2014
DOI: 10.3390/f5040847
|View full text |Cite
|
Sign up to set email alerts
|

Accountable Accounting: Carbon-Based Management on Marginal Lands

Abstract: Substantial discussion exists concerning the best land use options for mitigating greenhouse gas (GHG) emissions on marginal land. Emissions-mitigating land use options include displacement of fossil fuels via biofuel production and afforestation. Comparing C recovery dynamics under these different options is crucial to assessing the efficacy of offset programs. In this paper, we focus on forest recovery on marginal land, and show that there is substantial inaccuracy and discrepancy in the literature concernin… Show more

Help me understand this report

Search citation statements

Order By: Relevance

Paper Sections

Select...
3
1

Citation Types

0
6
0

Year Published

2014
2014
2019
2019

Publication Types

Select...
3
2
1
1

Relationship

0
7

Authors

Journals

citations
Cited by 8 publications
(6 citation statements)
references
References 67 publications
0
6
0
Order By: Relevance
“…Exclusion of the soil carbon and ecosystem respiration fluxes impose additional invalidation uncertainty for CARB-CAR protocols by the requirement of a 100-year invariant project baseline to ensure forest carbon storage permanence (California Air Resources Board, 2011; California Air Resources Board, 2014; California Air Resources Board, 2015b; Climate Action Reserve, 2018b). Soil carbon comprises up to three times the magnitude of above ground carbon composition, contributes up to ∼82% of ecosystem carbon exchange (Baldocchi & Penuelas, 2019; Barba et al, 2018; Giasson et al, 2013; Hollinger et al, 2013) and cannot be excluded from a complete, scientifically valid, carbon sequestration value for a forest project (Comeau et al, 2018; DiRocco et al, 2014; Li et al, 2018a; Li et al, 2018b). Soil warming and related soil CO 2 efflux predictions, including feedbacks to the biosphere (Davidson & Janssens, 2006), vary over the coming decades (Bond-Lamberty et al, 2018; Hicks Pries et al, 2017; Melillo et al, 2011; Wang et al, 2014; Yang et al, 2013) but they typically deny the assumption that the soil carbon pool and resulting fluxes will remain invariant over the 100-year required project interval (Bond-Lamberty et al, 2018; Li et al, 2018a; Li et al, 2018b).…”
Section: Discussionmentioning
confidence: 99%
“…Exclusion of the soil carbon and ecosystem respiration fluxes impose additional invalidation uncertainty for CARB-CAR protocols by the requirement of a 100-year invariant project baseline to ensure forest carbon storage permanence (California Air Resources Board, 2011; California Air Resources Board, 2014; California Air Resources Board, 2015b; Climate Action Reserve, 2018b). Soil carbon comprises up to three times the magnitude of above ground carbon composition, contributes up to ∼82% of ecosystem carbon exchange (Baldocchi & Penuelas, 2019; Barba et al, 2018; Giasson et al, 2013; Hollinger et al, 2013) and cannot be excluded from a complete, scientifically valid, carbon sequestration value for a forest project (Comeau et al, 2018; DiRocco et al, 2014; Li et al, 2018a; Li et al, 2018b). Soil warming and related soil CO 2 efflux predictions, including feedbacks to the biosphere (Davidson & Janssens, 2006), vary over the coming decades (Bond-Lamberty et al, 2018; Hicks Pries et al, 2017; Melillo et al, 2011; Wang et al, 2014; Yang et al, 2013) but they typically deny the assumption that the soil carbon pool and resulting fluxes will remain invariant over the 100-year required project interval (Bond-Lamberty et al, 2018; Li et al, 2018a; Li et al, 2018b).…”
Section: Discussionmentioning
confidence: 99%
“…This is because allometric tree growth relationships are influenced by the environmental conditions occurring in the specific areas in which they were developed. Inappropriate use of allometric relationships could also cause large errors in aboveground biomass carbon pool quantification [37]. In addition, age-specific relationships may be needed for certain species because tree allometry tends to change with stand age [38], a trend that was equally observed in short-rotation plantations [35].…”
mentioning
confidence: 99%
“…CARB-CAR projects categorically exclude the soil CO 2 and related carbon pools 55 (e.g., RF-6, IFM-6, AC-6, Methods, Table I), the primary component of ecosystem respiration and determinant of NEE 65,87,88 . Soil carbon content represents up to three times the magnitude of above ground carbon composition and up to ~80% of ecosystem carbon exchange 41,[87][88][89] ; it cannot be excluded from a complete, scientifically valid, net material carbon balance [90][91][92] for a forest project. In the case of CARB-CAR avoided carbon (e.g., AC) projects, specific to wetlands, while sampling of bulk soil carbon is recommended 93 , a corresponding term for soil carbon and CO 2 efflux (e.g., AC-6) is excluded from calculation of net GHG reduction ( Table I).…”
Section: Discussionmentioning
confidence: 99%
“…The anomalies noted for CARB-CAR sites (Table I) document non-standard, shifting protocol operations (e.g., arbitrary model operation to hindcast and forecast annual net forest carbon) and inconsistent reporting for the CARB-CAR and related protocols. Point three, above, is emphasized recognizing the lack of spatial and annual resolution provided by FVS analysis frameworks introducing errors of up to ~55% in calculation of annual changes in standing biomass for above ground carbon stock 90,[114][115][116] such as observed for Howland681. Similar errors likely apply to the population of CARB-CAR projects reporting given that sequential, annual forest mensuration survey is not required or routinely practiced to determine corresponding annual vintage year carbon sequestration differences.…”
Section: Howland Forest Site Methods Comparison the Howland Research mentioning
confidence: 99%