Please use this identifier to cite or link to this item: http://hdl.handle.net/10773/24421
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dc.contributor.authorVerheijen, Frank G. A.pt_PT
dc.contributor.authorJeffery, Simonpt_PT
dc.contributor.authorvan der Velde, Marijnpt_PT
dc.contributor.authorPenížek, Vítpt_PT
dc.contributor.authorBeland, Martinpt_PT
dc.contributor.authorBastos, Ana Catarinapt_PT
dc.contributor.authorKeizer, Jan Jacobpt_PT
dc.date.accessioned2018-10-22T14:13:15Z-
dc.date.available2018-10-22T14:13:15Z-
dc.date.issued2013-
dc.identifier.issn1748-9326pt_PT
dc.identifier.urihttp://hdl.handle.net/10773/24421-
dc.description.abstractBiochar can be defined as pyrolysed (charred) biomass produced for application to soils with the aim of mitigating global climate change while improving soil functions. Sustainable biochar application to soils has been estimated to reduce global greenhouse gas emissions by 71–130 Pg CO2-Ce over 100 years, indicating an important potential to mitigate climate change. However, these estimates ignored changes in soil surface reflection by the application of dark-coloured biochar. Through a laboratory experiment we show a strong tendency for soil surface albedo to decrease as a power decay function with increasing biochar application rate, depending on soil moisture content, biochar application method and land use. Surface application of biochar resulted in strong reductions in soil surface albedo even at relatively low application rates. As a first assessment of the implications for climate change mitigation of these biochar–albedo relationships, we applied a first order global energy balance model to compare negative radiative forcings (from avoided CO2 emissions) with positive radiative forcings (from reduced soil surface albedos). For a global-scale biochar application equivalent to 120 t ha−1, we obtained reductions in negative radiative forcings of 5 and 11% for croplands and 11 and 23% for grasslands, when incorporating biochar into the topsoil or applying it to the soil surface, respectively. For a lower global biochar application rate (equivalent to 10 t ha−1), these reductions amounted to 13 and 44% for croplands and 28 and 94% for grasslands. Thus, our findings revealed the importance of including changes in soil surface albedo in studies assessing the net climate change mitigation potential of biochar, and we discuss the urgent need for field studies and more detailed spatiotemporal modelling.pt_PT
dc.description.sponsorshipWe thank L Montanarella (Joint Research Centre) for making this study possible, W Mehl for help with the spectroscopy work and P Drahota for the mineralogy analyses. We thank the Portuguese Fundação para a Ciência e a Tecnologia (FCT) for providing F G A Verheijen with a postdoctoral grant (SFRH/BPD/74108/2010), and further want to acknowledge the financial support of the Czech Science Foundation (under grant No. GA 526/09/1762), and the Marie Curie CIG grant (No. GA 526/09/1762). We thank two anonymous reviewers for strengthening the letter.pt_PT
dc.language.isoengpt_PT
dc.publisherIOP Publishingpt_PT
dc.relationinfo:eu-repo/grantAgreement/FCT/SFRH/SFRH%2FBPD%2F74108%2F2010/PTpt_PT
dc.rightsopenAccesspt_PT
dc.subjectGeo-engineeringpt_PT
dc.subjectRadiative forcingpt_PT
dc.subjectSpectroscopypt_PT
dc.subjectSoilpt_PT
dc.subjectBiocharpt_PT
dc.titleReductions in soil surface albedo as a function of biochar application rate: implications for global radiative forcingpt_PT
dc.typearticlept_PT
dc.description.versionpublishedpt_PT
dc.peerreviewedyespt_PT
degois.publication.firstPage1- 044008pt_PT
degois.publication.issue4pt_PT
degois.publication.lastPage7 - 044008pt_PT
degois.publication.titleEnvironmental Research Letterspt_PT
degois.publication.volume8pt_PT
dc.identifier.doi10.1088/1748-9326/8/4/044008pt_PT
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