Outdoor cultivation of Chlorella vulgaris FSP-E in vertical tubular-type photobioreactors for microalgal protein production
Introduction
According to a report by The Food and Agriculture Organization of the United Nations, human consumption of fish increased from 137.3 million tons in 2006 to 153.6 million tons in 2011. However, the amount of fish captured from freshwater and seas has been maintained at around 90 million tons every year, while fish production from the aquaculture sector increased from 47.3 to 63.6 million tons over the period 2006 to 2011 [1]. Given the depletion of wild fish resources and the need to allow those resources to recover naturally, the aquaculture sector has seen a rapid growth to supplement the global demand for fish [1]. High-value fish species in aquaculture are often carnivorous, consuming more than 400 g/kg of protein. This high protein diet is commonly provided by fishmeal — the main protein source in aquafeed [2], [3], [4]. The increasing demand for fishmeal has caused a significant rise in the price of fishmeal [5], thus sparking the search for alternatives, with microalgal protein being a promising source. In addition, algal biomass also contains other valuable components, such as pigments, omega-3 fatty acids, minerals and vitamins, which further increase the nutritional value of algae-based feed [6], [7]. Previous studies showed that serving algal as animal feed additive resulted in enhancements growth, physiological activity, feed utilization efficiency, stress response, starvation tolerance, disease resistance and carcass quality of the cultured fish [5]. However, one of the major challenges of using algal as aquafeed is how to effectively cultivate the protein-rich microalgae in an outdoor large scale to produce proteins with high quality and low cost. It is well known that temperature variations, inconsistent sunlight supply, contamination, inefficient mixing, and light penetrating efficiency are vital factors for the outdoor phototrophic microalgae growth. Considering the lower operation cost and relatively large scale production, commercial production of microalgal biomass is still commonly achieved via outdoor cultivation. Therefore, it is required to develop high efficiency and cost-effective photobioreactors for outdoor algae cultivation. Chen et al. [6] reported that using 50 L outdoor vertical tubular-type photobioreactors (PBRs) was favorable for photoautotrophic growth of microalgae due to better mixing efficiency and higher CO2 retention time. Operation strategy, especially inoculum size, aeration rate and nitrogen sources, is the critical factor affecting the growth of microalgae, as the nitrogen source limitation significantly influences the production of microalgal biomass and cellular components, such as total proteins, carbohydrates and lipids [8], [9]. Previous research shows that using an appropriate inoculum size could effectively promote cell growth [10]. Besides, microalgae growth in a photobioreactor was influenced by nutrient uptake, gas–liquid mass transfer and strategies [11], [12], [13]. In addition, carbon dioxide concentration and feeding rate could also be used to improve microalgae biomass and protein production [14], [15]. Meanwhile, using preferable bioreactor mode, such as continuous and semi-batch operations, could also enhance the productivity of biomass as well as target products of microalgae [16].
This study was undertaken to first compare the performance of biomass production and protein productivity of Chlorella vulgaris FEP-E in indoor and outdoor microalgal cultivation using 50 L PBRs. Next, specific engineering strategy was applied to promote cell growth and protein production of C. vulgaris FEP-E in the 50 L PBRs. The operation factors that were optimized to achieve the best cell growth and protein production included nitrogen concentration, inoculum size and aeration rate. Finally, to assess the applicability of the microalgae-based protein production system, the outdoor vertical tubular-type photobioreactor was operated on a semi-batch mode for a prolonged period under the optimal operation conditions. The goals of this study are to develop feasible cultivation strategies to enhance microalgal protein productivity in outdoor cultivation, and to evaluate the potential of producing proteins from microalgae as an alternative to fishmeal in aquafeed applications.
Section snippets
Microalgal culture and medium composition
The microalga strain used in this study was isolated from a freshwater area located in southern Taiwan, and identified as C. vulgaris by its morphology and 18S plastid rDNA sequence matching. The microalgal strain was denoted as C. vulgaris FSP-E. The C. vulgaris FSP-E strain has the advantages of fast-growing, high protein content, and being able to survive under outdoor cultivation conditions. Thus, this strain was used in this study for protein production. A modified version of basal medium
Comparison of growth performance between indoor and outdoor cultivation
Large-scale culture is needed in order to obtain large amounts of biomass at low cost. Outdoor mass cultivation systems have already been widely used in the commercial production of microalgal biomass [20], [21], [22], [23]. However, outdoor operations are much more difficult than indoor ones due to variations in sunlight availability, light intensity and temperature. Furthermore, the risk of contamination with an outdoor culture is also higher [24]. In this study, the performance of indoor and
Conclusions
C. vulgaris FSP-E can be grown in 50 L outdoor PBRs with similar cell growth and protein production performance to those obtained in the outdoor culture. The optimum conditions of outdoor cultivation were identified as 18.4 mM urea concentration, 0.2 g/L inoculum size, and aeration of 2.0% CO2 at 0.05 vvm. The highest biomass and protein productivities achieved were 268.1 and 155.4 mg/L/d, respectively. Long-term semi-batch operation (50% medium replacement) of the outdoor culture was successfully
Acknowledgments
The authors gratefully acknowledge the financial support received from Taiwan's National Science Council under grant numbers NSC 104-2221-E-006-229, NSC 104-3113-E-006-003 and NSC 103-2622-E-011-021-CC2. This research was also supported in part by funding from the Headquarters of University Advancement at the National Cheng Kung University, which is sponsored by the Ministry of Education, Taiwan, ROC (D103-51A01).
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