Abstract

The concerns over food security and protein scarcity, driven by population increase and higher standards of living, have pushed scientists toward finding new protein sources. A considerable proportion of resources and agricultural lands are currently dedicated to proteinaceous feed production to raise livestock and poultry for human consumption. The 1st generation of microbial protein (MP) came into the market as land-independent proteinaceous feed for livestock and aquaculture. However, MP may be a less sustainable alternative to conventional feeds, such as soybean meal and fishmeal, because this technology currently requires natural gas and synthetic chemicals. These challenges have directed researchers toward the production of 2nd generation MP by integrating renewable energies, anaerobic digestion, nutrient recovery, biogas cleaning and upgrading, carbon-capture technologies, and fermentation. The fermentation of methane-oxidizing bacteria (MOB) and hydrogen-oxidizing bacteria (HOB), i.e., two protein rich microorganisms, has shown a great potential, on the one hand, to upcycle effluents from anaerobic digestion into protein rich biomass, and on the other hand, to be coupled to renewable energy systems under the concept of Power-to-X.This work compares various production routes for 2nd generation MP by reviewing the latest studies conducted in this context and introducing the state-of-the-art technologies, hoping that the findings can accelerate and facilitate upscaling of MP production. The results show that 2nd generation MP depends on the expansion of renewable energies. In countries with high penetration of renewable electricity, such as Nordic countries, off-peak surplus electricity can be used within MP-industry by supplying electrolytic H2, which is the driving factor for both MOB and HOB-based MP production. However, nutrient recovery technologies are the heart of the 2nd generation MP industry as they determine the process costs and quality of the final product. Although huge attempts have been made to date in this context, some bottlenecks such as immature nutrient recovery technologies, less efficient fermenters with insufficient gas-to-liquid transfer, and costly electrolytic hydrogen production and storage have hindered the scale up of MP production. Furthermore, further research into techno-economic feasibility and life cycle assessment (LCA) of coupled technologies is still needed to identify key points for improvement and thereby secure a sustainable production system.

Highlights

  • The increase in global temperature, caused by climate change, has become a formidable challenge so that United Nations’ IPCC Special report has encouraged the implementation of multidisciplinary actions by 2030 before climate change becomes irreversible [1]

  • Ammonium comprises more than 60% of the nitrogen in digestate, which is prone to ammonia volatilization right after field application

  • The concept of consecutive methane-oxidizing bacteria (MOB)-hydrogenoxidizing bacteria (HOB) fermen­ tation can, to some extent, compensate investment and operating costs associated with biogas upgrading by providing more income and addi­ tionally improve the environmental profile of 2nd generation microbial protein (MP) by decreasing energy and materials requirement

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Summary

Introduction

The increase in global temperature, caused by climate change, has become a formidable challenge so that United Nations’ IPCC Special report has encouraged the implementation of multidisciplinary actions by 2030 before climate change becomes irreversible [1]. Nitrogen use efficiency by plants is reportedly below 50% meaning the remaining half contributes to eutrophication, emissions of the potent greenhouse gas N2O, and degradation to nitrate (a contributor to eutrophication) or nitrite (toxic for most life forms) [10,11]. Such problems have motivated scientists to focus on nutrient recovery from digestate for valorization into value-added products or being used as less-bulky fertilizers [9,12,13]. Called 2nd generation MPs substitute synthetic nutrients and natural gas in this process with their counterparts from waste effluents such as nitrogen from digestate and methane from biogas thereby reducing cost and contributing to the sustainability of MP production [23,31]. In order to meet the SDG’s objectives, it will be ideal to find sustainable and biobased protein sources

Production routes for 2nd generation MP
MOB grown on renewable energy and residual resources
HOB grown on renewable energy and residual resources
Future possibilities for improving MP quality
Nutrient recovery technologies
Common approaches for nitrogen/phosphorus recovery
AD digestate as a nutrient-rich source
Biogas upgrading technologies
Water scrubbing
Organic solvent scrubbing
Chemical absorption
Cryogenic separation
Chemical hydrogenation process
Biological technologies
Chemoautotrophic biogas upgrading
Photoautotrophic biogas upgrading (PBU)
Bioelectrochemical biogas upgrading
Comparing different technologies for coupling biogas upgrading and MP production
Electrolyzers
Carbon dioxide capture technology
Fermentation and post-processing of MP
Sustainability aspects
Findings
Conclusion and prospective work
Full Text
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