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Enhanced methane production from cellulose using a two-stage process involving a bioelectrochemical system and a fixed film reactor.

作者信息

Sasaki Kengo, Sasaki Daisuke, Tsuge Yota, Morita Masahiko, Kondo Akihiko

机构信息

Graduate School of Science, Technology and Innovation, Kobe University, 1-1 Rokkodaicho, Nada-ku, Kobe, Hyogo, 657-8501, Japan.

Institute for Frontier Science Initiative, Kanazawa University, Kakuma-machi, Kanazawa, Ishikawa, 920-1192, Japan.

出版信息

Biotechnol Biofuels. 2021 Jan 6;14(1):7. doi: 10.1186/s13068-020-01866-x.


DOI:10.1186/s13068-020-01866-x
PMID:33407783
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC7789537/
Abstract

BACKGROUND: It is desirable to improve the anaerobic digestion processes of recalcitrant materials, such as cellulose. Enhancement of methane (CH) production from organic molecules was previously accomplished through coupling a bioelectrochemical system (BES); however, scaling-up BES-based production is difficult. Here, we developed a two-stage process consisting of a BES using low-cost and low-reactive carbon sheets as the cathode and anode, and a fixed film reactor (FFR) containing conductive material, i.e., carbon fiber textiles (CFTs) (:BES → FFR). By controlling the cathodic current at 2.7 μA/cm without abiotic H production, the three-electrode BES system was operated to mimic a microbial electrolysis cell. RESULTS: The thermophilic BES (inlet pH: 6.1) and FFR (inlet pH: 7.5) were operated using hydraulic retention times (HRTs) of 2.5 and 4.2 days, respectively, corresponding to a cellulose load of 3555.6 mg-carbon (C)/(L day). The BES → FFR process achieved a higher CH yield (37.5%) with 52.8 vol% CH in the product gas compared to the non-bioelectrochemical system (NBES) → FFR process, which showed a CH yield of 22.1% with 46.8 vol% CH. The CH production rate (67.5 mM/day) obtained with the BER → FFR process was much higher than that obtained using electrochemical methanogenesis (0.27 mM/day). Application of the electrochemical system or CFTs improved the yields of CH with the NBES → FFR or BES → non-fixed film reactor process, respectively. Meta 16S rRNA sequencing revealed that putative cellulolytic bacteria (identified as Clostridium species) were present in the BES and NBES, and followed (BES→ and NBES→) FFR. Notably, H-consuming methanogens, Methanobacterium sp. and Methanosarcina sp., showed increased relative abundances in the suspended fraction and attached fraction of (BES→) FFR, respectively, compared to that of (NBES→) FFR, although these methanogens were observed at trace levels in the BES and NBES. CONCLUSIONS: These results indicate that bioelectrochemical preprocessing at a low current effectively induces interspecies H transfer in the FFR with conductive material. Sufficient electrochemical preprocessing was observed using a relatively short HRT. This type of two-stage process, BES → FFR, is useful for stabilization and improvement of the biogas (CH) production from cellulosic material, and our results imply that the two-stage system developed here may be useful with other recalcitrant materials.

摘要
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e9f9/7789537/74e89b7a0464/13068_2020_1866_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e9f9/7789537/ebe0b044459a/13068_2020_1866_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e9f9/7789537/6a6567fe06c6/13068_2020_1866_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e9f9/7789537/cf7f88575abd/13068_2020_1866_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e9f9/7789537/f09773e823da/13068_2020_1866_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e9f9/7789537/74e89b7a0464/13068_2020_1866_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e9f9/7789537/ebe0b044459a/13068_2020_1866_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e9f9/7789537/6a6567fe06c6/13068_2020_1866_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e9f9/7789537/cf7f88575abd/13068_2020_1866_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e9f9/7789537/f09773e823da/13068_2020_1866_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e9f9/7789537/74e89b7a0464/13068_2020_1866_Fig5_HTML.jpg

相似文献

[1]
Enhanced methane production from cellulose using a two-stage process involving a bioelectrochemical system and a fixed film reactor.

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[2]
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[5]
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[6]
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[7]
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[8]
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[9]
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[10]
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本文引用的文献

[1]
Bioelectrochemical system for the enhancement of methane production by anaerobic digestion of alkaline pretreated sludge.

Bioresour Technol. 2020-2-12

[2]
Elucidating Syntrophic Butyrate-Degrading Populations in Anaerobic Digesters Using Stable-Isotope-Informed Genome-Resolved Metagenomics.

mSystems. 2019-8-6

[3]
Electroactive microorganisms in bioelectrochemical systems.

Nat Rev Microbiol. 2019-5

[4]
Impact of biochar-supported zerovalent iron nanocomposite on the anaerobic digestion of sewage sludge.

Environ Sci Pollut Res Int. 2019-2-13

[5]
Exploring the roles of and interactions among microbes in dry co-digestion of food waste and pig manure using high-throughput 16S rRNA gene amplicon sequencing.

Biotechnol Biofuels. 2019-1-4

[6]
A Review of the Processes, Parameters, and Optimization of Anaerobic Digestion.

Int J Environ Res Public Health. 2018-10-11

[7]
Biodiversity-function relationships in methanogenic communities.

Mol Ecol. 2018-11-22

[8]
Interfacing anaerobic digestion with (bio)electrochemical systems: Potentials and challenges.

Water Res. 2018-9-12

[9]
Hydrogenotrophic Methanogenesis and Autotrophic Growth of .

Archaea. 2018-7-17

[10]
Changes in the microbial consortium during dark hydrogen fermentation in a bioelectrochemical system increases methane production during a two-stage process.

Biotechnol Biofuels. 2018-6-22

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