Can Biochar From Contaminated Biomass Be Applied Into Soil for Remediation Purposes?
The carbon rich material obtained from pyrolysis process, i.e. biochar, has been widely discussed during the last decade due to its utilisation as a soil amendment. Furthermore, there is an unsolved question of biomass disposal from phytoremediation technologies. The idea of contaminated biomass pyr...
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| Veröffentlicht in: | Water, air, and soil pollution air, and soil pollution, 2015-06, Vol.226 (6), p.1, Article 193 |
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| description | The carbon rich material obtained from pyrolysis process, i.e. biochar, has been widely discussed during the last decade due to its utilisation as a soil amendment. Furthermore, there is an unsolved question of biomass disposal from phytoremediation technologies. The idea of contaminated biomass pyrolysis has appeared, but there is lack of information about possible biochar utilisation obtained by this process. The aim of our study was to observe sorption properties of biochar prepared from contaminated biomass and release of contaminants from biochar back into the environment. The biomass of fast growing trees and maize was harvested on a site significantly damaged by risk element contamination (Cd, Pb and Zn). Plant biomass was pyrolysed and then the batch (de)sorption experiments were settled. The results confirmed no significant differences in metal sorption ability between biochars prepared from contaminated and uncontaminated biomass under the same conditions. The trend of maximum sorption capacity of observed matrices followed the order: wood biochar + soil (WB + soil) > wood uncontaminated biochar + soil (WUB + soil) > maize biochar + soil (MB + soil) > soil for cadmium, WB + soil > WUB + soil > soil for lead and MB + soil > WUB + soil > WB + soil > soil for zinc. Despite of increase of Zn desorption from wood biochars, maximum sorption capacity of the final WB + soil system was comparable to the WUB+soil sample. Our laboratory experiments showed high potential of biochar from contaminated plants as a soil amendment with sorption abilities and minimal risk of metal release. |
| doi_str_mv | 10.1007/s11270-015-2456-9 |
| format | Article |
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Furthermore, there is an unsolved question of biomass disposal from phytoremediation technologies. The idea of contaminated biomass pyrolysis has appeared, but there is lack of information about possible biochar utilisation obtained by this process. The aim of our study was to observe sorption properties of biochar prepared from contaminated biomass and release of contaminants from biochar back into the environment. The biomass of fast growing trees and maize was harvested on a site significantly damaged by risk element contamination (Cd, Pb and Zn). Plant biomass was pyrolysed and then the batch (de)sorption experiments were settled. The results confirmed no significant differences in metal sorption ability between biochars prepared from contaminated and uncontaminated biomass under the same conditions. The trend of maximum sorption capacity of observed matrices followed the order: wood biochar + soil (WB + soil) > wood uncontaminated biochar + soil (WUB + soil) > maize biochar + soil (MB + soil) > soil for cadmium, WB + soil > WUB + soil > soil for lead and MB + soil > WUB + soil > WB + soil > soil for zinc. Despite of increase of Zn desorption from wood biochars, maximum sorption capacity of the final WB + soil system was comparable to the WUB+soil sample. Our laboratory experiments showed high potential of biochar from contaminated plants as a soil amendment with sorption abilities and minimal risk of metal release.</description><identifier>ISSN: 0049-6979</identifier><identifier>EISSN: 1573-2932</identifier><identifier>DOI: 10.1007/s11270-015-2456-9</identifier><language>eng</language><publisher>Cham: Springer International Publishing</publisher><subject>Atmospheric Protection/Air Quality Control/Air Pollution ; Biomass ; Cadmium ; Charcoal ; Climate Change/Climate Change Impacts ; Contaminants ; Corn ; Earth and Environmental Science ; Environment ; Environmental monitoring ; Experiments ; Heavy metal content ; Heavy metals ; Hydrogeology ; Information processing ; Nitrogen ; Phytoremediation ; Plant biomass ; Pyrolysis ; Raw materials ; Software ; Soil amendment ; Soil contamination ; Soil pollution ; Soil remediation ; Soil Science & Conservation ; Sorption ; Water Quality/Water Pollution ; Wood</subject><ispartof>Water, air, and soil pollution, 2015-06, Vol.226 (6), p.1, Article 193</ispartof><rights>Springer International Publishing Switzerland 2015</rights><rights>COPYRIGHT 2015 Springer</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-a378t-4fa28b38315fcdfdb64a44ff1257151388bd23afc2d89ac209ff2e60bcb384923</citedby><cites>FETCH-LOGICAL-a378t-4fa28b38315fcdfdb64a44ff1257151388bd23afc2d89ac209ff2e60bcb384923</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://link.springer.com/content/pdf/10.1007/s11270-015-2456-9$$EPDF$$P50$$Gspringer$$H</linktopdf><linktohtml>$$Uhttps://link.springer.com/10.1007/s11270-015-2456-9$$EHTML$$P50$$Gspringer$$H</linktohtml><link.rule.ids>314,776,780,27901,27902,41464,42533,51294</link.rule.ids></links><search><creatorcontrib>Brendova, Katerina</creatorcontrib><creatorcontrib>Tlustos, Pavel</creatorcontrib><creatorcontrib>Szakova, Jirina</creatorcontrib><title>Can Biochar From Contaminated Biomass Be Applied Into Soil for Remediation Purposes?</title><title>Water, air, and soil pollution</title><addtitle>Water Air Soil Pollut</addtitle><description>The carbon rich material obtained from pyrolysis process, i.e. biochar, has been widely discussed during the last decade due to its utilisation as a soil amendment. Furthermore, there is an unsolved question of biomass disposal from phytoremediation technologies. The idea of contaminated biomass pyrolysis has appeared, but there is lack of information about possible biochar utilisation obtained by this process. The aim of our study was to observe sorption properties of biochar prepared from contaminated biomass and release of contaminants from biochar back into the environment. The biomass of fast growing trees and maize was harvested on a site significantly damaged by risk element contamination (Cd, Pb and Zn). Plant biomass was pyrolysed and then the batch (de)sorption experiments were settled. The results confirmed no significant differences in metal sorption ability between biochars prepared from contaminated and uncontaminated biomass under the same conditions. The trend of maximum sorption capacity of observed matrices followed the order: wood biochar + soil (WB + soil) > wood uncontaminated biochar + soil (WUB + soil) > maize biochar + soil (MB + soil) > soil for cadmium, WB + soil > WUB + soil > soil for lead and MB + soil > WUB + soil > WB + soil > soil for zinc. Despite of increase of Zn desorption from wood biochars, maximum sorption capacity of the final WB + soil system was comparable to the WUB+soil sample. Our laboratory experiments showed high potential of biochar from contaminated plants as a soil amendment with sorption abilities and minimal risk of metal release.</description><subject>Atmospheric Protection/Air Quality Control/Air Pollution</subject><subject>Biomass</subject><subject>Cadmium</subject><subject>Charcoal</subject><subject>Climate Change/Climate Change Impacts</subject><subject>Contaminants</subject><subject>Corn</subject><subject>Earth and Environmental Science</subject><subject>Environment</subject><subject>Environmental monitoring</subject><subject>Experiments</subject><subject>Heavy metal content</subject><subject>Heavy metals</subject><subject>Hydrogeology</subject><subject>Information processing</subject><subject>Nitrogen</subject><subject>Phytoremediation</subject><subject>Plant biomass</subject><subject>Pyrolysis</subject><subject>Raw materials</subject><subject>Software</subject><subject>Soil amendment</subject><subject>Soil contamination</subject><subject>Soil pollution</subject><subject>Soil remediation</subject><subject>Soil Science & Conservation</subject><subject>Sorption</subject><subject>Water Quality/Water Pollution</subject><subject>Wood</subject><issn>0049-6979</issn><issn>1573-2932</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2015</creationdate><recordtype>article</recordtype><sourceid>BENPR</sourceid><recordid>eNp1kE1LAzEQhoMoWKs_wFvA89Z87iYnaYvVQkHReg7pblJTusmabA_-e7OsBy_OHAZm3mdmeAG4xWiGEaruE8akQgXCvCCMl4U8AxPMK1oQSck5mCDEZFHKSl6Cq5QOKIcU1QRsl9rDhQv1p45wFUMLl8H3unVe96YZJq1OCS4MnHfd0eXW2vcBvgd3hDZE-GZa0zjdu-Dh6yl2IZn0cA0urD4mc_Nbp-Bj9bhdPhebl6f1cr4pNK1EXzCridhRQTG3dWObXck0Y9ZiwivMMRVi1xCqbU0aIXVNkLSWmBLt6gwxSegU3I17uxi-Tib16hBO0eeTCpeiJCXhgmfVbFTt9dEo523oo65zNqZ1dfDGutyfM8ppKTkb1uIRqGNIKRqruuhaHb8VRmpwW41uq-y2GtxWMjNkZFLW-r2Jf175F_oBzGSA9w</recordid><startdate>20150601</startdate><enddate>20150601</enddate><creator>Brendova, Katerina</creator><creator>Tlustos, Pavel</creator><creator>Szakova, 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Furthermore, there is an unsolved question of biomass disposal from phytoremediation technologies. The idea of contaminated biomass pyrolysis has appeared, but there is lack of information about possible biochar utilisation obtained by this process. The aim of our study was to observe sorption properties of biochar prepared from contaminated biomass and release of contaminants from biochar back into the environment. The biomass of fast growing trees and maize was harvested on a site significantly damaged by risk element contamination (Cd, Pb and Zn). Plant biomass was pyrolysed and then the batch (de)sorption experiments were settled. The results confirmed no significant differences in metal sorption ability between biochars prepared from contaminated and uncontaminated biomass under the same conditions. The trend of maximum sorption capacity of observed matrices followed the order: wood biochar + soil (WB + soil) > wood uncontaminated biochar + soil (WUB + soil) > maize biochar + soil (MB + soil) > soil for cadmium, WB + soil > WUB + soil > soil for lead and MB + soil > WUB + soil > WB + soil > soil for zinc. Despite of increase of Zn desorption from wood biochars, maximum sorption capacity of the final WB + soil system was comparable to the WUB+soil sample. Our laboratory experiments showed high potential of biochar from contaminated plants as a soil amendment with sorption abilities and minimal risk of metal release.</abstract><cop>Cham</cop><pub>Springer International Publishing</pub><doi>10.1007/s11270-015-2456-9</doi></addata></record> |
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| ispartof | Water, air, and soil pollution, 2015-06, Vol.226 (6), p.1, Article 193 |
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| subjects | Atmospheric Protection/Air Quality Control/Air Pollution Biomass Cadmium Charcoal Climate Change/Climate Change Impacts Contaminants Corn Earth and Environmental Science Environment Environmental monitoring Experiments Heavy metal content Heavy metals Hydrogeology Information processing Nitrogen Phytoremediation Plant biomass Pyrolysis Raw materials Software Soil amendment Soil contamination Soil pollution Soil remediation Soil Science & Conservation Sorption Water Quality/Water Pollution Wood |
| title | Can Biochar From Contaminated Biomass Be Applied Into Soil for Remediation Purposes? |
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