Abstract

Paludiculture, and in particular the cultivation of perennial grasses as biomass feedstock for green biorefineries, may be an economic and environmentally sustainable option for agricultural peatlands in temperate regions. However, the optimal biomass quality for protein extraction from flood-tolerant grasses is largely unknown. The aim of this study was to define the combined effect of harvest and fertilization frequency, with one to five annual cuts, on protein yield and extractability for the grasses tall fescue (TF) and reed canary grass (RCG), cultivated on an agricultural fen peatland in Denmark.The content of protein fractions was determined according to the Cornell Net Carbohydrate and Protein System (CNCPS). We assessed protein extractability by lab-scale biorefinery techniques using a screw-press followed by acid precipitation of true protein. The two methods were compared to correlate potential extractable protein yields with actual biorefinery outputs. We found the highest annual biomass and crude protein (CP) yields in the two cut treatments, with 13.4 and 15.6 t dry matter (DM) ha−1 year−1, containing 2.9–3.4 t CP ha−1 year−1for TF and RCG, respectively. The highest neutral-extractable (fractions B1and B2) true protein yields of 1.1 and 1.5 t ha−1 year−1were found in the two cut treatments, representing 39% (TF) - 45% (RCG) of total CP. Using biorefining techniques, we were able to precipitate up to 2.2 t DM ha−1 year−1of protein concentrate, containing up to 39% CP. Significant correlations between methods were found, with a distinct relationship between CNCPS fractions B1+ B2and CP yield of the protein concentrate, indicating the suitability of the CNCPS as an indicator for extractable protein yields. Biomass and CP yields were not significantly improved beyond two annual cuts. However, timing and harvest frequencies significantly affected plant maturity and consequently extractable CP contents and protein concentrate yields. We conclude that TF and RCG are promising feedstocks for green biorefineries due to high biomass, extractable CP, and protein concentrate yields, and highlight the potential of flood-tolerant grasses, cultivated on wet agricultural peatlands, for an enhanced valorisation beyond the common utilisation for bioenergy.

Highlights

  • With an increasing world population, being expected to reach 9.7 billion in 2050 (United Nations, 2019), and the associated escalating demand for food and clean water (Ibarrola-Rivas et al, 2017) the competition for productive land areas is growing (Joosten et al, 2016)

  • The correlation decreased with increasing crude protein (CP) yield in the corresponding counterpart (B1 + B2 > B1 + B2 + B3 > Biomass), with tall fescue (TF) in all scenarios having a higher correlation coefficient compared to reed canary grass (RCG) (Figure 8)

  • We found the highest annual biomass and CP yields in the two cut treatments, with 13.4 and 15.6 t dry matter (DM) ha−1 year−1, yielding 2.9 and 3.4 t CP ha−1 year−1 for TF and RCG, respectively

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Summary

Introduction

With an increasing world population, being expected to reach 9.7 billion in 2050 (United Nations, 2019), and the associated escalating demand for food and clean water (Ibarrola-Rivas et al, 2017) the competition for productive land areas is growing (Joosten et al, 2016). Peatlands, being the dominating wetland type globally (Yu et al, 2010) and covering about 3% of the continental surface (Joosten and Clarke, 2002) contribute significantly to GHG emissions. Anthropogenic degradation of peatlands by drainage for agriculture led to a substantial loss of global peatlands and the associated ecosystem functions (Wichmann, 2017), and to emission hotspots releasing 6% of the total anthropogenic emissions in carbon dioxide equivalents (CO2eq) (Joosten, 2012), contributing up to 37% of the total emissions from the European agricultural sector (Geurts, et al, 2019). Paludiculture, defined as agriculture on wet or rewetted peatlands, has been proposed as a suitable mitigation strategy (Günther et al, 2014) in order to reverse traditional farming with unsustainable environmental concerns such as land subsidence, nutrient leaching and GHG emissions to the atmosphere (Tanneberger and Wichtmann, 2011; Giannini et al, 2017). The revenues of the peatland biomass for these purposes have so far been too low to provide a competitive sustainable business plan

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