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Cesium-137 distribution in soil and Leccinum aurantiacum in a spruce-aspen forest ecosystem
The assessment of caesium-137 accumulation in parts of fungi fruiting bodies of Leccinum aurantiacum (Bull.) Gray in a mixed spruce-aspen forest on sod-podzolic soil was carried out. Average specific activity of cesium-137 for caps is 1814±112 Bq/kg and for stems 873±73 Bq/kg. It was found that the...
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Published in: | E3S web of conferences 2023-01, Vol.390, p.4004 |
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description | The assessment of caesium-137 accumulation in parts of fungi fruiting bodies of Leccinum aurantiacum (Bull.) Gray in a mixed spruce-aspen forest on sod-podzolic soil was carried out. Average specific activity of cesium-137 for caps is 1814±112 Bq/kg and for stems 873±73 Bq/kg. It was found that the specific activity of cesium-137 does not exceed the permissible values, but significantly differs between the cap and stem of fruit bodies. The coefficients of cesium-137 accumulation from soil vary for caps from 4.6 to 6.1 and for stems from 1.7 to 2.8. High specific activity of cesium-137 in aspen leaf fall 289±27 Bq/kg and litter 339±23 Bq/kg compared to the underlying soil horizons was noted. |
doi_str_mv | 10.1051/e3sconf/202339004004 |
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Gray in a mixed spruce-aspen forest on sod-podzolic soil was carried out. Average specific activity of cesium-137 for caps is 1814±112 Bq/kg and for stems 873±73 Bq/kg. It was found that the specific activity of cesium-137 does not exceed the permissible values, but significantly differs between the cap and stem of fruit bodies. The coefficients of cesium-137 accumulation from soil vary for caps from 4.6 to 6.1 and for stems from 1.7 to 2.8. High specific activity of cesium-137 in aspen leaf fall 289±27 Bq/kg and litter 339±23 Bq/kg compared to the underlying soil horizons was noted.</description><identifier>ISSN: 2267-1242</identifier><identifier>ISSN: 2555-0403</identifier><identifier>EISSN: 2267-1242</identifier><identifier>DOI: 10.1051/e3sconf/202339004004</identifier><language>eng</language><publisher>Les Ulis: EDP Sciences</publisher><subject>Accumulation ; Cesium ; Cesium 137 ; Cesium radioisotopes ; Forest ecosystems ; Fruit bodies ; Leaf fall ; Soil horizons ; Soils ; Terrestrial ecosystems</subject><ispartof>E3S web of conferences, 2023-01, Vol.390, p.4004</ispartof><rights>2023. This work is licensed under https://creativecommons.org/licenses/by/4.0/ (the “License”). 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Gray in a mixed spruce-aspen forest on sod-podzolic soil was carried out. Average specific activity of cesium-137 for caps is 1814±112 Bq/kg and for stems 873±73 Bq/kg. It was found that the specific activity of cesium-137 does not exceed the permissible values, but significantly differs between the cap and stem of fruit bodies. The coefficients of cesium-137 accumulation from soil vary for caps from 4.6 to 6.1 and for stems from 1.7 to 2.8. High specific activity of cesium-137 in aspen leaf fall 289±27 Bq/kg and litter 339±23 Bq/kg compared to the underlying soil horizons was noted.</description><subject>Accumulation</subject><subject>Cesium</subject><subject>Cesium 137</subject><subject>Cesium radioisotopes</subject><subject>Forest ecosystems</subject><subject>Fruit bodies</subject><subject>Leaf fall</subject><subject>Soil horizons</subject><subject>Soils</subject><subject>Terrestrial ecosystems</subject><issn>2267-1242</issn><issn>2555-0403</issn><issn>2267-1242</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2023</creationdate><recordtype>article</recordtype><sourceid>PIMPY</sourceid><sourceid>DOA</sourceid><recordid>eNpNUU1LAzEQDaJgqf0HHgKeVydf-3GU4keh4EVPHkKaTCSlu6nJ7qH_3miLFGaYx_DmzQyPkFsG9wwUe0CRbRz8AwcuRAcgS1yQGed1UzEu-eUZviaLnLcAwLhqJcgZ-VxiDlNfMdFQF_KYwmYaQxxoGGiOYUfN4OgarQ3D1FMzJTOMwdiCC8HQvE-TxcrkPQ7Ux4R5pGhjPuQR-xty5c0u4-JU5-Tj-el9-Vqt315Wy8d1ZblSsrLWGFeDLwcpYMLJmlneMus78AjgvZKylq5BycAidEp612xsC20DKBSIOVkddV00W71PoTfpoKMJ-q8R05c2aQx2h7pB3na4EWVOSsdY10nBbcsEb53vSp2Tu6PWPsXvqbyjt3FKQzlf85YzoUp2hSWPLJtizgn9_1YG-tcVfXJFn7sifgCl5H9n</recordid><startdate>20230101</startdate><enddate>20230101</enddate><creator>Ivanov, Dmitriy M.</creator><creator>Ivanov, Evgeniy D.</creator><general>EDP Sciences</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7ST</scope><scope>8FD</scope><scope>8FE</scope><scope>8FG</scope><scope>ABJCF</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BGLVJ</scope><scope>BHPHI</scope><scope>BKSAR</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FR3</scope><scope>GNUQQ</scope><scope>H8D</scope><scope>HCIFZ</scope><scope>KR7</scope><scope>L6V</scope><scope>L7M</scope><scope>M7S</scope><scope>PATMY</scope><scope>PCBAR</scope><scope>PIMPY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PRINS</scope><scope>PTHSS</scope><scope>PYCSY</scope><scope>SOI</scope><scope>DOA</scope></search><sort><creationdate>20230101</creationdate><title>Cesium-137 distribution in soil and Leccinum aurantiacum in a spruce-aspen forest ecosystem</title><author>Ivanov, Dmitriy M. ; 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Gray in a mixed spruce-aspen forest on sod-podzolic soil was carried out. Average specific activity of cesium-137 for caps is 1814±112 Bq/kg and for stems 873±73 Bq/kg. It was found that the specific activity of cesium-137 does not exceed the permissible values, but significantly differs between the cap and stem of fruit bodies. The coefficients of cesium-137 accumulation from soil vary for caps from 4.6 to 6.1 and for stems from 1.7 to 2.8. High specific activity of cesium-137 in aspen leaf fall 289±27 Bq/kg and litter 339±23 Bq/kg compared to the underlying soil horizons was noted.</abstract><cop>Les Ulis</cop><pub>EDP Sciences</pub><doi>10.1051/e3sconf/202339004004</doi><oa>free_for_read</oa></addata></record> |
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subjects | Accumulation Cesium Cesium 137 Cesium radioisotopes Forest ecosystems Fruit bodies Leaf fall Soil horizons Soils Terrestrial ecosystems |
title | Cesium-137 distribution in soil and Leccinum aurantiacum in a spruce-aspen forest ecosystem |
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