Elsevier

Applied Energy

Volume 147, 1 June 2015, Pages 67-73
Applied Energy

Combination of dry dark fermentation and mechanical pretreatment for lignocellulosic deconstruction: An innovative strategy for biofuels and volatile fatty acids recovery

https://doi.org/10.1016/j.apenergy.2015.02.042Get rights and content

Highlights

  • A novel combination of solid-state fermentation and fine milling was developed.

  • Biological pretreatment produces valuable bioproducts (VFA and biohydrogen).

  • Solid-state dark fermentation improves considerably the milling efficiency.

  • Bioethanol yield was higher after a strong particle size reduction.

  • Substrate conversion was two times higher than conventional processes.

Abstract

In the present study, the feasibility of combining dry dark fermentation and mechanical pretreatment of wheat straw was studied in order to improve substrate valorization, save energy input, decrease the environmental impact and diversify biofuels and volatile fatty acids production. To this end, dark fermentation of wheat straw was performed at 55 °C and 35 °C under solid-state conditions (23% of total solid content) and it was considered as a biological pretreatment. Both biologically treated and raw straws were reduced at four particles size to cover the range of fine (50 < X < 500 μm) and ultrafine milling (<50 μm). Biological pretreatment led to a substrate conversion of 16% and 14%, mainly into volatile fatty acids and biohydrogen. Biological pretreatment improved the substrate grindability with a reduction of mean particle size up to 31% and a reduction of the milling specific energy consumption up to 35% compared to untreated straw. Finally, related to untreated straw, this combination of biological and mechanical treatments improved the bioethanol yield up to 83%, which leads to an enhancement of the overall substrate conversion up to 131%. Based on these high yields, this combination of dry biological–mechanical pretreatments appears more attractive and efficient in terms of bioproducts production, energy efficiency and environmental impact, compared to conventional pretreatments.

Introduction

Pretreatments of lignocellulosic biomass appeared to be critical stages for biorefinery development to improve transformation yields and rates. These processes aim to solubilize carbohydrates in order to enhance their conversion into biofuels (i.e. bioethanol and biogas). To date, different pretreatments have been investigated in literature, such as mechanical pretreatment (milling), thermal pretreatment (liquid hot water, steam explosion, CO2 explosion…), chemical pretreatment (acid, alkaline, oxidative…) or biological pretreatment (fungal, enzymes, fermentation) [1], [2]. The choice to use a single or a combination of pretreatments is often due to a compromise between carbohydrates solubilization efficiency, energy consumption and effluent management [3], [4]. Pretreatments that operated under dry conditions are particularly interesting, since they save energy and generate small quantity of effluent [5], [6]. Among them, strong particle size reduction is often considered as a process of interest for its ability to homogenize substrate, to reduce the cellulose crystallinity and to improve the carbohydrates solubilization [6], [7]. The application of fine (50 < X < 500 μm) and ultrafine (<50 μm) milling is particularly efficient to improve the enzymatic hydrolysis [8], [9] and consequently the bioethanol production from lignocellulosic substrates [10], [11]. However, the high energy consumption required to break the lignocellulosic structure [5], [7], [12] is generally considered as the main limiting factor for the application of mechanical pretreatments. Recently, combination of chemical and mechanical pretreatments have been proved to reduce the energy consumption of milling step and to maximize the efficiency of glucose release [9].

Solid-state biological processes that operate at a total solid (TS) content higher than 20%, have been recently applied for dark fermentation of lignocellulosic substrates [13], [14], [15]. Dark fermentation corresponds to the first step of the anaerobic digestion after inhibition of the methanogenic activity, and it conducts simultaneously to the production of high amount of hydrogen (H2) and valuable volatile fatty acids (VFA) [15], [16]. These organic acids, commonly acetic, propionic, butyric and lactic acids, have been investigated as precursors of various biotechnological applications: (1) for biodiesel production through the synthesis of single cell oils by oleaginous yeast [17]; (2) as substrate for microbial fuel cell [18]; (3) as external carbon source for the biological denitrification of wastewaters rich in nitrogen [19]; (4) as potential substrate for the production of hydrogen via photofermentation by mix microbial cultures [20]; (5) as the building blocks of various organic compounds including alcohols, aldehydes, ketones, esters and olefins [21] and (6) recently VFAs have been considered valuable substrates to produce bioplastics (i.e. poly-β-hydroxybutyrate, poly(hydroxy alcanoate)s) [22]. Dark fermentation can be considered as a substrate pretreatment due to a combination of both biological degradation and acidic conditions [13], [23]. To perform dark fermentation process, an anaerobic digestate is generally used as inoculum after inhibition of its methanogenic activity, induced for example by a thermal or an acid shock [16]. Nevertheless, acidification can be also easily induced under solid-state condition, reducing the amount of inoculum (i.e. with a substrate/inoculum ratio higher than 20) [24]. These fermentation conditions provide a solid fraction poor in water and sludge content, which do not require much treatment (cleaning) before further use of the lignocellulosic biomass.

The aim of this study was the development of a novel scheme of lignocellulosic biomass pretreatment to improve and diversify biofuels and volatile fatty acids production in a general concept of solid-state biorefinery. To this end, a combination of solid-state fermentation and fine milling was developed (Fig. 1). The different scenarios were tested and evaluated in term of biofuels (bio-hydrogen, methane and ethanol) yield, volatile fatty acids, and specific energy consumption.

Section snippets

Substrate characterization

Wheat straw (Triticum aestivum) was harvested during summer 2010 from a farm located in the south of France (Languedoc Roussillon Region, Herault department). A cutting mill (Retsch® SM100) equipped with a 10 mm grid, was used to grind straw coarsely. Total solids content (TS) was measured after drying sample at 105 °C during 48 h, while volatile solids (VS) was measured after 3 h of calcination at 550 °C. Substrate soluble fraction was assessed according to Van Soest extraction with a neutral

Solid-state biological pretreatment

Fig. 2 report the specific biogas production of straw under mesophilic and thermophilic conditions (BMT and BTT, respectively). In order to reach a complete transformation of the convertible fraction, the biological pretreatment was monitored during a longer time than the usual for dark fermentation processes (i.e. 64 days against 7-10 days as usual) [23]. Results revealed that, in all cases, about 50% of biogas were rapidly produced during the first 48 h, and that the 75% of biogas was produced

Conclusion

The feasibility of combining dry dark fermentation and mechanical pretreatment of wheat straw prior to bioethanol fermentation was confirmed in the present study. This novel combination improves the substrate conversion into bioproducts (i.e. biofuels and VFA) of a factor two. In addition, this work shows that it is possible to reduce significantly the energy consumption of mechanical processes, which applications are generally limited by operating costs despite their great interest in terms of

References (32)

Cited by (55)

  • Lignocellulosic biomass based microbial fuel cells: Performance and applications

    2022, Journal of Cleaner Production
    Citation Excerpt :

    It is predicted that it will possibly provide 38% of the world's biofuel and 17% electricity by 2050 (Feng and Lin, 2017). Now a days, the technologies and methods are being developed to efficiently convert biomass energy into other forms of energies including bio-fuels, gases, heat, and electricity (Motte et al., 2015). From past few years, an eco-friendly conversion of biomass waste into fuels, and other products is being considered as one of the effective approaches to involve renewable and sustainable energy.

  • Technical difficulties of mixed culture driven waste biomass-based biohydrogen production: Sustainability of current pretreatment techniques and future prospective

    2021, Renewable and Sustainable Energy Reviews
    Citation Excerpt :

    The cellulosic waste biomass known as lignocellulosic biomass (LCB) comprising municipal wastes and agricultural residuals, such as forest residues, stalks, straws, yard clippings, wood chips grass, and so on [3] are mostly used LCB for biohydrogen production due to their availability in nature. However, the conversion of raw LCB into hydrogen is troublesome because the hydrolysis of their complex polymeric (hemicellulose and cellulose) to smaller molecules is the rate-limiting step for biomass degradation [6,7]. Therefore, pretreatment of substrate is indispensable to metabolize crystalline and rigid structure of LCB for reducing the retention time of fermentation and to improve hydrogen yield.

View all citing articles on Scopus
View full text