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Production routes to bio-acetic acid: life cycle assessment

BACKGROUND: Similar to biofuels, numerous chemicals produced from petroleum resources can also be made from biomass. In this research we investigate cradle to biorefinery exit gate life cycle impacts of producing acetic acid from poplar biomass using a bioconversion process. A key step in developing...

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Autores principales: Budsberg, Erik, Morales-Vera, Rodrigo, Crawford, Jordan T., Bura, Renata, Gustafson, Rick
Formato: Online Artículo Texto
Lenguaje:English
Publicado: BioMed Central 2020
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7469289/
https://www.ncbi.nlm.nih.gov/pubmed/32905422
http://dx.doi.org/10.1186/s13068-020-01784-y
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author Budsberg, Erik
Morales-Vera, Rodrigo
Crawford, Jordan T.
Bura, Renata
Gustafson, Rick
author_facet Budsberg, Erik
Morales-Vera, Rodrigo
Crawford, Jordan T.
Bura, Renata
Gustafson, Rick
author_sort Budsberg, Erik
collection PubMed
description BACKGROUND: Similar to biofuels, numerous chemicals produced from petroleum resources can also be made from biomass. In this research we investigate cradle to biorefinery exit gate life cycle impacts of producing acetic acid from poplar biomass using a bioconversion process. A key step in developing acetic acid for commercial markets is producing a product with 99.8% purity. This process has been shown to be potentially energy intensive and in this work two distillation and liquid–liquid extraction methods are evaluated to produce glacial bio-acetic acid. Method one uses ethyl acetate for extraction. Method two uses alamine and diisobutyl ketone. Additionally two different options for meeting energy demands at the biorefinery are modeled. Option one involves burning lignin and natural gas onsite to meet heat/steam and electricity demands. Option two uses only natural gas onsite to meet heat/steam demands, purchases electricity from the grid to meet biorefinery needs, and sells lignin from the poplar biomass as a co-product to a coal burning power plant to be co-fired with coal. System expansion is used to account for by-products and co-products for the main life cycle assessment. Allocation assessments are also performed to compare the life cycle tradeoffs of using system expansion, mass allocation, or economic allocation for bio-acetic acid production. Finally, a sensitivity analysis is conducted to determine potential effects of a decrease in the fermentation of glucose to acetic acid. RESULTS: Global warming potential (GWP) and fossil fuel use (FFU) for ethyl acetate extraction range from 1000–2500 kg CO(2) eq. and 32–56 GJ per tonne of acetic acid, respectively. Alamine and diisobutyl ketone extraction method GWP and FFU ranges from −370–180 kg CO(2) eq. and 15−25 GJ per tonne of acetic acid, respectively. CONCLUSIONS: Overall the alamine/diisobutyl ketone extraction method results in lower GWP and FFU values compared to the ethyl acetate extraction method. Only the alamine/diisobutyl extraction method finds GWP and FFU values lower than those of petroleum based acetic acid. For both extraction methods, exporting lignin as a co-product produced larger GWPs and FFU values compared to burning the lignin at the biorefinery.
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spelling pubmed-74692892020-09-03 Production routes to bio-acetic acid: life cycle assessment Budsberg, Erik Morales-Vera, Rodrigo Crawford, Jordan T. Bura, Renata Gustafson, Rick Biotechnol Biofuels Research BACKGROUND: Similar to biofuels, numerous chemicals produced from petroleum resources can also be made from biomass. In this research we investigate cradle to biorefinery exit gate life cycle impacts of producing acetic acid from poplar biomass using a bioconversion process. A key step in developing acetic acid for commercial markets is producing a product with 99.8% purity. This process has been shown to be potentially energy intensive and in this work two distillation and liquid–liquid extraction methods are evaluated to produce glacial bio-acetic acid. Method one uses ethyl acetate for extraction. Method two uses alamine and diisobutyl ketone. Additionally two different options for meeting energy demands at the biorefinery are modeled. Option one involves burning lignin and natural gas onsite to meet heat/steam and electricity demands. Option two uses only natural gas onsite to meet heat/steam demands, purchases electricity from the grid to meet biorefinery needs, and sells lignin from the poplar biomass as a co-product to a coal burning power plant to be co-fired with coal. System expansion is used to account for by-products and co-products for the main life cycle assessment. Allocation assessments are also performed to compare the life cycle tradeoffs of using system expansion, mass allocation, or economic allocation for bio-acetic acid production. Finally, a sensitivity analysis is conducted to determine potential effects of a decrease in the fermentation of glucose to acetic acid. RESULTS: Global warming potential (GWP) and fossil fuel use (FFU) for ethyl acetate extraction range from 1000–2500 kg CO(2) eq. and 32–56 GJ per tonne of acetic acid, respectively. Alamine and diisobutyl ketone extraction method GWP and FFU ranges from −370–180 kg CO(2) eq. and 15−25 GJ per tonne of acetic acid, respectively. CONCLUSIONS: Overall the alamine/diisobutyl ketone extraction method results in lower GWP and FFU values compared to the ethyl acetate extraction method. Only the alamine/diisobutyl extraction method finds GWP and FFU values lower than those of petroleum based acetic acid. For both extraction methods, exporting lignin as a co-product produced larger GWPs and FFU values compared to burning the lignin at the biorefinery. BioMed Central 2020-09-03 /pmc/articles/PMC7469289/ /pubmed/32905422 http://dx.doi.org/10.1186/s13068-020-01784-y Text en © The Author(s) 2020 Open AccessThis article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated in a credit line to the data.
spellingShingle Research
Budsberg, Erik
Morales-Vera, Rodrigo
Crawford, Jordan T.
Bura, Renata
Gustafson, Rick
Production routes to bio-acetic acid: life cycle assessment
title Production routes to bio-acetic acid: life cycle assessment
title_full Production routes to bio-acetic acid: life cycle assessment
title_fullStr Production routes to bio-acetic acid: life cycle assessment
title_full_unstemmed Production routes to bio-acetic acid: life cycle assessment
title_short Production routes to bio-acetic acid: life cycle assessment
title_sort production routes to bio-acetic acid: life cycle assessment
topic Research
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7469289/
https://www.ncbi.nlm.nih.gov/pubmed/32905422
http://dx.doi.org/10.1186/s13068-020-01784-y
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