2018
DOI: 10.1007/s11367-018-1495-z
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The influence of system boundaries and baseline in climate impact assessment of forest products

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Cited by 25 publications
(26 citation statements)
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“…In contrast, commencing at the time of replanting shows the opposite trend: a period of CO 2 removal during forest growth, followed by a pulse emission returning the CO 2 to the atmosphere. Thus, stand‐level assessments give inconsistent results and can be misleading as a basis to assess climate impacts of forest systems (Berndes et al, 2013; Cintas, Berndes, Cowie, et al, 2017; Peñaloza et al, 2019). Furthermore, when considering only the stand level, it is difficult to identify whether the forest is sustainably managed or subject to unsustainable practices that cause declining productive capacity and decreasing carbon stocks.…”
Section: Stand Versus Landscape Scale Assessmentmentioning
confidence: 99%
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“…In contrast, commencing at the time of replanting shows the opposite trend: a period of CO 2 removal during forest growth, followed by a pulse emission returning the CO 2 to the atmosphere. Thus, stand‐level assessments give inconsistent results and can be misleading as a basis to assess climate impacts of forest systems (Berndes et al, 2013; Cintas, Berndes, Cowie, et al, 2017; Peñaloza et al, 2019). Furthermore, when considering only the stand level, it is difficult to identify whether the forest is sustainably managed or subject to unsustainable practices that cause declining productive capacity and decreasing carbon stocks.…”
Section: Stand Versus Landscape Scale Assessmentmentioning
confidence: 99%
“…Across the whole forest landscape, that is, at the scale that forests are generally managed, temporal fluctuations observed at stand level are evened out and the forest carbon stock fluctuates around a trend line that can be increasing or decreasing, or roughly stable, depending on the age class distribution and weather patterns (Cowie et al, 2013). Landscape‐level assessment provides a more complete representation of the dynamics of forest systems, as it can integrate the effects of all changes in forest management and harvesting taking place in response to—experienced or anticipated—bioenergy demand, and it also incorporates the effects of landscape‐scale processes such as fire (Cintas et al, 2016; Cowie et al, 2013; Dwivedi et al, 2019; Koponen et al, 2018; Peñaloza et al, 2019).…”
Section: Stand Versus Landscape Scale Assessmentmentioning
confidence: 99%
“…The dynamic LCA method appears to be adequate, tackling the issue of timing biogenic elementary flows, as applied in several other studies of forest bioproducts (Fouquet et al 2015;Daystar et al 2016;Peñaloza et al 2016Peñaloza et al , 2018Demertzi et al 2018), and more specifically of forest-bioenergy (Zetterberg and Chen 2015;Albers et al 2019a). As highlighted by Levasseur et al (2012c), none of the current carbon accounting methods consider the temporal profiles of Cbio flows.…”
mentioning
confidence: 99%
“…Published studies have applied the historic (Vogtländer et al 2014;Zetterberg and Chen 2015;Demertzi et al 2018;Albers et al 2019a), future (Cherubini et al 2011b, a;Levasseur et al 2012b;Repo et al 2015;Pingoud et al 2016;De Rosa et al 2017) and occasionally both (Levasseur et al 2012c;Fouquet et al 2015;Peñaloza et al 2018) approaches. These opposed time perspectives yield different results, which require careful justification of the modelling choice.…”
mentioning
confidence: 99%
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