>Mercury</topic><topic>Mercury (metal)</topic><topic>Mercury - analysis</topic><topic>Metals, Heavy - analysis</topic><topic>Mexico</topic><topic>Mining</topic><topic>Monitoring/Environmental Analysis</topic><topic>Optical emission spectroscopy</topic><topic>Organic matter</topic><topic>Organic soils</topic><topic>Physicochemical processes</topic><topic>Physicochemical properties</topic><topic>Pollution</topic><topic>Principal components analysis</topic><topic>Risk assessment</topic><topic>Scientific imaging</topic><topic>Soil</topic><topic>Soil - chemistry</topic><topic>Soil contamination</topic><topic>Soil Pollutants - analysis</topic><topic>Soil pollution</topic><topic>Soil water</topic><topic>Soils</topic><topic>Spectrometry</topic><topic>Water analysis</topic><topic>Water Pollutants, Chemical - analysis</topic><topic>Water pollution</topic><topic>Water sampling</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Silva-Gigante, M.</creatorcontrib><creatorcontrib>Hinojosa-Reyes, L.</creatorcontrib><creatorcontrib>Bazzan-Dessuy, M.</creatorcontrib><creatorcontrib>Rosas-Castor, J. 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M.</au><au>Torres-Gaytán, D. E.</au><au>Quero-Jiménez, P. C.</au><au>Caballero-Quintero, A.</au><au>Guzmán-Mar, J. L.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Traces of the past: assessing the impact of potentially toxic elements from an abandoned mine on groundwater and agricultural soil in San Luis Potosí, México</atitle><jtitle>Environmental monitoring and assessment</jtitle><stitle>Environ Monit Assess</stitle><addtitle>Environ Monit Assess</addtitle><date>2024-11-01</date><risdate>2024</risdate><volume>196</volume><issue>11</issue><spage>1015</spage><pages>1015-</pages><artnum>1015</artnum><issn>0167-6369</issn><issn>1573-2959</issn><eissn>1573-2959</eissn><abstract>The study was conducted in Cerritos, San Luis Potosí, México, near the Guaxcama mine, focused on environmental contamination (groundwater and agricultural soil) from antimony (Sb), arsenic (As), lead (Pb), cadmium (Cd), and mercury (Hg). In March 2022, 20 agricultural soil and 16 groundwater samples were collected near the historically cinnabar (HgS)- and arsenopyrite (FeAsS)-rich Guaxcama mine. Hydride generation atomic fluorescence spectrometry (HG-AFS) for As, cold vapor atomic fluorescence spectrometry (CV-AFS) for Hg, and inductively coupled plasma optical emission spectrometry (ICP-OES) for Cd, Pb, and Sb were used for the determinations of potentially toxic elements (PTEs). While concentrations of Cd, Hg, Pb, and Sb in groundwater were below detection limits, As levels exhibited a range from 40.9 ± 1.4 to 576.0 ± 1.0 µg/L, exceeding permissible limits for drinking water (10 µg/L). In agricultural soil, As was between 7.67 ± 0.16 and 24.1 ± 0.4 µg/g, Hg ranged from 0.203 ± 0.018 to 2.33 ± 0.19 µg/g, Cd from 2.53 ± 0.90 to 2.78 ± 0.01 µg/g, and Pb from 11.7 ± 1.2 to 34.3 ± 4.1 µg/g. Only one study area surpassed the Mexican As soil limit of 22 µg/g. Sequential extraction (four-step BCR procedure) indicated significant As bioavailability in soil (fractions 1 and 2) ranging from 3.66 to 10.36%, heightening the risk of crop transfer, in contrast to the low bioavailability of Hg, showing that fractions 1, 2, and 3 were below the limit of quantification (LOQ). Crucial physicochemical parameters in soil, including nitrate levels, pH, and organic matter, were pivotal in understanding contamination dynamics. Principal component analysis highlighted the influence of elements like Fe and Ca on phytoavailable As, while Pb and Cd likely originated from a common source. Ecological risk assessments underscored the significant impact of pollution, primarily due to the concentrations of Cd and Hg. Non-cancer and cancer risks to residents through As poisoning via contaminated water ingestion also were found. The hazard index (HI) values varied between 4.0 and 82.2 for adults and children. The total incremental lifetime cancer risk (TILCAR) values for adults ranged from 7.75E − 04 to 1.06E − 02, whereas for children, the values were from 2.47E − 04 to 3.17E − 03.</abstract><cop>Cham</cop><pub>Springer International Publishing</pub><pmid>39365363</pmid><doi>10.1007/s10661-024-13081-4</doi></addata></record> |
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subjects | Abandoned mines Adults Agricultural land Agriculture Antimony Antimony - analysis Arsenic Arsenic - analysis Arsenopyrite Atmospheric Protection/Air Quality Control/Air Pollution Bioavailability Cadmium Cadmium - analysis Cancer Children Contamination Detection limits Drinking water Earth and Environmental Science Ecology Ecotoxicology Environment Environmental impact Environmental Management Environmental Monitoring Fluorescence Groundwater Groundwater - chemistry Groundwater mining Health risks Impact analysis Inductively coupled plasma Ingestion Lead Lead - analysis Mercury Mercury (metal) Mercury - analysis Metals, Heavy - analysis Mexico Mining Monitoring/Environmental Analysis Optical emission spectroscopy Organic matter Organic soils Physicochemical processes Physicochemical properties Pollution Principal components analysis Risk assessment Scientific imaging Soil Soil - chemistry Soil contamination Soil Pollutants - analysis Soil pollution Soil water Soils Spectrometry Water analysis Water Pollutants, Chemical - analysis Water pollution Water sampling |
title | Traces of the past: assessing the impact of potentially toxic elements from an abandoned mine on groundwater and agricultural soil in San Luis Potosí, México |
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