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Effect of Cd-containing wood ash on the microflora of coniferous forest humus
Abstract The use of wood ash in forestry has been questioned because the cadmium (Cd) concentration of ash, which varies between 1 and 20 mg kg−1 ash, exceeds the level allowed for fertilizers (3 mg kg−1) used in agriculture. To investigate the combined and separated effects of Cd and ash on the for...
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Published in: | FEMS microbiology ecology 2000-04, Vol.32 (1), p.43-51 |
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creator | Fritze, Hannu Perkiömäki, Jonna Saarela, Ulla Katainen, Riikka Tikka, Päivi Yrjälä, Kim Karp, Matti Haimi, Jari Romantschuk, Martin |
description | Abstract
The use of wood ash in forestry has been questioned because the cadmium (Cd) concentration of ash, which varies between 1 and 20 mg kg−1 ash, exceeds the level allowed for fertilizers (3 mg kg−1) used in agriculture. To investigate the combined and separated effects of Cd and ash on the forest humus microflora, pumice or wood ash, spiked with a water-soluble (CdCl2) or -insoluble (CdO) form of Cd at three levels (0, 400 and 1000 mg kg−1), were applied at a fertilization level of 5000 kg ha−1 in a laboratory microcosm study. The trial consisted of 60 microcosms (five replications per treatment), which were incubated in darkness at +20°C and a constant relative air humidity of 60%. After two months the humus in the microcosms was sampled. Analyses of CO2 evolution to measure the overall microbial activity and of phospholipid fatty acid (PLFA) pattern to measure microbial community structure were performed. The substrate-use patterns of Biolog EcoPlates were analyzed as a measure of bacterial functionality. Finally the bacterial 3H-thymidine incorporation in the presence of different concentrations of Cd and the number of colony forming units (cfu) of bacteria on nutrient agar in the presence of 0, 5 and 20 mg Cd l−1 agar were applied to measure Cd tolerance. The use of pumice (pH of humus under the pumice 4.0) did not induce any changes in the above variables compared to two untreated microcosms (humus pH 3.9). Pumice was therefore used to distribute the Cd evenly over the humus surface in order to estimate the possible effect of Cd without ash (pH of humus under the ash 7.0). The application of ash increased the microbial activity, changed the PLFA and substrate-use patterns and increased cfu compared to the humus under pumice. The form and level of Cd in the ash had no further effect on this result. In the humus under pumice the level, but not the form of Cd decreased the microbial activity and changed the PLFA pattern compared to the unspiked pumice. None of the treatments induced bacterial tolerance to Cd. Ash thus protected the humus microflora from the harmful effects of Cd. |
doi_str_mv | 10.1111/j.1574-6941.2000.tb00697.x |
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The use of wood ash in forestry has been questioned because the cadmium (Cd) concentration of ash, which varies between 1 and 20 mg kg−1 ash, exceeds the level allowed for fertilizers (3 mg kg−1) used in agriculture. To investigate the combined and separated effects of Cd and ash on the forest humus microflora, pumice or wood ash, spiked with a water-soluble (CdCl2) or -insoluble (CdO) form of Cd at three levels (0, 400 and 1000 mg kg−1), were applied at a fertilization level of 5000 kg ha−1 in a laboratory microcosm study. The trial consisted of 60 microcosms (five replications per treatment), which were incubated in darkness at +20°C and a constant relative air humidity of 60%. After two months the humus in the microcosms was sampled. Analyses of CO2 evolution to measure the overall microbial activity and of phospholipid fatty acid (PLFA) pattern to measure microbial community structure were performed. The substrate-use patterns of Biolog EcoPlates were analyzed as a measure of bacterial functionality. Finally the bacterial 3H-thymidine incorporation in the presence of different concentrations of Cd and the number of colony forming units (cfu) of bacteria on nutrient agar in the presence of 0, 5 and 20 mg Cd l−1 agar were applied to measure Cd tolerance. The use of pumice (pH of humus under the pumice 4.0) did not induce any changes in the above variables compared to two untreated microcosms (humus pH 3.9). Pumice was therefore used to distribute the Cd evenly over the humus surface in order to estimate the possible effect of Cd without ash (pH of humus under the ash 7.0). The application of ash increased the microbial activity, changed the PLFA and substrate-use patterns and increased cfu compared to the humus under pumice. The form and level of Cd in the ash had no further effect on this result. In the humus under pumice the level, but not the form of Cd decreased the microbial activity and changed the PLFA pattern compared to the unspiked pumice. None of the treatments induced bacterial tolerance to Cd. Ash thus protected the humus microflora from the harmful effects of Cd.</description><identifier>ISSN: 0168-6496</identifier><identifier>EISSN: 1574-6941</identifier><identifier>DOI: 10.1111/j.1574-6941.2000.tb00697.x</identifier><identifier>PMID: 10779618</identifier><language>eng</language><publisher>Oxford, UK: Blackwell Publishing Ltd</publisher><subject>Agar ; Agronomy. Soil science and plant productions ; Animal, plant and microbial ecology ; Applied ecology ; Ashes ; Bacteria ; Biological activity ; Biological and medical sciences ; Cadmium ; Cadmium chloride ; Carbon dioxide ; Community structure ; Coniferous forest humus ; Coniferous forests ; Darkness ; Decomposing organic matter ; Ecology ; Ecotoxicology, biological effects of pollution ; Fatty acids ; Fertilization ; Fertilizers ; Forestry ; Forests ; Fundamental and applied biological sciences. Psychology ; Hardwoods ; Heavy metal tolerance ; Humus ; Microbial activity ; Microbial community structure ; Microbiology ; Microcosms ; Microflora ; Microorganisms ; pH effects ; Phospholipids ; Pumice ; Relative humidity ; Soil and water pollution ; Soil science ; Substrates ; Terrestrial environment, soil, air ; Thymidine ; Wood ; Wood ash</subject><ispartof>FEMS microbiology ecology, 2000-04, Vol.32 (1), p.43-51</ispartof><rights>2000 Federation of European Microbiological Societies. Published by Elsevier Science B.V. All rights reserved. 2000</rights><rights>2000 INIST-CNRS</rights><rights>2000 Federation of European Microbiological Societies. Published by Elsevier Science B.V. All rights reserved.</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4043-da9edb941696b8930c247659682462e64272c3dc18944b327b001b0a17179e63</citedby><cites>FETCH-LOGICAL-c4043-da9edb941696b8930c247659682462e64272c3dc18944b327b001b0a17179e63</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,777,781,27905,27906</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=1409088$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/10779618$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Fritze, Hannu</creatorcontrib><creatorcontrib>Perkiömäki, Jonna</creatorcontrib><creatorcontrib>Saarela, Ulla</creatorcontrib><creatorcontrib>Katainen, Riikka</creatorcontrib><creatorcontrib>Tikka, Päivi</creatorcontrib><creatorcontrib>Yrjälä, Kim</creatorcontrib><creatorcontrib>Karp, Matti</creatorcontrib><creatorcontrib>Haimi, Jari</creatorcontrib><creatorcontrib>Romantschuk, Martin</creatorcontrib><title>Effect of Cd-containing wood ash on the microflora of coniferous forest humus</title><title>FEMS microbiology ecology</title><addtitle>FEMS Microbiol Ecol</addtitle><description>Abstract
The use of wood ash in forestry has been questioned because the cadmium (Cd) concentration of ash, which varies between 1 and 20 mg kg−1 ash, exceeds the level allowed for fertilizers (3 mg kg−1) used in agriculture. To investigate the combined and separated effects of Cd and ash on the forest humus microflora, pumice or wood ash, spiked with a water-soluble (CdCl2) or -insoluble (CdO) form of Cd at three levels (0, 400 and 1000 mg kg−1), were applied at a fertilization level of 5000 kg ha−1 in a laboratory microcosm study. The trial consisted of 60 microcosms (five replications per treatment), which were incubated in darkness at +20°C and a constant relative air humidity of 60%. After two months the humus in the microcosms was sampled. Analyses of CO2 evolution to measure the overall microbial activity and of phospholipid fatty acid (PLFA) pattern to measure microbial community structure were performed. The substrate-use patterns of Biolog EcoPlates were analyzed as a measure of bacterial functionality. Finally the bacterial 3H-thymidine incorporation in the presence of different concentrations of Cd and the number of colony forming units (cfu) of bacteria on nutrient agar in the presence of 0, 5 and 20 mg Cd l−1 agar were applied to measure Cd tolerance. The use of pumice (pH of humus under the pumice 4.0) did not induce any changes in the above variables compared to two untreated microcosms (humus pH 3.9). Pumice was therefore used to distribute the Cd evenly over the humus surface in order to estimate the possible effect of Cd without ash (pH of humus under the ash 7.0). The application of ash increased the microbial activity, changed the PLFA and substrate-use patterns and increased cfu compared to the humus under pumice. The form and level of Cd in the ash had no further effect on this result. In the humus under pumice the level, but not the form of Cd decreased the microbial activity and changed the PLFA pattern compared to the unspiked pumice. None of the treatments induced bacterial tolerance to Cd. Ash thus protected the humus microflora from the harmful effects of Cd.</description><subject>Agar</subject><subject>Agronomy. Soil science and plant productions</subject><subject>Animal, plant and microbial ecology</subject><subject>Applied ecology</subject><subject>Ashes</subject><subject>Bacteria</subject><subject>Biological activity</subject><subject>Biological and medical sciences</subject><subject>Cadmium</subject><subject>Cadmium chloride</subject><subject>Carbon dioxide</subject><subject>Community structure</subject><subject>Coniferous forest humus</subject><subject>Coniferous forests</subject><subject>Darkness</subject><subject>Decomposing organic matter</subject><subject>Ecology</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>Fatty acids</subject><subject>Fertilization</subject><subject>Fertilizers</subject><subject>Forestry</subject><subject>Forests</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Hardwoods</subject><subject>Heavy metal tolerance</subject><subject>Humus</subject><subject>Microbial activity</subject><subject>Microbial community structure</subject><subject>Microbiology</subject><subject>Microcosms</subject><subject>Microflora</subject><subject>Microorganisms</subject><subject>pH effects</subject><subject>Phospholipids</subject><subject>Pumice</subject><subject>Relative humidity</subject><subject>Soil and water pollution</subject><subject>Soil science</subject><subject>Substrates</subject><subject>Terrestrial environment, soil, air</subject><subject>Thymidine</subject><subject>Wood</subject><subject>Wood ash</subject><issn>0168-6496</issn><issn>1574-6941</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2000</creationdate><recordtype>article</recordtype><recordid>eNqVkV2L1DAYhYMo7rj6F6ToIt60vvloPgQvZJhVYRdv9j6kaeJ0aJsxadndf78pHVREBXOTizwn57zvQegVhgrn8-5Q4VqwkiuGKwIA1dQAcCWqu0do8-PpMdoA5rLkTPEz9CylAwCuKYOn6AyDEIpjuUHXO--dnYrgi21b2jBOphu78VtxG0JbmLQvwlhMe1cMnY3B9yGahc1g510Mcyp8iC5NxX4e5vQcPfGmT-7F6T5HN5e7m-3n8urrpy_bj1elZcBo2Rrl2iZn5Io3UlGwhAleKy4J48RxRgSxtLVYKsYaSkSeDzdgsMBCOU7P0dv122MM3-fsrocuWdf3ZnQ5ksayVpSAYDKjb_6NspoqwCKDr38DD2GOY55CE0qxzIsni_P7lcrLSCk6r4-xG0y81xj0Uo4-6KUBvTSgl3L0qRx9l8UvTxZzM7j2F-naRgYuToBJ1vQ-mtF26SfHQIFcsA8rdtv17v4_EujL3TWjWV-v-jAf_6Iu_5T_AQWAuAo</recordid><startdate>200004</startdate><enddate>200004</enddate><creator>Fritze, Hannu</creator><creator>Perkiömäki, Jonna</creator><creator>Saarela, Ulla</creator><creator>Katainen, Riikka</creator><creator>Tikka, Päivi</creator><creator>Yrjälä, Kim</creator><creator>Karp, Matti</creator><creator>Haimi, Jari</creator><creator>Romantschuk, Martin</creator><general>Blackwell Publishing Ltd</general><general>Blackwell</general><general>Oxford University Press</general><scope>IQODW</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7QL</scope><scope>7QP</scope><scope>7QR</scope><scope>7SN</scope><scope>7T7</scope><scope>7TK</scope><scope>7TM</scope><scope>7X7</scope><scope>7XB</scope><scope>88E</scope><scope>8FD</scope><scope>8FE</scope><scope>8FH</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BBNVY</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FR3</scope><scope>FYUFA</scope><scope>GHDGH</scope><scope>GNUQQ</scope><scope>HCIFZ</scope><scope>K9.</scope><scope>LK8</scope><scope>M0S</scope><scope>M1P</scope><scope>M7N</scope><scope>M7P</scope><scope>P64</scope><scope>PATMY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>RC3</scope><scope>7ST</scope><scope>SOI</scope><scope>7X8</scope></search><sort><creationdate>200004</creationdate><title>Effect of Cd-containing wood ash on the microflora of coniferous forest humus</title><author>Fritze, Hannu ; Perkiömäki, Jonna ; Saarela, Ulla ; Katainen, Riikka ; Tikka, Päivi ; Yrjälä, Kim ; Karp, Matti ; Haimi, Jari ; Romantschuk, Martin</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4043-da9edb941696b8930c247659682462e64272c3dc18944b327b001b0a17179e63</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2000</creationdate><topic>Agar</topic><topic>Agronomy. Soil science and plant productions</topic><topic>Animal, plant and microbial ecology</topic><topic>Applied ecology</topic><topic>Ashes</topic><topic>Bacteria</topic><topic>Biological activity</topic><topic>Biological and medical sciences</topic><topic>Cadmium</topic><topic>Cadmium chloride</topic><topic>Carbon dioxide</topic><topic>Community structure</topic><topic>Coniferous forest humus</topic><topic>Coniferous forests</topic><topic>Darkness</topic><topic>Decomposing organic matter</topic><topic>Ecology</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Fatty acids</topic><topic>Fertilization</topic><topic>Fertilizers</topic><topic>Forestry</topic><topic>Forests</topic><topic>Fundamental and applied biological sciences. 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The use of wood ash in forestry has been questioned because the cadmium (Cd) concentration of ash, which varies between 1 and 20 mg kg−1 ash, exceeds the level allowed for fertilizers (3 mg kg−1) used in agriculture. To investigate the combined and separated effects of Cd and ash on the forest humus microflora, pumice or wood ash, spiked with a water-soluble (CdCl2) or -insoluble (CdO) form of Cd at three levels (0, 400 and 1000 mg kg−1), were applied at a fertilization level of 5000 kg ha−1 in a laboratory microcosm study. The trial consisted of 60 microcosms (five replications per treatment), which were incubated in darkness at +20°C and a constant relative air humidity of 60%. After two months the humus in the microcosms was sampled. Analyses of CO2 evolution to measure the overall microbial activity and of phospholipid fatty acid (PLFA) pattern to measure microbial community structure were performed. The substrate-use patterns of Biolog EcoPlates were analyzed as a measure of bacterial functionality. Finally the bacterial 3H-thymidine incorporation in the presence of different concentrations of Cd and the number of colony forming units (cfu) of bacteria on nutrient agar in the presence of 0, 5 and 20 mg Cd l−1 agar were applied to measure Cd tolerance. The use of pumice (pH of humus under the pumice 4.0) did not induce any changes in the above variables compared to two untreated microcosms (humus pH 3.9). Pumice was therefore used to distribute the Cd evenly over the humus surface in order to estimate the possible effect of Cd without ash (pH of humus under the ash 7.0). The application of ash increased the microbial activity, changed the PLFA and substrate-use patterns and increased cfu compared to the humus under pumice. The form and level of Cd in the ash had no further effect on this result. In the humus under pumice the level, but not the form of Cd decreased the microbial activity and changed the PLFA pattern compared to the unspiked pumice. None of the treatments induced bacterial tolerance to Cd. Ash thus protected the humus microflora from the harmful effects of Cd.</abstract><cop>Oxford, UK</cop><pub>Blackwell Publishing Ltd</pub><pmid>10779618</pmid><doi>10.1111/j.1574-6941.2000.tb00697.x</doi><tpages>9</tpages><oa>free_for_read</oa></addata></record> |
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subjects | Agar Agronomy. Soil science and plant productions Animal, plant and microbial ecology Applied ecology Ashes Bacteria Biological activity Biological and medical sciences Cadmium Cadmium chloride Carbon dioxide Community structure Coniferous forest humus Coniferous forests Darkness Decomposing organic matter Ecology Ecotoxicology, biological effects of pollution Fatty acids Fertilization Fertilizers Forestry Forests Fundamental and applied biological sciences. Psychology Hardwoods Heavy metal tolerance Humus Microbial activity Microbial community structure Microbiology Microcosms Microflora Microorganisms pH effects Phospholipids Pumice Relative humidity Soil and water pollution Soil science Substrates Terrestrial environment, soil, air Thymidine Wood Wood ash |
title | Effect of Cd-containing wood ash on the microflora of coniferous forest humus |
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