Using Radionuclides from Atmospheric Deposition in the Study of Their Geochemical Migration in Soils: Review
This article provides an overview of the results of long-term studies of the migration of radionuclides in the composition of lysimetric waters (leachates). It considers peculiarities of lysimeter-based studies at various stages of advancement in radioecology. It is noted that, for a long time, the...
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description | This article provides an overview of the results of long-term studies of the migration of radionuclides in the composition of lysimetric waters (leachates). It considers peculiarities of lysimeter-based studies at various stages of advancement in radioecology. It is noted that, for a long time, the use of lysimeters was limited to a low level of radionuclides in soil solutions; the studies gained momentum after the Chernobyl deposition (1986). Release of radionuclides to leachates is shown to be the greatest in the forest and coniferous phytocenoses, in particular, and the least in meadows and agrophytocenoses. The intensity of radionuclide migration in the leachates is the maximum during the initial period after atmospheric deposition in the long-term dynamics and during summer in the seasonal dynamics. Gravity flow was assessed in redistribution of radionuclides across the soil profile. The annual flux with vertical subsurface flow varies depending on edaphic and climatic conditions; time elapsed after the deposition; and thickness and depth of the layer. The annual flux ranges from tenths of a percent to a low percentage of the forest floor and from hundredths to tenths of a percent from a 0- to 20-cm layer of the total radionuclide inventory in these layers. The relative flux of
90
Sr significantly surpasses that of
137
Cs. From 70 to 90% of radionuclides (
90
Sr,
137
Сs,
238
Pu,
239+240
Pu, and
241
Am) are present in soil solution in the form of radionuclide–organic compounds of various molecular weights. |
doi_str_mv | 10.3103/S0147687422040123 |
format | Article |
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90
Sr significantly surpasses that of
137
Cs. From 70 to 90% of radionuclides (
90
Sr,
137
Сs,
238
Pu,
239+240
Pu, and
241
Am) are present in soil solution in the form of radionuclide–organic compounds of various molecular weights.</description><identifier>ISSN: 0147-6874</identifier><identifier>EISSN: 1934-7928</identifier><identifier>DOI: 10.3103/S0147687422040123</identifier><language>eng</language><publisher>Moscow: Pleiades Publishing</publisher><subject>atmospheric deposition ; bulls ; Cesium 137 ; Cesium isotopes ; Cesium radioisotopes ; Climatic conditions ; Coniferous forests ; Deposition ; Earth and Environmental Science ; Earth Sciences ; Fluctuations ; Forest floor ; forest litter ; forests ; gravity ; Gravity flow ; Historical Geology ; inventories ; Leachates ; Low level ; Lysimeters ; Meadows ; Organic compounds ; Paleontology ; Plant communities ; Radioecology ; Radioisotopes ; Seasonal variations ; Soil profiles ; Soil properties ; Soil solution ; Strontium ; Strontium 90 ; Strontium radioisotopes ; subsurface flow ; summer ; Ukraine</subject><ispartof>Moscow University soil science bulletin, 2022-12, Vol.77 (4), p.213-217</ispartof><rights>Allerton Press, Inc. 2022. ISSN 0147-6874, Moscow University Soil Science Bulletin, 2022, Vol. 77, No. 4, pp. 213–217. © Allerton Press, Inc., 2022. Russian Text © The Author(s), 2022, published in Vestnik Moskovskogo Universiteta, Seriya 17: Pochvovedenie, 2022, No. 4, pp. 5–10.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c1943-ffc0a82f666e38b2dafa97b0be551fa9db55b9bdfea2f7d1b74d64d4a27a5efc3</citedby><cites>FETCH-LOGICAL-c1943-ffc0a82f666e38b2dafa97b0be551fa9db55b9bdfea2f7d1b74d64d4a27a5efc3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://link.springer.com/content/pdf/10.3103/S0147687422040123$$EPDF$$P50$$Gspringer$$H</linktopdf><linktohtml>$$Uhttps://link.springer.com/10.3103/S0147687422040123$$EHTML$$P50$$Gspringer$$H</linktohtml><link.rule.ids>314,776,780,27901,27902,41464,42533,51294</link.rule.ids></links><search><creatorcontrib>Shcheglov, A. I.</creatorcontrib><creatorcontrib>Tsvetnova, O. B.</creatorcontrib><creatorcontrib>Agapkina, G. I.</creatorcontrib><creatorcontrib>Klyashtorin, A. L.</creatorcontrib><title>Using Radionuclides from Atmospheric Deposition in the Study of Their Geochemical Migration in Soils: Review</title><title>Moscow University soil science bulletin</title><addtitle>Moscow Univ. Soil Sci. Bull</addtitle><description>This article provides an overview of the results of long-term studies of the migration of radionuclides in the composition of lysimetric waters (leachates). It considers peculiarities of lysimeter-based studies at various stages of advancement in radioecology. It is noted that, for a long time, the use of lysimeters was limited to a low level of radionuclides in soil solutions; the studies gained momentum after the Chernobyl deposition (1986). Release of radionuclides to leachates is shown to be the greatest in the forest and coniferous phytocenoses, in particular, and the least in meadows and agrophytocenoses. The intensity of radionuclide migration in the leachates is the maximum during the initial period after atmospheric deposition in the long-term dynamics and during summer in the seasonal dynamics. Gravity flow was assessed in redistribution of radionuclides across the soil profile. The annual flux with vertical subsurface flow varies depending on edaphic and climatic conditions; time elapsed after the deposition; and thickness and depth of the layer. The annual flux ranges from tenths of a percent to a low percentage of the forest floor and from hundredths to tenths of a percent from a 0- to 20-cm layer of the total radionuclide inventory in these layers. The relative flux of
90
Sr significantly surpasses that of
137
Cs. From 70 to 90% of radionuclides (
90
Sr,
137
Сs,
238
Pu,
239+240
Pu, and
241
Am) are present in soil solution in the form of radionuclide–organic compounds of various molecular weights.</description><subject>atmospheric deposition</subject><subject>bulls</subject><subject>Cesium 137</subject><subject>Cesium isotopes</subject><subject>Cesium radioisotopes</subject><subject>Climatic conditions</subject><subject>Coniferous forests</subject><subject>Deposition</subject><subject>Earth and Environmental Science</subject><subject>Earth Sciences</subject><subject>Fluctuations</subject><subject>Forest floor</subject><subject>forest litter</subject><subject>forests</subject><subject>gravity</subject><subject>Gravity flow</subject><subject>Historical Geology</subject><subject>inventories</subject><subject>Leachates</subject><subject>Low level</subject><subject>Lysimeters</subject><subject>Meadows</subject><subject>Organic compounds</subject><subject>Paleontology</subject><subject>Plant communities</subject><subject>Radioecology</subject><subject>Radioisotopes</subject><subject>Seasonal variations</subject><subject>Soil profiles</subject><subject>Soil properties</subject><subject>Soil solution</subject><subject>Strontium</subject><subject>Strontium 90</subject><subject>Strontium radioisotopes</subject><subject>subsurface flow</subject><subject>summer</subject><subject>Ukraine</subject><issn>0147-6874</issn><issn>1934-7928</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2022</creationdate><recordtype>article</recordtype><recordid>eNp10MtKxDAUBuAgCo6XB3AXcOOmmlub1p14B0VwZtYlTU5mIm0zJq3i25thFEFxlQPn-w_hR-iIklNOCT-bEipkUUrBGBGEMr6FJrTiIpMVK7fRZL3O1vtdtBfjCyF5wQSZoHYeXb_Az8o434-6dQYitsF3-GLofFwtITiNr2DloxsSwa7HwxLwdBjNB_YWz5bgAr4Fr5fQOa1a_OgWQX3bqXdtPMfP8Obg_QDtWNVGOPx699H85np2eZc9PN3eX148ZJpWgmfWaqJKZouiAF42zCirKtmQBvKcptE0ed5UjbGgmJWGNlKYQhihmFQ5WM330cnm7ir41xHiUHcuamhb1YMfY83KUhYs1VUmevyLvvgx9Ol3dQJUEl4WPCm6UTr4GAPYehVcp8JHTUm97r_-03_KsE0mJtsvIPxc_j_0CT-aiIA</recordid><startdate>20221201</startdate><enddate>20221201</enddate><creator>Shcheglov, A. I.</creator><creator>Tsvetnova, O. B.</creator><creator>Agapkina, G. I.</creator><creator>Klyashtorin, A. L.</creator><general>Pleiades Publishing</general><general>Springer Nature B.V</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7UA</scope><scope>C1K</scope><scope>7S9</scope><scope>L.6</scope></search><sort><creationdate>20221201</creationdate><title>Using Radionuclides from Atmospheric Deposition in the Study of Their Geochemical Migration in Soils: Review</title><author>Shcheglov, A. I. ; Tsvetnova, O. B. ; Agapkina, G. I. ; Klyashtorin, A. L.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c1943-ffc0a82f666e38b2dafa97b0be551fa9db55b9bdfea2f7d1b74d64d4a27a5efc3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2022</creationdate><topic>atmospheric deposition</topic><topic>bulls</topic><topic>Cesium 137</topic><topic>Cesium isotopes</topic><topic>Cesium radioisotopes</topic><topic>Climatic conditions</topic><topic>Coniferous forests</topic><topic>Deposition</topic><topic>Earth and Environmental Science</topic><topic>Earth Sciences</topic><topic>Fluctuations</topic><topic>Forest floor</topic><topic>forest litter</topic><topic>forests</topic><topic>gravity</topic><topic>Gravity flow</topic><topic>Historical Geology</topic><topic>inventories</topic><topic>Leachates</topic><topic>Low level</topic><topic>Lysimeters</topic><topic>Meadows</topic><topic>Organic compounds</topic><topic>Paleontology</topic><topic>Plant communities</topic><topic>Radioecology</topic><topic>Radioisotopes</topic><topic>Seasonal variations</topic><topic>Soil profiles</topic><topic>Soil properties</topic><topic>Soil solution</topic><topic>Strontium</topic><topic>Strontium 90</topic><topic>Strontium radioisotopes</topic><topic>subsurface flow</topic><topic>summer</topic><topic>Ukraine</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Shcheglov, A. I.</creatorcontrib><creatorcontrib>Tsvetnova, O. B.</creatorcontrib><creatorcontrib>Agapkina, G. I.</creatorcontrib><creatorcontrib>Klyashtorin, A. L.</creatorcontrib><collection>CrossRef</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>AGRICOLA</collection><collection>AGRICOLA - Academic</collection><jtitle>Moscow University soil science bulletin</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Shcheglov, A. I.</au><au>Tsvetnova, O. B.</au><au>Agapkina, G. I.</au><au>Klyashtorin, A. L.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Using Radionuclides from Atmospheric Deposition in the Study of Their Geochemical Migration in Soils: Review</atitle><jtitle>Moscow University soil science bulletin</jtitle><stitle>Moscow Univ. Soil Sci. Bull</stitle><date>2022-12-01</date><risdate>2022</risdate><volume>77</volume><issue>4</issue><spage>213</spage><epage>217</epage><pages>213-217</pages><issn>0147-6874</issn><eissn>1934-7928</eissn><abstract>This article provides an overview of the results of long-term studies of the migration of radionuclides in the composition of lysimetric waters (leachates). It considers peculiarities of lysimeter-based studies at various stages of advancement in radioecology. It is noted that, for a long time, the use of lysimeters was limited to a low level of radionuclides in soil solutions; the studies gained momentum after the Chernobyl deposition (1986). Release of radionuclides to leachates is shown to be the greatest in the forest and coniferous phytocenoses, in particular, and the least in meadows and agrophytocenoses. The intensity of radionuclide migration in the leachates is the maximum during the initial period after atmospheric deposition in the long-term dynamics and during summer in the seasonal dynamics. Gravity flow was assessed in redistribution of radionuclides across the soil profile. The annual flux with vertical subsurface flow varies depending on edaphic and climatic conditions; time elapsed after the deposition; and thickness and depth of the layer. The annual flux ranges from tenths of a percent to a low percentage of the forest floor and from hundredths to tenths of a percent from a 0- to 20-cm layer of the total radionuclide inventory in these layers. The relative flux of
90
Sr significantly surpasses that of
137
Cs. From 70 to 90% of radionuclides (
90
Sr,
137
Сs,
238
Pu,
239+240
Pu, and
241
Am) are present in soil solution in the form of radionuclide–organic compounds of various molecular weights.</abstract><cop>Moscow</cop><pub>Pleiades Publishing</pub><doi>10.3103/S0147687422040123</doi><tpages>5</tpages></addata></record> |
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subjects | atmospheric deposition bulls Cesium 137 Cesium isotopes Cesium radioisotopes Climatic conditions Coniferous forests Deposition Earth and Environmental Science Earth Sciences Fluctuations Forest floor forest litter forests gravity Gravity flow Historical Geology inventories Leachates Low level Lysimeters Meadows Organic compounds Paleontology Plant communities Radioecology Radioisotopes Seasonal variations Soil profiles Soil properties Soil solution Strontium Strontium 90 Strontium radioisotopes subsurface flow summer Ukraine |
title | Using Radionuclides from Atmospheric Deposition in the Study of Their Geochemical Migration in Soils: Review |
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