Biochar carbon removal

spruce wood chips, drying

Reference product spruce wood chips, dried RER

Published Version 1.0.1 Latest published

Stable dataset identity spruce-wood-chips-drying

Unit
kilogram
Reuse license
Undisclosed license type; I take responsibility for sharing it
Published
2026-07-21
Version
1.0.1
Technology maturity
See quality profile

Published inventory

Overview

Scope, source, release context, and stable identifying information.

Description

This dataset supplies 1 kilogram of preprocessed spruce wood chips before entering the pyrolysis process. The wood goes through drying and chipping. The energy requirements for drying the feedstock depend on its moisture content. The moisture level is assumed to be 40% (based on data from Tisserant, A., Morales, M., Cavalett, O., O'Toole, A., Weldon, S., Rasse, D. P., & Cherubini, F. (2022). Life-cycle assessment to unravel co-benefits and trade-offs of large-scale biochar deployment in Norwegian agriculture. Resources, Conservation and Recycling, 179, 106030. https://doi.org/10.1016/j.resconrec.2021.106030) with a conversion factor to dry ton of 0.6. The feedstock is assumed to be dried to zero moisture content to be on the safe side in accounting for the energy requirements of evaporating water at all stages. Rotary drier requirements: 0.1 GJ electricity/tonnes of water and 2.7 GJ thermal energy/tonnes of water. Electricity and heat requirements are taken from Manouchehrinejad, M., & Mani, S. (2019). Process simulation of an integrated biomass torrefaction and pelletization (iBTP) plant to produce solid biofuels. Energy Conversion and Management: X, 1, 100008. https://doi.org/10.1016/j.ecmx.2019.100008. Electric chipping requirements: 0.0005 GJ/ MJfsdry. The requirements for electric chipping are taken from Kuptz, D., & Hartmann, H. (2014). Throughput Rate and Energy Consumption During Wood Chip Production in Relation to Raw Material, Chipper Type and Machine Setting. https://doi.org/10.5071/22ndEUBCE2014-2CO.1.5. The distance from the collection point to the plant is assumed to be 100km.

Source: Hoeskuldsdottir, Gudrun. 2022. Life Cycle Assessment of Biochar to Soil Systems: A Parametric Analysis. Master’s thesis, Swiss Federal Institute of Technology Zürich and Paul Scherrer Institute.

Source

Thesis or dissertation

Hoeskuldsdottir, Gudrun. 2022. Life Cycle Assessment of Biochar to Soil Systems: A Parametric Analysis. Master’s thesis, Swiss Federal Institute of Technology Zürich and Paul Scherrer Institute.

Dataset details Expand Collapse

Dataset details

Classification
Biochar carbon removal (carbon-removal/biochar)
Background database
ecoinvent / 3.10
Background system model
cut-off
Biosphere database
ecoinvent / 3.10
Bookmarks
0
Raw file downloads
0
Generated export downloads
0

These are the source profiles for this version. Foreground modelling assumptions and allocation belong in the dataset description.

Classification path: Carbon removal > Biochar carbon removal

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Technology profile

Technology characterization

Scale, utilization, production, and lifetime data. Missing values remain visible to guide future metadata improvements.

Commercial maturity stage
Early commercial
Design capacity
Not provided
Design capacity unit
Not provided
Capacity factor
Not provided
Annual production volume
Not provided
Annual production volume unit
Not provided
Annual production volume year
Not provided
Plant lifetime
Not provided
Changes from version 1.0.0 Automatically detected by comparing the complete inventory snapshots. Exchange row order is ignored; structured proposal edits preserve their published-row correspondence. Open the base version. Show changes Hide changes

Public revision record

This comparison is permanently visible with the published version so users can assess every detected change before reuse.

Modified exchanges
0
Added exchanges
0
Removed exchanges
0
Inventory metadata
0
Version metadata
1

Metadata changes

Scope Field Previous value Revised value
Version metadata Description This dataset supplies 1 kilogram of preprocessed spruce wood chips before entering the pyrolysis process. The wood goes through drying and chipping. The energy requirements for drying the feedstock depend on its moisture content. The moisture level is assumed to be 40% (based on data from Tisserant, A., Morales, M., Cavalett, O., O'Toole, A., Weldon, S., Rasse, D. P., & Cherubini, F. (2022). Life-cycle assessment to unravel co-benefits and trade-offs of large-scale biochar deployment in Norwegian agriculture. Resources, Conservation and Recycling, 179, 106030. https://doi.org/10.1016/j.resconrec.2021.106030) with a conversion factor to dry ton of 0.6. The feedstock is assumed to be dried to zero moisture content to be on the safe side in accounting for the energy requirements of evaporating water at all stages. Rotary drier requirements: 0.1 GJ electricity/tonnes of water and 2.7 GJ thermal energy/tonnes of water. Electricity and heat requirements are taken from Manouchehrinejad, M., & Mani, S. (2019). Process simulation of an integrated biomass torrefaction and pelletization (iBTP) plant to produce solid biofuels. Energy Conversion and Management: X, 1, 100008. https://doi.org/10.1016/j.ecmx.2019.100008. Electric chipping requirements: 0.0005 GJ/ MJfsdry. The requirements for electric chipping are taken from Kuptz, D., & Hartmann, H. (2014). Throughput Rate and Energy Consumption During Wood Chip Production in Relation to Raw Material, Chipper Type and Machine Setting. https://doi.org/10.5071/22ndEUBCE2014-2CO.1.5. The distance from the collection point to the plant is assumed to be 100km. This dataset supplies 1 kilogram of preprocessed spruce wood chips before entering the pyrolysis process. The wood goes through drying and chipping. The energy requirements for drying the feedstock depend on its moisture content. The moisture level is assumed to be 40% (based on data from Tisserant, A., Morales, M., Cavalett, O., O'Toole, A., Weldon, S., Rasse, D. P., & Cherubini, F. (2022). Life-cycle assessment to unravel co-benefits and trade-offs of large-scale biochar deployment in Norwegian agriculture. Resources, Conservation and Recycling, 179, 106030. https://doi.org/10.1016/j.resconrec.2021.106030) with a conversion factor to dry ton of 0.6. The feedstock is assumed to be dried to zero moisture content to be on the safe side in accounting for the energy requirements of evaporating water at all stages. Rotary drier requirements: 0.1 GJ electricity/tonnes of water and 2.7 GJ thermal energy/tonnes of water. Electricity and heat requirements are taken from Manouchehrinejad, M., & Mani, S. (2019). Process simulation of an integrated biomass torrefaction and pelletization (iBTP) plant to produce solid biofuels. Energy Conversion and Management: X, 1, 100008. https://doi.org/10.1016/j.ecmx.2019.100008. Electric chipping requirements: 0.0005 GJ/ MJfsdry. The requirements for electric chipping are taken from Kuptz, D., & Hartmann, H. (2014). Throughput Rate and Energy Consumption During Wood Chip Production in Relation to Raw Material, Chipper Type and Machine Setting. https://doi.org/10.5071/22ndEUBCE2014-2CO.1.5. The distance from the collection point to the plant is assumed to be 100km.

Source: Hoeskuldsdottir, Gudrun. 2022. Life Cycle Assessment of Biochar to Soil Systems: A Parametric Analysis. Master’s thesis, Swiss Federal Institute of Technology Zürich and Paul Scherrer Institute.

Inventory workspace

Inventory & impacts

Inspect every exchange and its contribution to the selected EF v3.1 indicator.

Precalculated screening profile

Environmental impacts

Results per kilogram, using UVEK 2025 and the ecoinvent 3.10 biosphere. Exchange rows are shaded from green to red by relative contribution to the selected indicator.

Climate change 0.0365483 kg CO2-Eq / kilogram
Screening result

This screening result uses Brightpath mappings from the source background to UVEK 2025; mapped suppliers are not claims of scientific equivalence.

Show all 16 indicator totals
Acidification 0.000150123 mol H+-Eq / kilogram
Climate change 0.0365483 kg CO2-Eq / kilogram
Freshwater ecotoxicity 0.110895 CTUe / kilogram
Freshwater eutrophication 2.0602e-06 kg P-Eq / kilogram
Marine eutrophication 7.0990e-05 kg N-Eq / kilogram
Terrestrial eutrophication 0.000716881 mol N-Eq / kilogram
Human toxicity, cancer 5.0274e-11 CTUh / kilogram
Human toxicity, non-cancer 1.7297e-10 CTUh / kilogram
Ionising radiation 0.00275037 kBq U235-Eq / kilogram
Land use 85.6287 dimensionless / kilogram
Ozone depletion 8.9221e-10 kg CFC-11-Eq / kilogram
Particulate matter 4.4976e-10 disease incidence / kilogram
Photochemical ozone formation 0.000652996 kg NMVOC-Eq / kilogram
Resource use, fossils 0.498165 MJ, net calorific value / kilogram
Resource use, minerals and metals 3.3403e-08 kg Sb-Eq / kilogram
Water use 0.0126332 m3 world Eq deprived / kilogram
Calculation details

Profile uvek-2025-ef-v3-1-4e70d56a85b1 · artifact 4e70d56a85b1 · calculated 2026-09-30 13:49 UTC. These screening results do not replace a reviewed comparative LCA.

Dataset contents

Reference flows, emissions, technosphere inputs, and natural resources in this published snapshot.

Outputs

Reference flow

1 row

Reference production exchanges extracted from the uploaded inventory.

Exchange Reference / categories Amount Unit Metadata Climate change contribution
spruce wood, chipping and drying
RER
spruce wood, chipped and dried
1
kilogram - Reference flow

Inputs

Technosphere inputs

2 rows

Linked foreground or background product inputs used by this dataset.

Exchange Reference / categories Amount Unit Metadata Climate change contribution
softwood forestry, spruce, sustainable forest management
DE
cleft timber, measured as dry mass
1
kilogram
0.0365483 kg CO2-Eq / kilogram 100.0% of total
BAFU:2025
market for heat, district or industrial, other than natural gas
Europe without Switzerland
heat, district or industrial, other than natural gas
0
megajoule Zero amount

Parameters

Read-only definitions preserved with this inventory version. Values are supplied by the source; CLIC does not evaluate formulas or recalculate exchange amounts and impact scores from them.

No parameter definitions were supplied with this inventory snapshot.

Evidence and scrutiny

Quality & review

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Quality and maturity details Expand Collapse

Quality and maturity

TRL scale Higher is more mature. 9: routine commercial deployment 8: commercial, but still niche or scaling 7: first-commercial or advanced demonstration 6: engineering-scale demonstration 5: pilot or large prototype 4: bench or lab validated 3: research-stage concept Technology readiness level
1 to 5 scale Lower is better. 1: strong market- or operating-data basis 2: commercially plausible, but still somewhat specific 3: partly representative, with modelling or adaptation bias 4: pilot, proxy-based, scaled-up, or prospective 5: weak representation of the real technology state Technological representativeness
1 to 5 scale Lower is better. 1: geography matches the claimed scope well 2: regionally credible, but broader or less exact 3: generic regional or global proxy 4: weak proxy or clear geographic mismatch 5: geography is effectively unsupported Geographical representativeness
1 to 5 scale Lower is better. 1: current for that technology class 2: slightly dated, but still good 3: dated enough to need caution 4: stale, pilot-era, or prospective relative to current practice 5: clearly not representative of the current state Temporal representativeness

Missing exchange uncertainty generation: Not requested

Representativeness scores use a 1–5 scale when provided. Lower scores indicate a closer fit to the modeled technology, geography, or time period.

Public review record Curator-led bulk import. Public evidence is shown without participant accounts, assignments, recommendations, or private editor notes. Show review Hide review

Publication route

Curator-led bulk import

This inventory was restored from a public CLIC archive. Its original publication route is Curator-led bulk import; private review and workflow records were not transferred.

Source inventory archive

No public review transcript is available for this version.

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Raw uploaded files

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Original uploaded files were not included in the inventory archive. Generated inventory exports remain available.

Version history

Published versions are immutable and remain available.

Version Published Link
Version 1.0.1 2026-07-21 Current view
Version 1.0.0 2026-07-15 Open version