Water reuse and growth inhibition mechanisms for cultivation of microalga Euglena gracilis

Abstract

Background Microalgae can contribute to more than 40% of global primary biomass production and are suitable candidates for various biotechnology applications such as food, feed products, drugs, fuels, and wastewater treatment. However, the primary limitation for large-scale algae production is the fact that algae requires large amounts of fresh water for cultivation. To address this issue, scientists around the world are working on ways to reuse the water to grow microalgae so that it can be grown in successive cycles without the need for fresh water. Results In this study, we present the results when we cultivate microalgae with cultivation water that is purified and reused. Specifically, we purify the cultivation water using an ultrafiltration membrane (UFM) treatment and investigate how this treatment affects: the biomass and biochemical components of the microalgae; characteristics of microalgae growth inhibitors; the mechanism whereby potential growth inhibitors are secreted (followed using metabolomics analysis); the effect of activated carbon (AC) treatment and advanced oxidation processes (AOPs) on the removal of growth inhibitors of Euglena gracilis. Firstly, the results show that E. gracilis can be only cultivated through two growth cycles with water that has been filtered and reused, and the growth of E. gracilis is significantly inhibited when the water is used a third time. Secondly, as the number of reused water cycles increases, the Cl− concentration gradually increases in the cultivation water. When the Cl− concentration accumulates to a level of fivefold higher than that of the control, growth of E. gracilis is inhibited as the osmolality tolerance range is exceeded. Interestingly, the osmolality of the reused water can be reduced by replacing NH4Cl with urea as the source of nitrogen in the cultivation water. Thirdly, E. gracilis secretes humic acid (HA)—which is produced by the metabolic pathways for valine, leucine, and isoleucine biosynthesis and by linoleic acid metabolism—into the cultivation water. Because HA contains large fluorescent functional groups, specifically extended π(pi)-systems containing C=C and C=O groups and aromatic rings, we were able to observe a positive correlation between HA concentration and the rate of inhibition of E. gracilis growth using fluorescence spectroscopy. Moreover, photosynthetic efficiency is adversely interfered by HA, thereby reductions in the synthetic efficiency of paramylon and lipid in E. gracilis. In this way, we are able to confirm that HA is the main growth inhibitor of E. gracilis. Finally, we verify that all the HA is removed or converted into nutrients efficiently by AC or UV/H2O2/O3 treatments, respectively. As a result of these treatments, growth of E. gracilis is restored (AC treatment) and the amount of biomass is promoted (UV/H2O2/O3 treatment). Conclusions These studies have important practical and theoretical significance for the cyclic cultivation of E. gracilis and for saving water resources. Our work may also provide a useful reference for other microalgae cultivation.

Redox Mediators in Microbial Electrochemical Systems

“…So far, the research regarding the recycling or removal of mediators in BESs is rather scarce but can benefit readily from the research efforts in other relevant fields. For instance, the reuse of culture medium has been a long‐term desire in biotechnology (especially for large scale cultivation) to reduce the operation cost [21–23] . Membrane or chromatography‐based approaches are used mostly to separate and recycle usable nutrients.…”

“…For instance, the reuse of culture medium has been a long-term desire in biotechnology (especially for large scale cultivation) to reduce the operation cost. [21][22][23] Membrane or chromatography-based approaches are used mostly to separate and recycle usable nutrients. These might also be applicable in BESs for mediator recycling, while the economic feasibility might be a key limitation.…”

The Effect of Dichloromethane on Product Separation during Continuous Hydrothermal Liquefaction of Chlorella vulgaris and Aqueous Product Recycling for Algae Cultivation

“…Another commonly used purification method is the removal of organics by adsorption, which is widely applied in the removal of pollutants from water, especially employing activated carbon absorption (ACA), because it is costeffective and easily adaptable. In a recent study, 40 ACA treatment has been shown to remove or convert humic acid into nutrients and water recovery. In our study, SCWG and ACA treatments were applied as purification steps of the aqueous product from microalgae HTL.…”

Humic Substances as Microalgal Biostimulants—Implications for Microalgal Biotechnology

“…Microalgae release into their cultivation media various organic compounds with various molecular masses, including aromatic amino acids such as tryptophan and tyrosine, heterocyclic pigments such as biopterin, proteins, etc., that generate humic-like substances, algal organic matter (AOM) [ 182 ]. This dissolved organic matter that results from microalgae organisms is also called humic matter due to its aromaticity (π-π systems) related to significant fluorescence [ 183 , 184 ]. In several cases, accumulations of this organic matter during microalgae cultivation block water reuse.…”