Research progress on the content and distribution of rare earth elements in rivers and lakes in China
This study reviewed the content and distribution of rare earth elements (REE) in rivers and lakes in China based on the online literature. The sequence distribution of REE presented the decreasing trends in the order: of Ce > La > Nd > Pr > Sm > Gb > Dy>Er > Yb > Eu > L...
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Veröffentlicht in: | Marine pollution bulletin 2023-06, Vol.191, p.114916-114916, Article 114916 |
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description | This study reviewed the content and distribution of rare earth elements (REE) in rivers and lakes in China based on the online literature. The sequence distribution of REE presented the decreasing trends in the order: of Ce > La > Nd > Pr > Sm > Gb > Dy>Er > Yb > Eu > Lu > Ho > Tb > Tm in rivers water. Pearl River and the Jiulong River constitute a significant sediments REE reservoir with an average value mean of 229.6 mg/kg and 266.86 mg/kg, respectively; both have higher concentrations than the global river average (174.8 mg/kg) and higher than the local soil background (Chinese soil background). The Liaohe River is one of China's most polluted rivers, with REE distribution ranging from 106.61 to 174.71 g/L (average 144.59 g/L in water). The total concentrations of dissolved REE in rivers near REE mining areas in China are higher than in other rivers. Increasing anthropogenic inputs to natural systems may permanently alter the natural signatures of REE. The distribution characteristics of REE in Chinese lakes (sediments) varied greatly, and the mean enrichment factor (EF) was sorted as follows: Ce > La > Nd > Pr > Sm > Gd > Dy>Er > Yb > Eu > Ho > Tb > Tm > Lu, where Ce was the most abundant followed by La, Nd, and Pr, and these four elements account for 85.39 % of the total concentration of REE. The REE in the sediments obtained from Poyang Lake and Dongting Lake had an average concentration respectively of 254.0 μg/g and 197.95 μg/g; both are considerably higher than the average upper continental crust (146.4 μg/g) and higher than in other lakes in China and around the world. The distribution and accumulation of LREE in most lake sediments result from the joint action of human activities and natural processes. It concluded that mining tailings were the primary cause of REE pollution in sediments, and industrial and agricultural activities are mainly responsible for water contamination.
[Display omitted]
•REE are recognized as emerging micro-pollutants in aquatic ecosystems.•Multiple environmental problems resulted from the widespread exploitation of REE.•The REE in Chinese lakes varied greatly; Ce La, Nd, and Pr were the most abundant.•The distribution of REE in water results from human activities and natural processes. |
doi_str_mv | 10.1016/j.marpolbul.2023.114916 |
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[Display omitted]
•REE are recognized as emerging micro-pollutants in aquatic ecosystems.•Multiple environmental problems resulted from the widespread exploitation of REE.•The REE in Chinese lakes varied greatly; Ce La, Nd, and Pr were the most abundant.•The distribution of REE in water results from human activities and natural processes.</description><identifier>ISSN: 0025-326X</identifier><identifier>EISSN: 1879-3363</identifier><identifier>DOI: 10.1016/j.marpolbul.2023.114916</identifier><identifier>PMID: 37058831</identifier><language>eng</language><publisher>England: Elsevier Ltd</publisher><subject>China ; Distribution ; Environmental Monitoring ; Humans ; Lakes ; Metals, Rare Earth - analysis ; Rare earth elements (REE) ; Rivers ; Soil ; Water</subject><ispartof>Marine pollution bulletin, 2023-06, Vol.191, p.114916-114916, Article 114916</ispartof><rights>2023 Elsevier Ltd</rights><rights>Copyright © 2023 Elsevier Ltd. All rights reserved.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c371t-40085f3ad3d1fa6c3851df366ad0daeaee315260364bf7004769d9dac3d90ba43</citedby><cites>FETCH-LOGICAL-c371t-40085f3ad3d1fa6c3851df366ad0daeaee315260364bf7004769d9dac3d90ba43</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://www.sciencedirect.com/science/article/pii/S0025326X23003478$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,776,780,3537,27901,27902,65306</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/37058831$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Traore, Mory</creatorcontrib><creatorcontrib>He, Yafei</creatorcontrib><creatorcontrib>Wang, Yiwen</creatorcontrib><creatorcontrib>Gong, Aijun</creatorcontrib><creatorcontrib>Qiu, Lina</creatorcontrib><creatorcontrib>Bai, Yuzhen</creatorcontrib><creatorcontrib>Liu, Yang</creatorcontrib><creatorcontrib>Zhang, Min</creatorcontrib><creatorcontrib>Chen, Yifan</creatorcontrib><creatorcontrib>Huang, Xinyu</creatorcontrib><title>Research progress on the content and distribution of rare earth elements in rivers and lakes in China</title><title>Marine pollution bulletin</title><addtitle>Mar Pollut Bull</addtitle><description>This study reviewed the content and distribution of rare earth elements (REE) in rivers and lakes in China based on the online literature. The sequence distribution of REE presented the decreasing trends in the order: of Ce > La > Nd > Pr > Sm > Gb > Dy>Er > Yb > Eu > Lu > Ho > Tb > Tm in rivers water. Pearl River and the Jiulong River constitute a significant sediments REE reservoir with an average value mean of 229.6 mg/kg and 266.86 mg/kg, respectively; both have higher concentrations than the global river average (174.8 mg/kg) and higher than the local soil background (Chinese soil background). The Liaohe River is one of China's most polluted rivers, with REE distribution ranging from 106.61 to 174.71 g/L (average 144.59 g/L in water). The total concentrations of dissolved REE in rivers near REE mining areas in China are higher than in other rivers. Increasing anthropogenic inputs to natural systems may permanently alter the natural signatures of REE. The distribution characteristics of REE in Chinese lakes (sediments) varied greatly, and the mean enrichment factor (EF) was sorted as follows: Ce > La > Nd > Pr > Sm > Gd > Dy>Er > Yb > Eu > Ho > Tb > Tm > Lu, where Ce was the most abundant followed by La, Nd, and Pr, and these four elements account for 85.39 % of the total concentration of REE. The REE in the sediments obtained from Poyang Lake and Dongting Lake had an average concentration respectively of 254.0 μg/g and 197.95 μg/g; both are considerably higher than the average upper continental crust (146.4 μg/g) and higher than in other lakes in China and around the world. The distribution and accumulation of LREE in most lake sediments result from the joint action of human activities and natural processes. It concluded that mining tailings were the primary cause of REE pollution in sediments, and industrial and agricultural activities are mainly responsible for water contamination.
[Display omitted]
•REE are recognized as emerging micro-pollutants in aquatic ecosystems.•Multiple environmental problems resulted from the widespread exploitation of REE.•The REE in Chinese lakes varied greatly; Ce La, Nd, and Pr were the most abundant.•The distribution of REE in water results from human activities and natural processes.</description><subject>China</subject><subject>Distribution</subject><subject>Environmental Monitoring</subject><subject>Humans</subject><subject>Lakes</subject><subject>Metals, Rare Earth - analysis</subject><subject>Rare earth elements (REE)</subject><subject>Rivers</subject><subject>Soil</subject><subject>Water</subject><issn>0025-326X</issn><issn>1879-3363</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2023</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqFkE1LxDAQhoMoun78Bc3RS9dJ0ybtURa_QBBEwVtIk6mbtduuSSr4781-6NXTwMzzzjAPIRcMpgyYuFpMl9qvhq4Zu2kOOZ8yVtRM7JEJq2SdcS74PpkA5GXGc_F2RI5DWACAzCU7JEdcQllVnE0IPmNA7c2crvzw7jEEOvQ0zpGaoY_YR6p7S60L0btmjC4Nh5Z67ZGmWJxT7HCZsEBdT737Qh82iU5_4KY3m7ten5KDVncBz3b1hLze3rzM7rPHp7uH2fVjZrhkMSsAqrLl2nLLWi0Mr0pmWy6EtmA1akTOylwAF0XTSoBCitrWVhtua2h0wU_I5XZveuZzxBDV0gWDXad7HMag8gpYLeuigoTKLWr8EILHVq28S1K_FQO1dqwW6s-xWjtWW8cpeb47MjZLtH-5X6kJuN4CmF79cuhVMA57g9Z5NFHZwf175AfD5pLi</recordid><startdate>202306</startdate><enddate>202306</enddate><creator>Traore, Mory</creator><creator>He, Yafei</creator><creator>Wang, Yiwen</creator><creator>Gong, Aijun</creator><creator>Qiu, Lina</creator><creator>Bai, Yuzhen</creator><creator>Liu, Yang</creator><creator>Zhang, Min</creator><creator>Chen, Yifan</creator><creator>Huang, Xinyu</creator><general>Elsevier Ltd</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>7X8</scope></search><sort><creationdate>202306</creationdate><title>Research progress on the content and distribution of rare earth elements in rivers and lakes in China</title><author>Traore, Mory ; He, Yafei ; Wang, Yiwen ; Gong, Aijun ; Qiu, Lina ; Bai, Yuzhen ; Liu, Yang ; Zhang, Min ; Chen, Yifan ; Huang, Xinyu</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c371t-40085f3ad3d1fa6c3851df366ad0daeaee315260364bf7004769d9dac3d90ba43</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2023</creationdate><topic>China</topic><topic>Distribution</topic><topic>Environmental Monitoring</topic><topic>Humans</topic><topic>Lakes</topic><topic>Metals, Rare Earth - analysis</topic><topic>Rare earth elements (REE)</topic><topic>Rivers</topic><topic>Soil</topic><topic>Water</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Traore, Mory</creatorcontrib><creatorcontrib>He, Yafei</creatorcontrib><creatorcontrib>Wang, Yiwen</creatorcontrib><creatorcontrib>Gong, Aijun</creatorcontrib><creatorcontrib>Qiu, Lina</creatorcontrib><creatorcontrib>Bai, Yuzhen</creatorcontrib><creatorcontrib>Liu, Yang</creatorcontrib><creatorcontrib>Zhang, Min</creatorcontrib><creatorcontrib>Chen, Yifan</creatorcontrib><creatorcontrib>Huang, Xinyu</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>MEDLINE - Academic</collection><jtitle>Marine pollution bulletin</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Traore, Mory</au><au>He, Yafei</au><au>Wang, Yiwen</au><au>Gong, Aijun</au><au>Qiu, Lina</au><au>Bai, Yuzhen</au><au>Liu, Yang</au><au>Zhang, Min</au><au>Chen, Yifan</au><au>Huang, Xinyu</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Research progress on the content and distribution of rare earth elements in rivers and lakes in China</atitle><jtitle>Marine pollution bulletin</jtitle><addtitle>Mar Pollut Bull</addtitle><date>2023-06</date><risdate>2023</risdate><volume>191</volume><spage>114916</spage><epage>114916</epage><pages>114916-114916</pages><artnum>114916</artnum><issn>0025-326X</issn><eissn>1879-3363</eissn><abstract>This study reviewed the content and distribution of rare earth elements (REE) in rivers and lakes in China based on the online literature. The sequence distribution of REE presented the decreasing trends in the order: of Ce > La > Nd > Pr > Sm > Gb > Dy>Er > Yb > Eu > Lu > Ho > Tb > Tm in rivers water. Pearl River and the Jiulong River constitute a significant sediments REE reservoir with an average value mean of 229.6 mg/kg and 266.86 mg/kg, respectively; both have higher concentrations than the global river average (174.8 mg/kg) and higher than the local soil background (Chinese soil background). The Liaohe River is one of China's most polluted rivers, with REE distribution ranging from 106.61 to 174.71 g/L (average 144.59 g/L in water). The total concentrations of dissolved REE in rivers near REE mining areas in China are higher than in other rivers. Increasing anthropogenic inputs to natural systems may permanently alter the natural signatures of REE. The distribution characteristics of REE in Chinese lakes (sediments) varied greatly, and the mean enrichment factor (EF) was sorted as follows: Ce > La > Nd > Pr > Sm > Gd > Dy>Er > Yb > Eu > Ho > Tb > Tm > Lu, where Ce was the most abundant followed by La, Nd, and Pr, and these four elements account for 85.39 % of the total concentration of REE. The REE in the sediments obtained from Poyang Lake and Dongting Lake had an average concentration respectively of 254.0 μg/g and 197.95 μg/g; both are considerably higher than the average upper continental crust (146.4 μg/g) and higher than in other lakes in China and around the world. The distribution and accumulation of LREE in most lake sediments result from the joint action of human activities and natural processes. It concluded that mining tailings were the primary cause of REE pollution in sediments, and industrial and agricultural activities are mainly responsible for water contamination.
[Display omitted]
•REE are recognized as emerging micro-pollutants in aquatic ecosystems.•Multiple environmental problems resulted from the widespread exploitation of REE.•The REE in Chinese lakes varied greatly; Ce La, Nd, and Pr were the most abundant.•The distribution of REE in water results from human activities and natural processes.</abstract><cop>England</cop><pub>Elsevier Ltd</pub><pmid>37058831</pmid><doi>10.1016/j.marpolbul.2023.114916</doi><tpages>1</tpages></addata></record> |
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subjects | China Distribution Environmental Monitoring Humans Lakes Metals, Rare Earth - analysis Rare earth elements (REE) Rivers Soil Water |
title | Research progress on the content and distribution of rare earth elements in rivers and lakes in China |
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