Lifecycle Assessment and Techno-Economic Analysis of Biochar Pellet Production from Forest Residues and Field Application
Open accessAbstract
Biochar produced from low-value forest biomass can provide substantial benefits to ecosystems and mitigate climate change-induced risks such as forest fires. Forest residues from restoration activities and timber harvest and biochar itself are bulky and thus incur high logistic costs, so are considered major bottlenecks for the commercialization of the biochar industry. The objectives of this study were to assess the environmental footprints and techno-economic feasibility of converting forest residues in Pacific Northwest United States into biochar pellets using portable systems followed by delivery of the final product to end-users for land application (dispersion). Two portable systems (Biochar Solutions Incorporated (BSI) and Air Curtain Burner (ACB)) were considered for biochar production. A cradle-to-grave lifecycle assessment (LCA) and a discounted cash flow analysis method were used to quantify the environmental impacts and minimum selling price (MSP) of biochar. The global warming (GW) impact of biochar production through BSI and ACB was estimated to be 306–444, and 750–1016 kgCO₂eq/tonne biochar applied to the field, respectively. The MSP of biochar produced through BSI and ACB was 1674–1909 and 528–1051 USD/tonne biochar applied to the field, respectively. Pelletizing of biochar reduced GW impacts during outbound logistics (~8–20%) but increased emissions during pelletizing (~1–9%). Results show the BSI system was a more viable option in terms of GW impact, whereas the ACB system can produce biochar with lower MSP. The results of the study conclude that the production of biochar pellets through the two portable systems and applied to fields can be both an environmentally beneficial and economically viable option.
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Written from the paper’s full text.
TL;DR
This study assesses cradle-to-grave environmental impacts and techno-economic feasibility of producing biochar pellets from Pacific Northwest forest residues using two portable systems (BSI and ACB) and applying them to soil. BSI has lower global warming impact, while ACB has lower minimum selling price.
Key findings
- Cradle-to-grave global warming (GW) impact was 306–444 kgCO₂eq/tonne biochar for BSI and 750–1016 kgCO₂eq/tonne biochar for ACB; BSI was the more viable option for GW impact.
- Minimum selling price (MSP) was 1674–1909 USD/tonne biochar for BSI and 528–1051 USD/tonne biochar for ACB; ACB produced biochar with lower MSP.
- Pelletizing reduced GW impacts during outbound logistics (~8–20%) but increased emissions during pelletizing (~1–9%); for BSI, pelletizing reduced GW by 37–54 kgCO₂eq/tonne biochar (~9–18%), while for ACB it increased cradle-to-grave GW by 6%, largely due to diesel generator emissions of about 71 kgCO₂eq/tonne biochar.
- Field application for carbon sequestration reduced GW impacts substantially (by 2–6 times), with overall reductions of 1420–1800 kgCO₂eq/tonne biochar, making the systems carbon-negative.
Methods
- Cradle-to-grave LCA following ISO 14040/14044, using SimaPro 9.1 and TRACI 2.1, with a functional unit of 1 tonne biochar; eight scenarios varied portable system (BSI vs. ACB), biochar form (bulk vs. pellets), and inclusion/exclusion of forest operations.
- Primary data came from the Waste to Wisdom project and Schatz Energy Research Center for forest residue harvesting, feedstock preparation, and biochar production; pelletizing data were taken from literature.
- TEA used a discounted cash flow rate of return model with 10-year project life, 16.5% nominal discount rate, 40% income tax, 300 operating days/year, 16 h/day, and 2021 USD; sensitivity analysis varied input parameters by ±20% for GW impacts and MSP (MSP sensitivity for scenario 4 only).
Limitations
- The paper does not state a dedicated limitations section.
- Evident limitations include the geographic focus on five Pacific Northwest US sites and two portable systems; the authors note pulp log availability due to lack of markets may not reflect other regions of the U.S.
- The analysis relies on assumptions such as 50 km biochar transport, two relocations per year, 80.5% biochar carbon stability over 100 years, mass allocation for forest operations, and sawlogs outside the system boundary; the figures also note annual operating time of 100 days, while the methods state 300 days/year.
Model-written summary. Check it against the paper before relying on it.
Integrity signals
Registry
Cites
Statistics
Claims the paper makes
7 of 39 cited sources checked · 2 supported · 0 flagged · accuracy not yet measured
- Premisecitation
The wide geographic distribution of forest residues usually causes high costs of logistics operations such as collection, loading, transportation, unloading, and storage.
“Considering the low price of forest residues, they are considered as a potential feedstock for biochar; however, the wide geographic distribution of forest residues usually causes high costs of logistics operations, e.g., collection, loading, transportation, unloading, and storage [4,11,12].”
Quote in the paperSubstantial claim1 of 3 sources checked- cites [4] Sahoo, 2019, Techno-Economic Analysis of Producing Solid Biofuels and Biochar from Forest Residues Using Portable Systems, Appl. Energy source
- cites [11] Wright, 2010, Techno-Economic Analysis of Biomass Fast Pyrolysis to Transportation Fuels, Fuel source
- cites [12] Yazan, 2016, Design of Sustainable Second-Generation Biomass Supply Chains, Biomass Bioenergy source
Section 2.1 (Harvesting and collection; page unavailable) says dispersed biomass sites require more transport moves and describes negative economic impacts of dispersion. Section 5.2 (page unavailable) also links longer collection distances to higher transportation costs. The paper does not establish that forest residues specifically are widely distributed or that this distribution raises loading, unloading, and storage costs. (LLM, conf=0.84)
Experimental — accuracy not yet measured
- Premisecitation
The high cost of inbound and outbound logistics is one of the main obstacles to the commercialization of the biochar industry and its growth.
“The high cost of inbound (i.e., biomass) and outbound (i.e., biochar) logistics is one of the main obstacles to the commercialization of the biochar industry and its growth.”
Quote in the paperSubstantial claim1 of 3 sources checked- cites [4] Sahoo, 2019, Techno-Economic Analysis of Producing Solid Biofuels and Biochar from Forest Residues Using Portable Systems, Appl. Energy source
- cites [11] Wright, 2010, Techno-Economic Analysis of Biomass Fast Pyrolysis to Transportation Fuels, Fuel source
- cites [12] Yazan, 2016, Design of Sustainable Second-Generation Biomass Supply Chains, Biomass Bioenergy source
The Introduction and §2.1 identify costly biomass transport as a barrier to the economic viability of second-generation bioenergy. Section 3.3 includes trucks carrying bio-oil and char, but the paper does not identify outbound biochar logistics as a main obstacle to commercialization or growth of a biochar industry; it studies supply chains in which biochar is a byproduct. (LLM, conf=0.87)
Experimental — accuracy not yet measured
- Premisecitation
Overall, biochar produced through the ACB system had higher carbon fixation compared to that of the BSI system.
“Overall, biochar produced through the ACB system had higher carbon fixation compared to that of the BSI system.”
Quote in the paperNot a substantial claim1 of 2 sources checked- cites [26] Sahoo, 2021, Life-Cycle Assessment and Techno-Economic Analysis of Biochar Produced from Forest Residues Using Portable Systems, Int. J. Life Cycle Assess. source
- cites [27] Puettmann, 2020, Life Cycle Assessment of Biochar Produced from Forest Residues Using Portable Systems, J. Clean. Prod. source
- Findingown data
Among all scenarios analyzed for the BSI system, the second scenario, biochar as bulk including forest operations during logging, had the highest global warming impact of 444 kgCO2eq/tonne of biochar.
“Among all scenarios analyzed for the BSI system, the second one, i.e., biochar as bulk, including forest operations during logging, had the highest GW (444 kgCO₂eq/tonne of biochar)”
Quote in the paperSubstantial claim - Findingown data
The MSP of biochar produced through the ACB system was in the range of 528-1051 USD/tonne.
“The MSP of biochar produced through the ACB system was in the range of 528-1051 USD/tonne.”
Quote in the paperSubstantial claim
- Findingown data
The annual cost of biochar produced through the ACB system was in the range of USD 950-2050 thousand for different scenarios.
“The annual cost of biochar produced through the ACB system was in the range of USD 950-2050 thousand for different scenarios (Figure 7).”
Quote in the paperNot a substantial claim - Findingown data
The minimum selling price of biochar produced through the ACB system was 528-1051 USD/tonne biochar applied to the field.
“The MSP of biochar produced through BSI and ACB was 1674-1909 and 528-1051 USD/tonne biochar applied to the field, respectively.”
Quote in the paperSubstantial claim - Findingnone given
Overall, field application of biochar for carbon sequestration reduced GW impacts substantially (by 2-6 times).
“Figure 5 shows that, overall, field application of biochar for carbon sequestration reduced GW impacts substantially (by 2-6 times).”
Quote in the paperSubstantial claim - Findingown data
35% (scenario 2) to 40% (scenario 4) of the annual cost was attributed to labor.
“In addition, 35% (scenario 2) to 40% (scenario 4) of the annual cost was attributed to labor.”
Quote in the paperNot a substantial claim - Findingown data
The global warming impact of biochar production through the ACB system was estimated to be 750-1016 kgCO2 eq/tonne biochar applied to the field.
“The global warming (GW) impact of biochar production through BSI and ACB was estimated to be 306-444, and 750-1016 kgCO 2 eq/tonne biochar applied to the field, respectively.”
Quote in the paperSubstantial claim - Findingown data
For all scenarios, capital cost and labor cost were the main components of annual production costs.
“For all scenarios, capital cost and labor cost were the main components of annual production costs.”
Quote in the paperNot a substantial claim - Findingown data
For the BSI system, the highest annual cost was associated with biochar production as powder, considering the inclusion of forest operations during logging.
“whereas the highest cost was associated with biochar production as powder, considering the inclusion of forest operations during logging (Figure 6).”
Quote in the paperNot a substantial claim - Findingown data
For the BSI system, biochar pellet production considering exclusion of forest operations during logging had the lowest annual cost.
“Biochar pellet production, considering exclusion of forest operations during logging, had the lowest annual cost”
Quote in the paperSubstantial claim - Findingown data
Pelletizing reduced the GW impacts in the products' transportation and biochar application process by about 64 kgCO2eq/tonne biochar.
“Although pelletizing reduced the GW impacts in the products' transportation and biochar application process, which was about 64 kgCO2eq/tonne biochar”
Quote in the paperSubstantial claim - Findingreasoning
The annual production cost of the ACB system is considerably higher than that of the BSI system.
“The comparison of the economics of BSI and ACB systems showed that the annual production cost of the ACB system is considerably higher than that of the BSI system”
Quote in the paperSubstantial claim - Findingreasoning
Among different scenarios considered, the GW impacts of scenarios 2 and 4 were higher than those of scenarios 1 and 3.
“Among different scenarios considered, the GW impacts of scenarios 2 and 4 were higher than those of scenarios 1 and 3.”
Quote in the paperSubstantial claim - Findingown data
The MSP of biochar produced through the BSI system was in the range of 1674-1909 USD/tonne biochar.
“The MSP of biochar produced through the BSI system was in the range of 1674-1909 USD/tonne biochar”
Quote in the paperSubstantial claim - Findingown data
Overall, biochar production through portable systems reduced GW impacts by 1420-1800 kgCO2eq/tonne of biochar.
“Overall, biochar production through portable systems reduced GW impacts by 1420-1800 kgCO2eq/tonne of biochar (Figure 5)”
Quote in the paperSubstantial claim - Findingown data
The annual cost of biochar production through the BSI system was in the range of USD 412-470 thousand for different scenarios.
“The annual cost of biochar production through the BSI system was in the range of USD 412-470 thousand for different scenarios.”
Quote in the paperNot a substantial claim - Findingown data
Scenario 3 had the lowest cost (USD 950 thousand).
“Scenario 3 had the lowest cost (USD 950 thousand)”
Quote in the paperNot a substantial claim - Findingown data
The minimum selling price of biochar produced through the BSI system was 1674-1909 USD/tonne biochar applied to the field.
“The MSP of biochar produced through BSI and ACB was 1674-1909 and 528-1051 USD/tonne biochar applied to the field, respectively.”
Quote in the paperSubstantial claim - Findingown data
Forest operation incurred about 26% of cradle-to-grave GW impacts of biochar production through the ACB system.
“Forest operation incurred about ~26% of cradle-to-grave GW impacts of biochar production through the ACB system.”
Quote in the paperNot a substantial claim - Findingown data
Scenario 2 had the highest cost (USD 2050 thousand).
“whereas scenario 2 had the highest cost (USD 2050 thousand).”
Quote in the paperNot a substantial claim - Findingown data
Among all scenarios analyzed for the ACB system, scenario 1 (biochar as bulk, excluding forest operations during logging) had the lowest GW impact (~750 kgCO2eq/tonne of biochar).
“whereas the first scenario, i.e., biochar as bulk, excluding forest operations during logging, had the lowest GW impact (~750 kgCO2eq/tonne of biochar).”
Quote in the paperSubstantial claim - Findingown data
The global warming impact of biochar production through the BSI system was estimated to be 306-444 kgCO2 eq/tonne biochar applied to the field.
“The GW impact of the BSI system varied from 306 to 444 kgCO 2 eq/tonne of biochar (Figure 3).”
- Also stated in: § Abstract · hedged
“The global warming (GW) impact of biochar production through BSI and ACB was estimated to be 306-444, and 750-1016 kgCO 2 eq/tonne biochar applied to the field, respectively.”
Quote in the paperSubstantial claim - Also stated in: § Abstract · hedged
- Findingnone given
Field application of biochar as a pellet reduced the annual costs compared to application in bulk form.
“whereas field application of biochar as a pellet reduced the annual costs compared to application in bulk form.”
Quote in the paperSubstantial claim - Findingown data
The contribution of capital cost to total annual cost was slightly less than that of labor cost, estimated to be from 30% (scenario 2) to 35% (scenario 4).
“The contribution of capital cost to total annual cost was slightly less than that of labor cost, which was estimated to be from 30% (scenario 2) to 35% (scenario 4).”
Quote in the paperNot a substantial claim - Findingreasoning
For the ACB system, pelletizing increased the cradle-to-grave GW impacts by 6%.
“Contrary to the BSI system, pelletizing increased the cradle-to-grave GW impacts by 6%.”
Quote in the paperSubstantial claim - Findingown data
Among all scenarios analyzed for the ACB system, scenario 4 (biochar as pellet, including forest operations during logging) had the highest GW impact (~1015 kgCO2eq/tonne of biochar).
“Among all scenarios analyzed for the ACB system, the fourth one, i.e., biochar as pellet, including forest operations during logging, had the highest GW impact (~1015 kgCO2eq/tonne of biochar)”
Quote in the paperSubstantial claim - Findingown data
Among all scenarios analyzed for the BSI system, the third scenario, biochar as pellets excluding forest operations during logging, had the lowest global warming impact of 306 kgCO2eq/tonne of biochar.
“whereas the third scenario, i.e., biochar as pellets, excluding forest operations during logging, had the lowest GW impact (306 kgCO₂eq/tonne of biochar).”
Quote in the paperSubstantial claim - Findingown data
Similar trends can be seen for biochar produced through the ACB system.
“Similar trends can be seen for biochar produced through the ACB system (Figure 8b).”
Quote in the paperNot a substantial claim - Findingown data
Among all input parameters, fuel use and biochar yield are the most influential input parameters affecting cradle-to-grave GW impacts of biochar produced in the BSI system.
“Among all input parameters, fuel use and biochar yield are the most influential input parameters affecting cradle-to-grave GW impacts of biochar produced in the BSI system.”
Quote in the paperSubstantial claim - Findingown data
The operational days in a year and operational hours had higher impacts for the BSI than the ACB system.
“The operational days in a year and operational hours had higher impacts for the BSI than the ACB system.”
Quote in the paperNot a substantial claim - Findingreasoning
The BSI system had higher costs in terms of labor and capital costs, which significantly increased the MSP of biochar produced in the BSI system compared to that of the ACB system.
“Third, the BSI system had higher costs in terms of labor, and capital costs, which significantly increased the MSP of biochar produced in the BSI system compared to that of the ACB system.”
Quote in the paperSubstantial claim - Findingown data
A 20% lower fuel use in the harvesting and processing of forest biomass can reduce the GW impacts of biochar produced in the BSI system by 10%.
“A 20% lower fuel use in the harvesting and processing of forest biomass can reduce the GW impacts of biochar produced in the BSI system by 10% (Figure 8a).”
Quote in the paperNot a substantial claim - Findingown data
Biochar production in pellet form had lower MSP compared to biochar production in bulk form.
“First, biochar production in pellet form had lower MSP compared to biochar production in bulk form.”
Quote in the paperSubstantial claim - Findingown data
A 20% lower biochar yield in the BSI system can increase the GW impacts of biochar by 24%.
“However, a 20% lower biochar yield in the BSI system can increase the GW impacts of biochar by 24%.”
Quote in the paperSubstantial claim - Findingown data
Among all input parameters affecting the MSP of biochar pellets, the most influential input parameters were biochar yield, operational cost, and feedstock costs, which are common to both BSI and ACB systems.
“Among all input parameters affecting the MSP of biochar pellets, the most influential input parameters were biochar yield, operational cost, and feedstock costs, which are common to both BSI and ACB systems.”
Quote in the paperSubstantial claim - Premisecitation
Use of portable systems for conversion of forest residues to biomass-based products at a point close to supply regions can potentially reduce biomass logistics costs.
“The use of portable systems for the conversion of forest residues to various biomass-based products at a point close to the supply regions can potentially reduce the biomass logistics costs [4,15].”
Quote in the paperNot a substantial claim0 of 2 sources checked - Premisecitation
Conversion of forest residues to biochar reduces the risk of forest fires.
“Consequentially, conversion of forest residues to a useful product, such as biochar, not only helps produce valuable biobased products but also reduces the risk of forest fires, which are becoming extreme due to increasing fuel loads in the forest, i.e., woody biomass [8].”
Quote in the paperSubstantial claim0 of 1 sources checked- cites [8] Cook, P.S., and Becker, D.R. (2017). State Funding for Wildfire Suppression in the Western Us, University of Idaho.
Not checked in the free run.
- Premisereasoning
The current literature either lacks or does not provide holistic information on the technical feasibility, costs, and environmental impacts of biochar production and pelletizing using portable systems.
“The current literature either lacks or does not provide holistic information on the technical feasibility, costs, and environmental impacts of biochar production and pelletizing using portable systems.”
Quote in the paperSubstantial claim - Interpretationown data
Biochar production through portable systems can be considered a carbon-negative solution.
“and thus can be considered as a carbon-negative solution.”
Quote in the paperSubstantial claim- Rests on an assumption: Biochar provides long-term storage for carbon that originated from trees pulling carbon dioxide from the atmosphere; when biochar is added to the soil, carbon sinks are formed and carbon sequestration occurs.
- Premisecitation
According to the 2016 billion-ton report baseline scenario, about 93.1 million dry tons of forest residues and whole-tree biomass from thinning operations and clear cutting will be available in 2022.
“According to the 2016 billion-ton report baseline scenario (assuming moderate growth in housing starts and low growth in biomass for energy), about 93.1 million dry tons of forest residues and whole-tree biomass from thinning operations and clear cutting will be available in 2022 [7].”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites [7] Stokes, B.J., Langholtz, M.H., and Eaton, L.M. (2016). 2016 Billion-Ton Report: Advancing Domestic Resources for a Thriving Bioeconomy, Volume 1: Economic Availability of Feedstocks, ORNL/TM-2016/160. source
- Interpretationreasoning
The higher annual production cost of the ACB system is mainly due to high costs of feedstock and handling, labor, and product packaging compared to the BSI system.
“and this was mainly due to high costs of feedstock and handling, labor, and product packaging in the ACB system compared to the BSI system.”
Quote in the paperSubstantial claim - Interpretationown data
Inclusion of forest operations during logging increases the global warming impacts.
“and, not unexpectedly, the inclusion of forest operations during logging increases the GW impacts.”
Quote in the paperSubstantial claim - Interpretationreasoning
Pelletizing would be a better option for biochar if biochar pellets are transported for further distances, as assumed in this study.
“pelletizing would be a better option for biochar if biochar pellets are transported for further distances, as assumed in this study.”
Quote in the paperSubstantial claim- The authors state this as an assumption: In this study, biochar pellets are assumed to be transported for further distances.
- Interpretationreasoning
Field application of biochar as pellets can potentially reduce the global warming impact by 8-15%.
“This indicates that the field application of biochar as pellets can potentially reduce (8-15%) the GW impact”
Quote in the paperSubstantial claim - Interpretationreasoning
The differences in GW impact were mainly due to the inclusion and exclusion of forest operations, rather than the field application of biochar either as bulk or pellet forms.
“This indicated that the differences in GW impact were mainly due to the inclusion and exclusion of forest operations, rather than the field application of biochar either as bulk or pellet forms.”
Quote in the paperSubstantial claim - Interpretationreasoning
The high feedstock cost share in the ACB system was due to the very low yield of biochar, requiring more woody biomass to be processed to offset this lower yield.
“This was due to the very low yield of biochar in the ACB system, and thus required more woody biomass to be processed to offset this lower yield.”
Quote in the paperSubstantial claim - Premisecitation
In the United States, forest residues, a byproduct of timber harvest, have a high potential to be utilized as a biomass feedstock for renewable products.
“In the United States, forest residues, a byproduct of timber harvest, have a high potential to be utilized as a biomass feedstock for renewable products [5,6].”
Quote in the paperSubstantial claim0 of 2 sources checked- cites [5] Tilman, 2009, Beneficial Biofuels—The Food, Energy, and Environment Trilemma, Science source
- cites [6] Bergman, R., Berry, M., Bilek, E.T., Bowers, T., Eastin, I., Ganguly, I., Han, H.-S., Hirth, K., Jacobson, A., and Karp, S. (2018). Waste to Wisdom: Utilizing Forest Residues for the Production of Bioenergy and Biobased Products, 78: Biomass Research and Development Initiative Program Award Number DE-EE0006297.
Not checked in the free run.
- Interpretationown data
ACB requires more wood to be processed to obtain a similar amount of biochar compared to the BSI system.
“Hence, ACB requires more wood to be processed to obtain a similar amount of biochar compared to the BSI system.”
Quote in the paperSubstantial claim - Interpretationreasoning
The inclusion of forest operations during logging increased the annual cost.
“Overall, the inclusion of forest operations during logging increased the annual cost”
Quote in the paperSubstantial claim - Interpretationnone given
Biochar pellet production from forest residues can be considered as an expensive means of capturing or removing carbon from the atmosphere.
“Biochar pellet production from forest residues can be considered as an expensive means of capturing or removing carbon from the atmosphere.”
Quote in the paperNot a substantial claim - Interpretationreasoning
The higher impact of forest operations on MSP in the ACB system was mainly affected by feedstock and handling costs.
“This was mainly affected by feedstock and handling costs in the ACB system.”
Quote in the paperSubstantial claim
- Classified as probably not a substantial claim. 9
- May combine two claims. 30
Classified as probably not a substantial claim.
PremisecitationPelletization has been recently considered as an alternative method for efficient handling and biochar application to soil to reduce the cost of biochar logistics.
“To reduce the cost of biochar logistics, pelletization has been recently considered as an alternative method for efficient handling and biochar application to soil [16,19].”
Quote in the paperSubstantial claim1 of 2 sources checked- cites [16] Bergman, R.D., Zhang, H., Englund, K., Windell, K., and Gu, H. (2016, January 6–10). Estimating Ghg Emissions from the Manufacturing of Field-Applied Biochar Pellets. Proceedings of the 59th International Convention of Society of Wood Science and Technology, Curitiba, Brazil.
- cites [19] Bartocci, 2018, Biocarbon pellet production: Optimization of pelletizing process, Chem. Eng. Trans source
The Introduction says pelletizing charcoal can improve bulk density and transportation and storage costs, supporting the logistics part of the claim. It discusses the pellets as fuel, however, and does not address efficient handling or applying biochar to soil. (LLM, conf=0.86)
Experimental — accuracy not yet measured
May combine two claims.
PremisecitationFew studies have evaluated the use of portable systems; however, their main focus is the production of bio-oil as the main product, but not biochar.
“Few studies have evaluated the use of portable systems; however, their main focus is the production of bio-oil as the main product, but not biochar [20][21][22][23].”
Quote in the paperSubstantial claim1 of 4 sources checked- cites [20] Badger, 2010, Techno-Economic Analysis: Preliminary Assessment of Pyrolysis Oil Production Costs and Material Energy Balance Associated with a Transportable Fast Pyrolysis System, BioResources source
- cites [21] Chen, 2018, Mobile Autothermal Pyrolysis System for Local Biomass Conversion: Process Simulation and Techno-Economic Analysis, Energy Fuels source
- cites [22] Mirkouei, 2016, Reducing the Cost and Environmental Impact of Integrated Fixed and Mobile Bio-Oil Refinery Supply Chains, J. Clean. Prod. source
- cites [23] Polagye, 2007, An Economic Analysis of Bio-Energy Options Using Thinnings from Overstocked Forests, Biomass Bioenergy source
May combine two claims.
PremisecitationThrough pelletizing, the bulk density of biochar is increased and the material is aggregated, thus reducing logistics costs.
“Through pelletizing, the bulk density of biochar is increased and the material is aggregated, thus reducing the logistics (i.e., transportation, storage, handling, and field application) costs [16,17].”
Quote in the paperSubstantial claim1 of 2 sources checked- cites [16] Bergman, R.D., Zhang, H., Englund, K., Windell, K., and Gu, H. (2016, January 6–10). Estimating Ghg Emissions from the Manufacturing of Field-Applied Biochar Pellets. Proceedings of the 59th International Convention of Society of Wood Science and Technology, Curitiba, Brazil.
- cites [17] Riva, 2019, A Study of Densified Biochar as Carbon Source in the Silicon and Ferrosilicon Production, Energy source
The Introduction says pelletization generally increases density and mechanical durability, helping address losses during handling and transportation. It also discusses minimizing transportation costs, but the paper measures pellet particle density rather than bulk density and does not establish reduced storage or field-application costs; its application is silicon and ferrosilicon production. (LLM, conf=0.86)
Experimental — accuracy not yet measured
May combine two claims.
PremisecitationConversion of forest residues to biochar in pellet form helps capture carbon from the environment and store it in the soil, thus reducing CO2 in the atmosphere, in addition to increasing soil productivity and enhancing soil carbon.
“Conversion of forest residues to biochar in the pellet form also helps to capture carbon from the environment and store it in the soil, thus reducing CO 2 in the atmosphere, in addition to increasing soil productivity and enhancing soil carbon [2,10].”
Quote in the paperSubstantial claim1 of 2 sources checked- cites [2] Agegnehu, 2017, The Role of Biochar and Biochar-Compost in Improving Soil Quality and Crop Performance: A Review, Appl. Soil Ecol. source
- cites [10] Jeffery, 2015, The Way Forward in Biochar Research: Targeting Trade-Offs between the Potential Wins, GCB Bioenergy source
The ‘Climate change mitigation vs. soil fertility’ section says biochar can sequester carbon in soil for extended periods and reports increased soil fertility, though fertility effects are highly variable. It does not establish these benefits specifically for biochar pellets made from forest residues, and it describes climate mitigation as a potential rather than a guaranteed reduction in atmospheric CO₂. (LLM, conf=0.88)
Experimental — accuracy not yet measured
May combine two claims.
Findingown dataPelletizing can reduce the global warming impacts by 37-54 kgCO2eq/tonne of biochar, about 9-18% of cradle-to-grave global warming impacts, mostly due to the logistics of biochar.
“However, pelletizing can reduce the GW impacts by 37-54 kgCO₂eq/tonne of biochar (~9-18% of cradle-to-grave GW impacts), mostly due to the logistics of biochar.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataForest operation incurred about 84-101 kgCO2eq/tonne of biochar, about 20-25%, towards cradle-to-grave global warming impacts of the BSI system.
“Forest operation incurred about 84-101 kgCO₂eq/tonne of biochar (~20-25%) towards cradle-to-grave GW impacts of the BSI system.”
Quote in the paperSubstantial claimMay combine two claims.
Findingnone givenThe productivity or throughput of the ACB system was much larger than the BSI system, thus notably reducing the MSP for the ACB system.
“Contrarily, the productivity or throughput of the ACB system was much larger than the BSI system, thus notably reducing the MSP for the ACB system.”
Quote in the paperSubstantial claimMay combine two claims.
FindingreasoningBiochar produced with the ACB portable system at near-forest locations showed higher GW impact (2-2.5 times more) compared to the BSI system, with GW emissions from 750 to 1016 kgCO2 eq/tonne biochar applied to the field.
“Biochar produced with the ACB portable system at near-forest locations showed higher GW impact (2-2.5 times more) compared to the BSI system, with GW emissions from 750 to 1016 kgCO 2 eq/tonne biochar applied to the field (Figure 4).”
Quote in the paperSubstantial claimMay combine two claims.
FindingreasoningAbout 20-27% (scenarios 1 and 3) and 52-60% (scenarios 2 and 4) of costs were due to feedstocks in scenarios where forest operations were excluded and included, respectively.
“About 20-27% (scenarios 1 and 3) and 52-60% (scenarios 2 and 4) were due to feedstocks in scenarios where the forest operations were excluded and included, respectively.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataThe BSI system produced lower cradle-to-gate GW impacts, but its carbon sequestration was lower due to lower carbon content in biochar for this system.
“Although the BSI system produced lower cradle-to-gate GW impacts, the carbon sequestration was lower due to lower carbon content in biochar for this system.”
Quote in the paperSubstantial claimMay combine two claims.
Findingnone givenConversion of biochar to pellets and exclusion of forest operations during logging reduced the MSP of biochar in the ACB system.
“Conversion of biochar to pellets and exclusion of forest operations during logging reduced the MSP of biochar in the ACB system.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataPelletizing of biochar reduced global warming impacts during outbound logistics by about 8-20% but increased emissions during pelletizing by about 1-9%.
“Pelletizing of biochar reduced GW impacts during outbound logistics (~8-20%) but increased emissions during pelletizing (~1-9%).”
Quote in the paperSubstantial claimMay combine two claims.
Findingnone givenThe biochar production yield of ACB and BSI systems was estimated to be 35.6 and 126.8 kg biochar/tonne of woody biomass at 21% (wb), respectively.
“The biochar production yield of ACB and BSI systems was estimated to be 35.6 and 126.8 kg biochar/tonne of woody biomass at 21% (wb), respectively.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataFor the BSI system, MSP was lowest in biochar pellet production excluding forest operations during logging and highest in biochar production as bulk including forest operations during logging.
“and it was lowest in biochar pellet production by considering exclusion of forest operations during logging and highest in biochar production as bulk by considering the inclusion of forest operations during logging (Figure 6).”
Quote in the paperNot a substantial claimMay combine two claims.
FindingreasoningThe inclusion of forest operations significantly affects the MSP in both BSI and ACB systems; however, the impact of inclusion and exclusion of forest operations in the ACB system was higher than that in the BSI system.
“Second, the inclusion of forest operations significantly affects the MSP in both BSI and ACB systems; however, the impact of inclusion and exclusion of forest operations in the ACB system was higher than that in the BSI system.”
Quote in the paperSubstantial claimMay combine two claims.
Findingnone givenConversion of biochar to pellets was found to reduce the overall GW impacts and MSP of biochar production.
“In addition, conversion of biochar to pellets was found to reduce the overall GW impacts and MSP of biochar production.”
Quote in the paperNot a substantial claimMay combine two claims.
FindingreasoningThe productivity of ACB systems, such as the hourly production capacity of biochar, was much higher (by ~5 times) than the BSI system, thus helping to reduce the cost including capital and operational costs.
“The productivity of ACB systems, such as the hourly production capacity of biochar, was much higher (by ~5 times) than the BSI system, thus helping to reduce the cost including capital and operational costs.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationConverting biochar into pellets may improve total porosity and aeration porosity; thus, its proper balance in the soil can help plant growth.
“In addition, converting biochar into pellets may improve total porosity and aeration porosity; thus, its proper balance in the soil can help the plant growth [18].”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites [18] Dumroese, 2011, Pelleted Biochar: Chemical and Physical Properties Show Potential Use as a Substrate in Container Nurseries, Biomass Bioenergy source
May combine two claims.
PremisecitationForest residues usually have low bulk and energy densities but high moisture content, which tends to generate high costs for feedstock transportation, handling, and drying.
“In addition, forest residues usually have both low bulk and energy densities but high moisture content, which tends to generate a high cost for feedstock transportation, handling, and drying [13,14].”
Quote in the paperSubstantial claim0 of 2 sources checked- cites [13] Parkhurst, 2016, An Energy Analysis Comparing Biomass Torrefaction in Depots to Wind with Natural Gas Combustion for Electricity Generation, Appl. Energy source
- cites [14] Sahoo, 2018, Economic Analysis of Forest Residues Supply Chain Options to Produce Enhanced-Quality Feedstocks, Biofuels Bioprod. Biorefining source
May combine two claims.
PremisecitationBased on literature, after 100 years of land application of biochar, 80.5% of carbon in biochar will remain stable and the remaining 19.5% will be emitted to the atmosphere.
“Based on the literature [38], it is estimated that after 100 years of land application of biochar, 80.5% of carbon in the biochar will remain stable and the remaining 19.5% will be emitted to the atmosphere.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites [38] Budai, A., Zimmerman, A.R., Cowie, A.L., Webber, J.B.W., Singh, B.P., Glaser, B., Masiello, C.A., Andersson, D., Shields, F., and Lehmann, J. (2021, May 15). Biochar Carbon Stability Test Method: An Assessment of Methods to Determine Biochar Carbon Stability. Available online: https://www.biochar-international.org/wp-content/uploads/2018/06/IBI_Report_Biochar_Stability_Test_Method_Final.pdf.
Not checked in the free run.
May combine two claims.
InterpretationreasoningDue to the high-quality biochar produced in the ACB system, the carbon storage capacity was much higher, and the net-GW impact was better.
“Due to the high-quality biochar produced in the ACB system, the carbon storage capacity was much higher, and the net-GW impact was better.”
Quote in the paperSubstantial claimMay combine two claims.
Interpretationown dataThe higher GW impact of ACB compared to BSI is mainly due to higher emissions during processing operations and lower biochar yield.
“This was mainly due to higher emissions during processing operations and lower biochar yield.”
Quote in the paperSubstantial claimMay combine two claims.
PremisecitationForest residues left on-site increase the risk of wildfires and diseases; the majority of fires result from overstocked forest land.
“In addition, forest residues left on-site increase the risk of wildfires and diseases; the majority of fires result from overstocked forest land (Dennison et al., 2014;USDOE, 2016).”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Dennison et al., 2014
Couldn’t be matched to a paper in Crossref, so it can’t be checked.
- cites USDOE, 2016
Couldn’t be matched to a paper in Crossref, so it can’t be checked.
May combine two claims.
Interpretationown dataThe BSI system was a more viable option in terms of global warming impact, whereas the ACB system can produce biochar with lower minimum selling price.
“Results show the BSI system was a more viable option in terms of GW impact, whereas the ACB system can produce biochar with lower MSP.”
Quote in the paperSubstantial claimClassified as probably not a substantial claim. May combine two claims.
PremisecitationApplication of biochar in agricultural lands is considered as a potential solution to prevent loss of fertilizers to water bodies and enhance soil quality by improving soil organic carbon, and hence improving agricultural productivity.
“Application of biochar in agricultural lands is considered as a potential solution to prevent loss of fertilizers to water bodies and enhance the soil quality by improving the soil organic carbon, and hence improving agricultural productivity [3].”
Quote in the paperSubstantial claim0 of 1 sources checked- cites [3] Aller, 2018, Long Term Biochar Effects on Corn Yield, Soil Quality and Profitability in the Us Midwest, Field Crops Res. source
Probably not a substantial claim: may not pass S3 (load-bearing).
Study design and conductcitationThe LCIA was performed using the TRACI 2.1 methodology.
“LCIA was performed using the Tools for the Reduction and Assessment of Chemical and other Environmental Impacts (TRACI) 2.1 methodology [36].”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites [36] US-EPA (2012). Tool for the Reduction and Assessment of Chemical and Other Environmental Impacts (Traci)–Traci Version 2.1 User’s Guide.
Not checked in the free run.
May combine two claims.
PremisecitationConversion of forest residues to biochar reduces the need for controlled pile and burning of forest residues, which causes air pollution and damages human health.
“It also reduces the need for controlled pile and burning of forest residues, which causes air pollution and damages human health [9].”
Quote in the paperSubstantial claim0 of 1 sources checked- cites [9] Berrill, 2017, Carbon, Harvest Yields, and Residues from Restoration in a Mixed Forest on California’s Coast Range, For. Sci. source
Probably not a substantial claim: may not pass S3 (load-bearing).
Study design and conductnone givenA sensitivity analysis was performed to estimate the impacts of variations in input parameters on the lifecycle assessment results and financial performance.
“A sensitivity analysis was performed to estimate the impacts of variations in input parameters on the lifecycle assessment results (i.e., GW impact) and financial performance (i.e., MSP).”
Quote in the paperNot a substantial claimMay combine two claims.
Interpretationown dataThe production of biochar pellets through the two portable systems and applied to fields can be both an environmentally beneficial and economically viable option.
“The results of the study conclude that the production of biochar pellets through the two portable systems and applied to fields can be both an environmentally beneficial and economically viable option.”
Quote in the paperSubstantial claimMay combine two claims.
Interpretationown dataThe 6% increase from pelletizing was due to emissions associated with high use of fuel in the diesel generator, about 71 kgCO2eq/tonne biochar.
“This was due to the emissions associated with the high use of fuel in the diesel generator, which was about 71 kgCO2eq/tonne biochar.”
Quote in the paperSubstantial claimClassified as probably not a substantial claim.
Study design and conductcitationThe LCA was conducted by following the ISO 14040 and ISO 14044 standards to quantify the environmental impacts of biochar production systems.
“LCA was conducted by following the ISO 14040 and ISO 14044 standards [31,32] to quantify the environmental impacts of biochar production systems.”
Quote in the paperSubstantial claim0 of 2 sources checked- cites [31] ISO (2006). Environmental Management: Life Cycle Assessment; Principles and Framework, International Organization for Standardization.
Not checked in the free run.
- cites [32] ISO (2006). Environmental Management: Life Cycle Assessments: Requirements and Guidelines, International Standardization Organization.
Not checked in the free run.
May combine two claims.
Interpretationown dataThe BSI system was revealed to be a more viable option in terms of GW impact, whereas the ACB system can produce biochar with lower MSP.
“Thus, the BSI system was revealed to be a more viable option in terms of GW impact, whereas the ACB system can produce biochar with lower MSP.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationFrom previous studies, the MSP of biochar production has been reported to be 838-1504 USD/tonne [41], and 774-1256 USD/tonne [42], depending on temperature, conversion rates, feedstock type, and price.
“From previous studies, the MSP of biochar production has been reported to be 838-1504 USD/tonne [41], and 774-1256 USD/tonne [42], depending on temperature, conversion rates, feedstock type, and price.”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites [41] Campbell, 2018, Financial Viability of Biofuel and Biochar Production from Forest Biomass in the Face of Market Price Volatility and Uncertainty, Appl. Energy source
- cites [42] Cheng, 2020, Slow Pyrolysis as a Platform for Negative Emissions Technology: An Integration of Machine Learning Models, Life Cycle Assessment, and Economic Analysis, Energy Convers. Manag. source
Classified as probably not a substantial claim.
InterpretationreasoningConsidering the vast area of forests requiring restoration, the BSI system would be considered the best option given its lower GW profile, costs, and MSP.
“Considering the vast area of forests requiring restoration, the BSI system would be considered the best option given its lower GW profile, costs, and MSP.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing), S4 (based).
Interpretationnone givenThese costs can be offset by incorporating United States Department of Agriculture Conservation Stewardship Program practices (e.g., E384135X).
“However, these costs can be offset by incorporating United States Department of Agriculture Conservation Stewardship Program practices (e.g., E384135X).”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationThe State of Washington has a financial incentive of 12,000 USD/ha [43], which would result in negative MSPs [26] for both BSI and ACB systems.
“For example, the State of Washington has a financial incentive of 12,000 USD/ha [43], which would result in negative MSPs [26] for both BSI and ACB systems.”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites [43] USDA-NRCS (2019). Conservation Enhancement Activity, E384135z.
Not checked in the free run.
- cites [26] Sahoo, 2021, Life-Cycle Assessment and Techno-Economic Analysis of Biochar Produced from Forest Residues Using Portable Systems, Int. J. Life Cycle Assess. source
The paper relies on this without support.
Biochar is often a dry powdery material that is difficult to handle and efficiently disperse.
“Biochar is often a dry powdery material that is difficult to handle and efficiently disperse.”
The paper relies on this without support.
The ACB system can process biomass with a wide range of moisture content.
“In addition, ACB can process biomass with a wide range of moisture content.”
The authors state this as an assumption.
All labile carbon and a certain part of recalcitrant carbon in biochar will degrade within a 100-year time-frame.
“This study considered that all labile carbon and a certain part of recalcitrant carbon in biochar will degrade within a 100-year time-frame [37].”
The authors state this as an assumption.
In this study, biochar pellets are assumed to be transported for further distances.
“as assumed in this study”
The paper relies on this without support.
Biochar provides long-term storage for carbon that originated from trees pulling carbon dioxide from the atmosphere; when biochar is added to the soil, carbon sinks are formed and carbon sequestration occurs.
“Furthermore, biochar can provide long-term storage for carbon that originated from trees pulling carbon dioxide from the atmosphere; thus, when biochar is added to the soil, carbon sinks, artificial reservoirs for accumulation of carbon dioxide, are formed and carbon sequestration occurs.”
The paper relies on this without support.
There are several other environmental benefits of making biochar and applying it to the field, including increasing soil quality and productivity.
“In addition, there are several other environmental benefits of making biochar and applying it to the field, which include increasing soil quality and productivity.”
Self-check
Percentages, sums and reported differences re-computed from the paper’s own numbers.
Each contradiction between two passages listed here was confirmed by an independent check.
ACB feedstock costs are substantial when forest operations are excluded, despite a stated zero feedstock price
MajorThe results assign 20-27% of costs to feedstocks in ACB scenarios 1 and 3, which exclude forest operations. The logistics-cost section says ACB feedstock costs zero under that exclusion, and the methods exclude ACB feedstock transport and preprocessing.
“About 20-27% (scenarios 1 and 3) and 52-60% (scenarios 2 and 4) were due to feedstocks in scenarios where the forest operations were excluded and included, respectively.”
“For ACB, the price of feedstock was either 0 or 16.5 USD/ODT based on excluding and including the cost incurred in forest operations of pulp logs.”
Final recommendation attributes lower MSP to BSI instead of ACB
MajorThe final recommendation calls BSI the lower-MSP option, contradicting the paper's reported MSP ranges and its preceding conclusion that ACB has the lower MSP.
“Considering the vast area of forests requiring restoration, the BSI system would be considered the best option given its lower GW profile, costs, and MSP.”
“In addition, biochar production through the ACB system had lower MSP compared to that of BSI (528-1051 vs. 1674-1909 USD/tonne biochar).”
Economic figures use 100 operating days despite a 300-day financial assumption
MajorThe financial analysis assumes 300 operating days annually, but the caption for the BSI annual-cost and MSP figure says 100 days. The ACB economic figure carries the same 100-day note.
“The analysis assumed that both portable systems operated 16 h/day (2 shifts × 8 h/shift) for 300 days annually.”
“Figure 6.Annual cost and minimum selling price of biochar production, in pellet and bulk forms, through BSI portable system, by considering the impact of forest operations.Note: annual operating time was considered to be 100 days.”
ACB pelletizing additions do not sum to the stated operating-cost increase
MinorThe three ACB additions shown in Table 6 total USD 54,406 per year, rather than the USD 53,364 added to its total operating cost.
Reported 53364 · recomputed 54406
“| Total operating cost | USD/year | 223,284 (+477) | 436,696 (+53,364) | |”
Outbound transport distances differ between LCA and cost calculations
MinorThe lifecycle inventory uses a 50 km trip to the application site, whereas the outbound logistics cost assumes 160 km one-way. The paper presents both for delivery of biochar without identifying them as different scenarios.
“The transportation distance was considered to be 50 km (Table 3).”
“Assuming the 4 h transportation time (one-way travel for a distance of 160 km), the outbound logistics costs of biochar as bulk and pellets were 42.35 USD/ODT and 19.8 USD/ODT, respectively.”
Conclusion says pelletizing lowers overall GW impacts, but ACB pelletizing raises them
MinorThe conclusion applies a reduction in overall GW impacts to biochar pelletizing, while the results explicitly report an increase for the ACB system.
“In addition, conversion of biochar to pellets was found to reduce the overall GW impacts and MSP of biochar production.”
“Contrary to the BSI system, pelletizing increased the cradle-to-grave GW impacts by 6%.”
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InfluentialThe feasibility and costs of biochar deployment in the UK
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Self-citationSahoo, K., Bilek, E., Bergman, R., & Mani, S. (2019) · Applied Energy · doi:10.1016/j.apenergy.2018.10.076 · Cited by 209 · see citing works
Self-citationCornelissen, G., Pandit, N., Taylor, P., Pandit, B., Sparrevik, M., & Schmidt, H. (2016) · PLoS ONE · doi:10.1371/journal.pone.0154617 · Cited by 179 · cited 1× · see citing works
“Data related to emissions for the BSI and ACB systems were taken from [24,35], respectively.”
MethodSahoo, K., Upadhyay, A., Runge, T., Bergman, R., Puettmann, M., & Bilek, E. (2021) · The International Journal of Life Cycle Assessment · doi:10.1007/s11367-020-01830-9 · Cited by 144 · cited 9× · see citing works
“For example, the State of Washington has a financial incentive of 12,000 USD/ha [43], which would result in negative MSPs [26] for both BSI and ACB systems.”
InfluentialSelf-citationLife cycle assessment of biochar produced from forest residues using portable systems
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The Economics of Biomass Logistics and Conversion Facility Mobility: An Oregon Case Study
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“Tractor 1 15,000 10 20% Biochar production 2 340,000 10 20% machine Pelletizer [39] 1 19,899 10 20% Gasifer genset 2 25,000 10 10% BSI: Biochar (bulk) production system 1 745,000 BSI: Biochar pellet production system 2 764,899”
Self-citationStrategies for Reducing Moisture Content in Forest Residues at the Harvest Site
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Performance and Emissions Control of Commercial-Scale Biochar Production Unit
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“223,284 436,696 Total operating cost USD/year (+477) (+53,364) † Consumables for BSI system included the fuel (5060 USD/year) used in the frontend loader (17 kW) for handling feedstocks [4], supplemental propane (920 USD/year) used to ignite the daily initial feedstock in the reactor and faring in the emission control…”
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Method(2016) · Cited by 4 · see citing works
Self-citation
Flagged first, then by citations
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Osman, A. I., Farghali, M. R. F., Ihara, I., Elgarahy, A. M., Ayyad, A., Mehta, N., Ng, K. H., El-Monaem, E. M. A., Eltaweil, A. S., Hosny, M., et al. (2023) · Environmental Chemistry Letters · doi:10.1007/s10311-023-01573-7 · Cited by 232 · see citing works
Ravindiran, G., Sivarethinamohan, R., Janardhan, G., Hayder, G., Alagumalai, A., Mahian, O., Lam, S. S., & Sonne, C. (2024) · Biochar · doi:10.1007/s42773-024-00350-1 · Cited by 205 · see citing works
Hassan, M., Mohanty, A. K., & Misra, M. (2023) · Materials & Design · doi:10.1016/j.matdes.2023.112558 · Cited by 146 · see citing works
Environmental impacts and techno-economic assessments of biobased products: A review
Mousavi‐Avval, S. H., Sahoo, K., Nepal, P., Runge, T. M., & Bergman, R. D. (2023) · Renewable and Sustainable Energy Reviews · doi:10.1016/j.rser.2023.113302 · Cited by 80 · see citing works
Self-citationLife cycle assessment of biochar for sustainable agricultural application: A review
Li, J., Sun, W., Lichtfouse, É., Maurer, C., & Liu, H. (2024) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2024.175448 · Cited by 67 · see citing works
Saharudin, D. M., Jeswani, H. K., & Azapagic, A. (2024) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2024.170266 · Cited by 61 · see citing works
Pristine and engineered biochar as Na-ion batteries anode material: A comprehensive overview
Bartoli, M., Piovano, A., Elia, G. A., Meligrana, G., Pedraza, R., Pianta, N., Tealdi, C., Pagot, G., Negro, E., Triolo, C., et al. (2024) · Renewable and Sustainable Energy Reviews · doi:10.1016/j.rser.2024.114304 · Cited by 52 · see citing works
Kavindi, G. A. G., Tang, L., & Sasaki, Y. (2024) · Resources Conservation and Recycling · doi:10.1016/j.resconrec.2024.107900 · Cited by 47 · see citing works
A comprehensive review of the production, adoption and sustained use of biomass pellets in Ghana
Mawusi, S. K., Shrestha, P., Xue, C., et al. (2023) · Heliyon · doi:10.1016/j.heliyon.2023.e16416 · Cited by 35 · see citing works
“[124] reported that the high cost of labor and equipment impacted the production of wood”
BackgroundTechno-economic analysis of microwave pyrolysis of sugarcane bagasse biochar production
Mari Selvam, S., Balasubramanian, P., Chintala, M., et al. (2024) · Biomass Conversion and Biorefinery · doi:10.1007/s13399-024-06232-7 · Cited by 35 · see citing works
Prochnow, F. D., Cavali, M., Dresch, A. P., Belli, I. M., Libardi, N., & de Castilhos, A. B. (2024) · Processes · doi:10.3390/pr12051006 · Cited by 33 · see citing works
Drupitha, M. P., Misra, M., & Mohanty, A. K. (2023) · Environmental Science Advances · doi:10.1039/d3va00107e · Cited by 33 · see citing works
“32,33 The economic feasibility of biochar production was investigated using forest residues as feedstock in a small-scale portable machine.”
Yao, Y., & Zhang, B. (2025) · Environmental Science & Technology · doi:10.1021/acs.est.4c09510 · Cited by 33 · see citing works
O'Boyle, M., Mohamed, B. A., & Li, L. Y. (2023) · Chemosphere · doi:10.1016/j.chemosphere.2023.141074 · Cited by 25 · see citing works
Roy, P., Rodriguez‐Uribe, A., Mohanty, A. K., Pujari, D., Tiessen, M., Bali, A., & Misra, M. (2024) · Sustainability · doi:10.3390/su16135633 · Cited by 24 · see citing works
Mawusi, S. K., Shrestha, P., Gao, T., Liu, M., Li, Z., Jiao, M., Li, Y., Yan, M., Li, C., Xue, C., et al. (2022) · Energy Sustainable Development/Energy for sustainable development · doi:10.1016/j.esd.2022.12.011 · Cited by 22 · see citing works
Baniasadi, H., Äkräs, L., Paganelli, Z., Dammann, N., Abidnejad, R., Lipponen, S., Silvenius, F., Vahvaselkä, M., Ilvesniemi, H., Seppälä, J. V., et al. (2025) · Environmental Research · doi:10.1016/j.envres.2025.121446 · Cited by 22 · see citing works
Desjardins, S. M., Ter‐Mikaelian, M. T., & Chen, J. (2024) · Biochar · doi:10.1007/s42773-024-00352-z · Cited by 19 · see citing works
“Perhaps high cost (Sahoo et al. 2019; Bergman et al. 2022) is causing portable pyrolysis systems to remain in their infancy as demonstrated by the shortage of relevant literature.”
Varthan, M. K. H., Keerthana, V. S., Saravanan, A., Deivayanai, V. C., Kumar, R., Raveendran, S. K., Ahmed, Z. H. T., Indumathi, S. M., & Prakash, P. (2025) · Fuel · doi:10.1016/j.fuel.2025.136599 · Cited by 18 · see citing works
Biochar as a sustainable alternative to carbon black in agricultural mulch films
Hernandez-Charpak, Y. D., Mozrall, A. M., Williams, N. J., et al. (2023) · Environmental Research · doi:10.1016/j.envres.2023.117916 · Cited by 15 · see citing works
Ahmed, N. N., Pokharel, R., Miesel, J., & Saffron, C. M. (2025) · GCB Bioenergy · doi:10.1111/gcbb.70030 · Cited by 13 · see citing works
“Bergman et al. (2022) reported the annual cost of relocating one portable unit to be $23,568 when units relocate twice a year.”
InfluentialGoldáraz-Salamero, N., Baima, L., Moles, S., Sierra-Pérez, J., Martínez, I. C., Murillo, R., Brun, F., & Blanc, S. (2025) · Bioresource Technology · doi:10.1016/j.biortech.2025.132772 · Cited by 13 · see citing works
Katarov, V., Syunev, V. S., & Kolesnikov, G. (2022) · Forests · doi:10.3390/f13101538 · Cited by 13 · see citing works
Khatri, P., Bergman, R. D., Nepal, P., Nicholls, D., & Gray, A. N. (2025) · Biomass and Bioenergy · doi:10.1016/j.biombioe.2025.108059 · Cited by 12 · see citing works
Self-citationNandikes, G., Anh, N. T. V., Siddiqui, S. I., et al. (2025) · Journal of Industrial and Engineering Chemistry · doi:10.1016/j.jiec.2025.02.047 · Cited by 12 · see citing works
Wibowo, Y. G., Anwar, D., Safitri, H., Setiawan, A., Supriyatna, Y. I., Sudibyo, Yuliansyah, A. T., & Petrus, H. T. B. M. (2025) · Bioresource Technology Reports · doi:10.1016/j.biteb.2025.102034 · Cited by 9 · see citing works
Rezvani, B. (2025) · The Canadian Journal of Chemical Engineering · doi:10.1002/cjce.25702 · Cited by 9 · see citing works
Life Cycle Assessment of Biochar: A Bibliometric Analysis of Trends and Future Perspectives
Admas, B. F., Moura, L. C., Gashaw, T., Silva, D. V., Melo, R. L. F., & do Carmo, F. R. (2026) · BioEnergy Research · doi:10.1007/s12155-026-10959-8 · Cited by 8 · see citing works
Desjardins, S. M., Ter‐Mikaelian, M. T., & Chen, J. (2025) · ACS Sustainable Resource Management · doi:10.1021/acssusresmgt.4c00263 · Cited by 7 · see citing works
Developing a framework towards global biochar supply chains to optimize regional production cost
Kern, J., Abdelshafy, A., & Walther, G. (2025) · Environmental Technology & Innovation · doi:10.1016/j.eti.2025.104658 · Cited by 7 · see citing works
Ghosh, D., Anderson, N., & Han, H. (2025) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2025.147269 · Cited by 7 · see citing works
Hazbawi, I. (2026) · Results in Engineering · doi:10.1016/j.rineng.2026.110039 · Cited by 7 · see citing works
Nahuat-Sansores, J. R., Cruz, J. C., Gurrola, M. P., & Trejo-Arroyo, D. L. (2022) · Revista de Ingeniería Civil · doi:10.35429/jce.2022.16.6.12.31 · Cited by 6 · see citing works
Samsudin, M. H., Yusoff, M. Z. M., Roslan, A. M., Hassan, M. A., Idris, J., Farid, M. A. A., & Shirai, Y. (2025) · Environmental Science and Pollution Research · doi:10.1007/s11356-025-36859-6 · Cited by 5 · see citing works
“This basic concept resonated with the conclusion reported, revealing that pilot-scaled production rates are a major determinant of biochar economics (Bergman et al. 2022; Nematian et al. 2021).”
Zheng, Y., Zhou, Z., Han, F., Fu, J., & Yu, C. (2025) · Environmental chemistry and safety · doi:10.26599/ecs.2025.9600011 · Cited by 5 · see citing works
Gavrilaş, S., Chereji, B.-D., & Munteanu, F. (2026) · Processes · doi:10.3390/pr14071076 · Cited by 6 · see citing works
Robert, É., & Braghiroli, F. L. (2022) · Clean Technologies · doi:10.3390/cleantechnol4030047 · Cited by 5 · see citing works
Towards a Bioeconomy: Supplying Forest Residues for the Australian Market
Garvie, L. C., Lee, D. J., & Kulišić, B. (2024) · Energies · doi:10.3390/en17020397 · Cited by 4 · see citing works
Azizpanah, A., Namdari, M., & Abed, A. K. (2025) · Results in Engineering · doi:10.1016/j.rineng.2025.106380 · Cited by 4 · see citing works
CO2 sequestration for conventional utilization and industrial application
Shammi, M., & Akter, B. (2024) · Elsevier eBooks · doi:10.1016/b978-0-443-13607-8.00011-0 · Cited by 3 · see citing works
Beljin, J., Isakovski, M. K., Rončević, S. D., et al. (2025) · Journal of Hazardous Materials Advances · doi:10.1016/j.hazadv.2025.100874 · Cited by 3 · see citing works
Wu, W., & Zhai, H. (2026) · International journal of greenhouse gas control · doi:10.1016/j.ijggc.2026.104653 · Cited by 4 · see citing works
Characterization of Hemp Hurd-Derived Biochar for Potential Agricultural Applications
Assirelli, A., Fischetti, E., Scarfone, A., Santangelo, E., Carnevale, M., Paris, E., Palma, A., & Gallucci, F. (2025) · Agronomy · doi:10.3390/agronomy15092136 · Cited by 5 · see citing works
Adam, R., Kirsten, C., Schedl, A. E., et al. (2025) · Renewable Energy · doi:10.1016/j.renene.2025.124511 · Cited by 2 · see citing works
Assessing biomass carbon dioxide removal supply chains: System modelling and economic assessment
Grimm, V., Niazmand, K., & Runge, P. (2025) · Renewable and Sustainable Energy Reviews · doi:10.1016/j.rser.2025.116298 · Cited by 2 · see citing works
Le, L. B., Nguyen, B. T., & Dinh, T. D. (2026) · Water Air & Soil Pollution · doi:10.1007/s11270-026-09109-9 · Cited by 3 · see citing works
“Logistical constraints— including the labor-intensive transport and field application of BC—further restrict its widespread use (Bergman et al., 2022).”
Solórzano, R., Damián, L., Herrera, S., PICHIS-GARCÍA, R. A. H., Cabello-Torres, R., Padilla-Castro, C., Arias-Arredondo, A. G., Chávez, A., & Vallejos-Torres, G. (2026) · Frontiers in Agronomy · doi:10.3389/fagro.2026.1787188 · Cited by 2 · see citing works
Biochar for environmental remediation at a glance: principles, applications, and prospects
Gwenzi, W. (2025) · Elsevier eBooks · doi:10.1016/b978-0-323-99889-5.00001-3 · Cited by 2 · see citing works
Pretreatment strategies for woody biomass
Sharma, S. G., & Arora, R. (2023) · Elsevier eBooks · doi:10.1016/b978-0-323-91187-0.00008-4 · Cited by 1 · see citing works
Adopting Biochar as Immobilization Support for Hyper Ammonia-Producing Bacteria Proliferation
Bitrus, C., Hammed, A., Ayodele, T. O., Alarape, K., Sarker, N. C., Clementson, C., & Monono, E. (2025) · Applied microbiology · doi:10.3390/applmicrobiol5040111 · Cited by 1 · see citing works
“From an economic perspective, HAB–biochar systems may be particularly advantageous for organic production, where higher premiums on inputs can offset processing costs [47–49].”
Mashiat, I., Prodhan, A. A. A., Alam, M. M., Rahman, M. M., Bhuiyan, M. K. H., & Fakir, M. K. H. (2026) · Carbon Trends · doi:10.1016/j.cartre.2026.100651 · Cited by 1 · see citing works
Engstam, L., Bulkan, G., Janke, L., Sundberg, C., & Nordberg, Å. (2026) · International Journal of Hydrogen Energy · doi:10.1016/j.ijhydene.2026.156625 · Cited by 1 · see citing works
Kant, R. (2026) · Bioresource Technology Reports · doi:10.1016/j.biteb.2026.102974 · Cited by 1 · see citing works
Gwenzi, W. (2025) · Elsevier eBooks · doi:10.1016/b978-0-323-99889-5.00024-4 · Cited by 1 · see citing works
Acosta, R. A. S., Damián, L., Herrera, S., et al. (2025) · Research Square · doi:10.21203/rs.3.rs-6857389/v1
Ni, L., Huang, A., He, Y., Feng, X., Zhong, Y., Liu, S., Chen, C., Liu, Z., & Zhao, J. (2026) · Energy · doi:10.1016/j.energy.2026.140020
Progress in Degradation of Volatile Organic Compounds by Biochar Fillers
Qu, M., Zhou, R., Cheng, Z., et al. (2026) · Water Air & Soil Pollution · doi:10.1007/s11270-026-09204-x
“Several TEA and LCA (Bergman et al., 2022; Mishra et al., 2023; Schoor et al., 2025) studies demonstrate that when co-benefits such as waste management savings, emission reduction, and extended service life are incorporated, biochar-based systems can achieve competitive or superior cost–performance ratios compared wit…”
InfluentialCutting Edge Innovations: New Approach of Developments in Biochar Technology
Pal, G., & Madhurangi, B. L. N. K. (2026) · Springer eBooks · doi:10.1007/978-3-032-16746-0_11
Techno-economic analysis of biochar in water treatment
Manikandan, S. K., Nandini, I. V., & Nair, V. (2026) · Elsevier eBooks · doi:10.1016/b978-0-443-29865-3.00011-x
Technoeconomic and life cycle assessment of biochar applications for wastewater treatment
Manga, M., Muoghalu, C., Ekyalimpa, R., Patrick, J., & Kaboggoza, H. C. (2026) · Elsevier eBooks · doi:10.1016/b978-0-443-44581-1.00003-x
Sustainable energy transitions through biomass pelleting: policy levers for carbon neutrality
Rahman, M. M., & Ciolkosz, D. E. (2026) · Frontiers in Sustainability · doi:10.3389/frsus.2026.1790793
Bhattacharyya, P. N., Paul, B., Sarma, B., Al‐Ani, L. K. T., Handique, L., Gogoi, P., Sarma, R. K., & Dastagir, M. R. (2026) · Nanotechnology in the life sciences · doi:10.1007/978-981-92-2405-0_4
Economic Risk Modeling in Forestry Projects Using Harvesting and Transportation Cost Variables
de Freitas, L. C., da Silva, M. L., Ferreira, F. D. A. C., et al. (2026) · Forests · doi:10.3390/f17070846
“According to Bergman et al. (2022) [42], productive forest sites tend to reduce economic risk because higher yields dilute operational costs per unit of wood produced.”
Techno-Economic Feasibility of Biochar Production from Local Biomass Resources in Qatar: A Review
Fouladi, S., Mahmoud, K. A., Al‐Ansari, T. A., et al. (2026) · Resources Conservation & Recycling Advances · doi:10.1016/j.rcradv.2026.200370
Acorn review: Biochar and its applications in US forestry
Dhungel, G., Baker, J. S., Henderson, J. D., & Cook, R. L. (2026) · Forest Ecology and Management · doi:10.1016/j.foreco.2026.124134
Yaghoubi, M., Tabatabaei, S. H., Shadnia, R., & Raiesi, T. (2026) · International Journal of Environmental Science and Technology · doi:10.1007/s13762-026-07377-w
“Life cycle assessment (LCA) studies indicate that biochar production via pyrolysis generates 306–1016 kg CO 2 -eq per tonne, with pyrolysis energy consumption and transportation identified as the primary contributors to the carbon footprint (Bergman et al. 2022; Saleem et al. 2026).”
Li, Z., Nabhai, A., Sheets, C., et al. (2026) · ACS Applied Bio Materials · doi:10.1021/acsabm.6c01027
Kumar, B., & Cabezas, H. (2026) · Energies · doi:10.3390/en19173950
Zhao, Z., Wu, S., Liu, Y., & Cao, Y. (2026) · Fuel · doi:10.1016/j.fuel.2026.141225
Chambers, C., Abrar, M. F., Grimes, S., et al. (2026) · Next Sustainability · doi:10.1016/j.nxsust.2026.100524
Greenhouse gas and economic assessments of biochar-based composite panels from forest residues
Aguirre‐Villegas, H. A., Bergman, R. D., Yan, Q., Zhiyong, C., Nepal, P., & Runge, T. M. (2026) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2026.149483
Self-citationRevisiting Biochar Production Technologies: A Multifaceted Tool for Environmental Sustainability
Negi, B., Nath, Y., Rai, M., Bhatnagar, P., Edrisi, S. A., Hukum, S., Gururani, P., & Tripathi, V. (2026) · Water Air & Soil Pollution · doi:10.1007/s11270-026-09988-y
“While biochar systems can achieve net negative emissions, potential trade-offs related to energy consumption, emissions during processing, and feedstock contamination must be considered (Bergman et al., 2022).”
Guimarães, D. P. D. S., Carneiro, A. D. C. O., Ucella-Filho, J. G. M., Abreu, E. L., Evangelista, E. L. C., Torres, F. T. P., & Abranches, G. F. (2026) · Biomass Conversion and Biorefinery · doi:10.1007/s13399-026-07281-w
Modified biochars for sustainable wastewater treatment: A critical review
Uddin, M. R., & Juneja, A. (2026) · Chemical Engineering Journal Green and Sustainable · doi:10.1016/j.cejgas.2026.100142
- Authors
- Bergman, R., Sahoo, K., Englund, K., & Mousavi-Avval, S. H.
- Affiliations
- Forest Products Laboratory (US)
- University of Wisconsin–Madison (US)
- Washington State University (US)
- Forest Products Laboratory, United States Forest Service, 1 Gifford Pinchot Drive, Madison, WI 53726, USA
- Corresponding author
- Bergman, Richard
- Venue
- Energies
- Publisher
- MDPI AG
- Published
- 2022-02-20
- Volume
- 15
- Issue
- 4
- Pages
- 1559
- ISSN
- 1996-1073 (ISSN-L)
- OpenAlex
- W4213068390
- Semantic Scholar
- b5a4703ea85d34fb22baf59fe29f71f47f0c9e1e
- Cited by
- 75
- References
- 34
- Citations by year
- 2026: 28 · 2025: 23 · 2024: 12 · 2023: 8 · 2022: 4
- FWCI
- 3.18
- Type
- journal article
- Language
- en
- Open access
- gold
- doi.org
- Licence
- Locations
- Energies (publishedVersion, cc-by)
- RePEc: Research Papers in Economics (submittedVersion)
- DOAJ (DOAJ: Directory of Open Access Journals) (submittedVersion, cc-by-sa)
- OSTI OAI (U.S. Department of Energy Office of Scientific and Technical Information) (submittedVersion)
- Funders
- National Institute of Food and Agriculture (2020-68012-31881, 2011-10006-30357)
- United States Department of Energy (DE-EE0006297)
- U.S. Endowment for Forestry & Communities, Inc., Endowment Green Building Partnership—Phase 1 (18-JV-11111137-021)
- Topics
- Physical Sciences › Engineering › Biomedical Engineering › Thermochemical Biomass Conversion Processes
- Physical Sciences › Engineering › Mechanics of Materials › Forest Biomass Utilization and Management
- Life Sciences › Agricultural and Biological Sciences › Forestry › Agricultural and Food Sciences
- Keywords
- forest residues, biochar production, pelletization, global warming potential, minimum selling price, techno-economic feasibility, wildfire mitigation, Pacific Northwest
About these checks
Registry, retraction, Cites and statistics results are computed, not judged, with one exception: a printed reference that no index lists is read once by a model before it counts as a citation error. Claims are extracted by a model and kept only when their quote appears verbatim in the text; each cited source is then checked, with a model’s help, for whether it says what the claim relies on. Those verdicts can be wrong — read the claim’s quote and the cited source before relying on one.
Claims read by deepseek-v4.1-flash under definition version 3 (extract-v3) on 2026-10-23.
Classified by jev-1.13-20260917 (gold-guideline-v0.2) on 2026-10-23.
Cited sources are checked by gpt-6-sol.
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