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158                     Refining Biomass Residues for Sustainable Energy and Bioproducts


           In this work the adequacy of different wastewater streams to sustain microalgae
         growth is reviewed. The liquid streams were classified according to their origin and
         composition as follows: digestate slurries, domestic and industrial flows, LLs, and
         treatment plant effluents.



         7.3.1 Digestates

         The AD of organic materials is a way to treat wastes with the production of biogas
         (methane, CH 4 ) as clean energy and a liquid digestate. During AD, bacteria trans-
         form complex organic wastes into biogas. The transformed wastes are then used as
         a green fertilizer because of their high nutrient contents. When lipids, carbohy-
         drates, and proteins contained in these wastes are converted to CH 4 , nitrogen is
         released, typically as NH 3 , the main source of nitrogen in digestate slurries. This
         large content of NH 3 is one of the drawbacks of the use of this stream for algae
         cultivation, since NH 3 can be, at high levels, toxic to algae. Therefore the dilution
         of these liquid wastes based on the NH 3 concentration is a common practice.
         This, at the same time, improves light penetration to the cultures prepared from
         digestates, as their characteristic dark-brown color can interfere with light reach-
         ing the cells.
           Recent works have reported on the use of digestate as a source of nutrients
         to grow algae (Table 7.2). These investigations aimed at defining ideal concen-
         trations of digestate to be used, at assessing strain tolerances, and at establishing
         the conditions for wastewater cleaning, and biomass productivity and
         composition.
           Ji et al. (2014a) evaluated the growth of Desmodesmus sp. in 2.5%, 5%, and
         10% of AD wastewater (ADW) and found that the best growth and removal rate of
         nutrients was observed at 10% of ADW. Similarly, Koutra et al. (2018) tested the
         performance of seven different microalgae strains to select the most appropriate one
         for biomass production and digestate bioremediation. In their study, microalgae
         were grown in 10% digestate (derived from agro-industrial wastes) diluted in water,
         during a cultivation period of 25 days. The maximum growth was observed in the
         cultures of Ponticola kessleri, Anisancylus obliquus, and Chlorella vulgaris with
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         specific growth rates of 0.130, 0.145, and 0.161 day , respectively.
           Similar values of biomass (0.32 g/L) and lipid production (15.5%) were found
         for Chlorella sorokiniana grown in diluted digestate (10%) and in commercial
         medium (BBM) (Lizzul et al., 2014).
           Culture media formulated from digestates at different dilution ratios have been
         used to produce value-added components from the biomass. The growth and pro-
         duction of polyhydroxy butyrate (PHB) of a brackish cyanobacteria strain
         Synechocystis cf. salina was compared in a 33% digestate diluted in water, and in
         an artificial culture medium (BG11) (Meixner et al., 2016). The cultivation in the
         diluted digestate achieved 84% of the biomass and 78% of the PHB values obtained
         in BG11. However, the cultivation took almost 50% more time in the diluted
         digestate.
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