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Article

Bench-Scale Cultivation of Microalgae Scenedesmus almeriensis for CO2 Capture and Lutein Production

1
ENEA, Italian National Agency for New Technologies, Energy and Sustainable Economic Development, Department of Sustainability-CR Portici. P. Enrico Fermi, 1, 80055 Portici (NA), Italy
2
Department of Engineering, University of Campania “Luigi Vanvitelli”, Real Casa dell’Annunziata, Via Roma 29, 81031 Aversa (CE), Italy
*
Author to whom correspondence should be addressed.
Energies 2019, 12(14), 2806; https://doi.org/10.3390/en12142806
Submission received: 18 June 2019 / Revised: 14 July 2019 / Accepted: 21 July 2019 / Published: 22 July 2019

Abstract

:
In this study, Scenedesmus almeriensis as green microalga was cultivated on bench-scale for carbon dioxide (CO2) capture and lutein production. The autotrophic cultivation of S. almeriensis was carried out by using a vertical bubble column photo-bioreactor (VBC-PBR) with a continuous flow of a gaseous mixture of oxygen (O2), nitrogen (N2), and CO2, the latter in content of 0.0–3.0 %v/v. The liquid phase was batch. S. almeriensis growth was optimized. In addition, lutein extraction was carried out by using accelerated solvent extraction with ethanol as Generally Recognized as Safe (GRAS) solvent at 67 °C and 10 MPa. Upon optimization of CO2 concentration, the maximum biomass productivity, equal to 129.24 mg·L−1·d−1, was achieved during the cultivation by using a content of CO2 equal to 3.0 %v/v and it allowed to obtain a lutein content of 8.54 mg·g−1, which was 5.6-fold higher in comparison to the analogous process carried out without CO2 addition. The ion chemical analysis in the growth medium showed that by gradually increasing CO2 content, the nutrient consumption during the growth phase also increased. This study may be of potential interest for lutein extraction at industrial scale, since it is focused on pigment production from a natural source with a concomitantly CO2 capture.

Graphical Abstract

1. Introduction

Microalgae cultivation is widely accepted as a valid method for carbon dioxide (CO2) capture from industrial plants, and for the extraction of high-value products, such as carotenoids and fatty acids [1,2,3,4,5,6,7,8]. Microalgae-based CO2 biofixation and biomass production are strongly dependent on the microalgae strain selection and the adopted growth conditions [5]. Scenedesmus almeriensis, being the highest lutein natural producer, has attracted growing interest and it represents the only commercialized microalgae for pigment extraction [9,10,11,12]. Lutein is classified as a primary xanthophyll because of the presence of two hydroxyl functional groups in the structure [13,14,15]. It acts as a light energy harvesting compound, which improves the photosynthesis efficiency and it prevents photodamage [16]. A daily lutein intake of 1 mg/kg body weight was suggested by the European Food Safely Authority (EFSA) [17], which could provide several health benefits. Moreover, lutein also acts as an antioxidant, anti-inflammatory, and colorant, which promotes its application for nutraceutical and pharmaceutical purposes [9]. Lutein is accumulated in the macula of the human eye retina and it is able to prevent or ameliorate cardiovascular diseases [18].
An enhanced production of lutein from microalgae can be achieved through a proper design of suitable culture strategies. The main parameters typically considered for potential microalgal producers of lutein are lutein content and biomass productivity. As reported by several authors, lutein content can be improved by optimizing the main physico-chemical (CO2 content, inoculum concentration, light intensity, temperature, and pH) and hydrodynamic (flow rate, distribution by mixing, and CO2 mass transfer) parameters [1,7,9,14,15,19,20,21,22,23,24,25,26,27,28,29]. Furthermore, under autotrophic growth conditions, microalgae cultivation is free of contamination from external sources, and the pH, if it is necessary, can also be regulated by feeding CO2 [15]. Autotrophic cultivation of microalgae could offer several environmental benefits, such as CO2 sequestration for a reduced greenhouse gas (GHG) emission [15,29,30,31]. The autotrophic growth requires inorganic carbon sources under illumination, which could potentially be derived from sun light, thus optimizing the overall production cost.
Xie et al. [14] evaluated the effect of CO2 concentration on microalgae biomass and lutein production from Desmodesmus sp. F51, and they found that by fixing CO2 concentration at 0.03, 2.5, 5.0, 7.5, 10.0, and 12.5%, biomass productivity and specific growth rate increased with increasing CO2 concentration from 0.03% to 2.5%, and they showed a decrease when CO2 concentration was further increased to 12.5% [14]. Therefore, in this study, a CO2 content of 3 %v/v as a maximum value was selected.
The extraction of intracellular compounds from microalgae biomass by using chemical solvents is the most reliable method to extract compounds by microalgae. Extraction efficiency and lutein recovery by organic solvents are higher than those associated with other physical methods. However, the effectiveness of the used solvent relies intensely on microalgae strains and on physical properties of microalgae biomass. Additionally, after the solvent extraction, lutein could be used in nutraceutical and pharmaceutical industries, while the exhausted biomass could be used in an integrated biorefinery for bioenergy production [32,33,34].
The effect of different CO2 contents, in the range of 0–3 %v/v, on biomass and lutein production, and on average CO2 capture rate and CO2 conversion efficiency, was investigated. Biomass harvesting was carried out through vacuum filtration, while the subsequent solvent extraction of lutein was performed by using the accelerated solvent extraction (ASE) technique. Ethanol, as Generally Recognized as Safe (GRAS) solvent, was used for the extraction step, operating at 67 °C, 10 MPa. Extraction was performed on mechanically pretreated S. almeriensis biomass. Lutein analysis was carried out by means of u-HPLC analysis.

2. Materials and Methods

2.1. Microalgae and Growth Medium

Microalgae S. almeriensis were supplied by AlgaRes Srl, Rome, Italy, and used as the inoculum for cultivation under laboratory conditions. Microalgae cells were cultivated using a modified Mann and Myers medium [19,35], which consisted of: NaNO3 (1.0 g/L), K2HPO4 (0.1 g/L), MgSO4·7H2O (1.2 g/L), and CaCl2 (0.3 g/L). Also, a micronutrient solution of 10 mL was added into 990 mL of Mann and Myers medium. The micronutrients stock solution contained Na2EDTA (0.001 mg/L), MnCl2 (1.4 mg/L), ZnSO4·7H2O (0.33 mg/L), FeSO4·2H2O (2 mg/L), CuSO4·5H2O (0.002 mg/L), and Co(NO3)2·6H2O (0.007 mg/L).

2.2. Photo-Bioreactor

S. almeriensis was cultivated in a vertical bubble column photo-bioreactor (VBC-PBR), made of Plexiglas, with a working volume of 28.5 L (effective height: 680 mm; external diameter: 250 mm; thickness: 10 mm) and with the volume to surface ratio (V/S) of 56.5 L/m2. The VBC-PBR was equipped with control and monitoring systems for monitoring and regulating gaseous mixture flow rate, temperature, pH, and light intensity. VBC-PBR was fed by a gaseous mixture (N2/ON2/CO2) from cylinders. Gaseous mixture flow rate was controlled by using Bronkhorst controllers (The Netherlands), with flow control accuracy of 0.5%. The bottom of the reactor was equipped with 6 sintered steel spargers, installed through 6 filleted holes (1/2”), to feed the gaseous mixture into the photo-bioreactor. The top of the reactor was equipped with a temperature sensor (thermocouple) and with a pH sensor. Temperature measurement was used to drive the temperature control system by modifying the flow rate of a cooling fluid flowing into an AISI 316L coaxial pipe (diameter = 60.3 mm, thickness = 1 mm). A temperature control system allowed the regulation of the temperature inside the reactor with a precision of ±1 °C in the range of 15–35 °C, thanks to a heat pump.
The lighting system consisted of a semi-cylinder, located at a distance of 100 mm from the VBC-PBR with blue, white, and red lights from a selective LED system (only blue/only white/only red, or a mix of them), with a light intensity in the range of 0–5000 lux on the surface of the VBC-PBR. The diameter of the lighting system was 350 mm, which was controlled and regulated by SCADA (Supervisory Control and Data Acquisition). The SCADA system was equipped with a touch-screen, custom software and PC to collect and record experimental data of temperature, gas flow rate, pH, and light intensity. A schematization of the experimental set-up in Figure 1 is sketched.

2.3. Growth Conditions

Cultivation of microalgae was carried out by using a modified Mann and Myers medium with the above mentioned concentration (Section 2.1.). During investigations, a desired amount of inoculum was added to achieve an optical density of 0.6–0.7 at 420 nm. Each investigation was carried out by using a working volume of 28.5 L. The microalgae growth was performed under white light with a lux intensity on the VBC-PBR surface of 4000 lux, and by continuously feeding, for all the cultivation time, a gaseous mixture stream consisting of O2, N2, and CO2 with a flow rate of 300 mL·min−1. The CO2 content was varied in the range of 0–3.0 %v/v (O2 = 21 %v/v). Cultivation was carried out by keeping temperature constant at 28 °C. Each experimental condition was investigated three times, and for each condition, the standard deviation (SD) value was calculated.

2.4. Average CO2 Capture Rate and CO2 Conversion Efficiency

Average CO2 capture rate, RCO2 (gCO2·L−1·d−1), can be assessed by considering the elemental carbon content of the microalgae cell and the biomass productivity, according to the following equation [36]:
R C O 2 = C C · P · ( M C O 2 M C )
where Cc is the carbon content of the microalgae cell (% wt), P is the biomass productivity (gbiomass·L−1·d−1), MCO2 is the molecular weight of CO2, and MC is the molecular weight of carbon.
Average CO2 capture efficiency can be assessed according to the following equation [37]:
E C O 2 = R C O 2 · V P B R · t ρ C O 2 V C O 2 × 100
where RCO2, VPBR, VCO2, and ρCO2 are the average CO2 capture rate (gCO2·L−1·d−1), the volume of the VBC-PBR (L), total CO2 consumed (L) during the cultivation time t (d), and the density of CO2 (g·L−1), respectively.

2.5. Analytical Methods

2.5.1. Determination of Algal Cell Concentration and Dry Cell Weight

S. almeriensis cell growth was monitored by determining the absorbance of each sample at 420 and 690 nm for Chlorophyll-a, and 480 and 620 nm for Chlorophyll-b, by using a UV/Visible spectrophotometer (Multiskan, Thermo Fisher Scientific, USA). The biomass dry cell weight (DCW) was calculated using the absorbance values at different biomass concentrations evaluated during the growth phase, obtaining a calibration curve between absorbance and concentration as showed in Equation (3).
DCW = (0.0867·A) − 0.1868
where DCW is concentration of biomass on dry cell weight (g/L) and A is the total absorbance obtained from the sum of the absorbance values obtained for the four chlorophyll wavelengths.
The final dry weight was determined through cell culture dewatering by a vacuum filtration system, using vacuum filters with a pore size of 0.45 μm (Sigma-Aldrich, USA); microalgal pellets from dewatering were lyophilized for 24 h.

2.5.2. Accelerated Solvent Extraction

Lutein extraction was carried out from mechanically pre-treated biomass of S. almeriensis cells, by using Dionex-ASE 200 extractor (Salt Lake City, UT, USA). The pretreatment was performed at optimized conditions, according to the procedure described elsewhere [38]. Four consecutive extraction cycles (single extraction cycle = 20 min) were performed by using ethanol at optimized extraction conditions, 67 °C and 10 MPa, for the complete biomass discoloring, as reported in a previous work [39]. At the end of each extraction cycle, extracts were collected into 40 mL amber glass vials by flushing the system with 6.6 mL of fresh solvent, and the system was purged for 1 minute with nitrogen (Purity ≥ 99.999%).

2.5.3. Nutrient Consumption Chemical Analysis

The nutrient (anions and cations) concentrations were analyzed using an ion Chromatograph (Dionex™ ICS-1100, Thermo Scientific, Massachusetts, USA), as reported by Pruvost et al. [40], at the beginning and at the end of the growth period. The Dionex ICS-1100 was an integrated ion chromatography system equipped with a pump, injection valve, and conductivity detector. Several nutrients such as Mg2+, SO42−, Na+, NO3, NO2, Ca2+, Cl, K+, and PO43−, which are essential for growth of microalgae, were analyzed.

2.5.4. Lutein Analysis

The extract obtained after each extraction cycle was equally transferred into two different vials by adding BHT at 0.1 % wt as antioxidant for gravimetric analysis and saponification. The total lutein content was gravimetrically quantified, after the complete removal of the solvent using a Zymark TurboVap evaporator (Zymark, Hopkinton, MA, USA). Lutein analysis consisted of two steps: The first one was the saponification of samples to avoid the overlap of the spectra with the species present in the carotenoid family (lipids and chlorophylls) [41,42,43]; the second one was the measurement by using u-HPLC technology (Agilent 1290 Infinity II). The detailed procedure is reported elsewhere [41,42,43].

3. Results and Discussion

3.1. Effect of CO2 Content on Culture Medium pH

For each growth condition investigated, during the days of microalgal cultivation, a slight variation of pH was observed. In particular, pH increased from the initial value of 7.5 at the beginning of the cultivation, to the final value of 8.5 at the end of the cultivation; therefore, for the CO2 concentration range investigated (0–3.0 %v/v), the pH of the culture medium was marginally affected by the CO2 content, as reported by several authors [44,45]. The increase of the pH value during the cultivation can be attributed to the alkalinization of the medium as a result of CO2 biofixation during photosynthesis: Carbonate and bicarbonate, and hydroxide contents increased, while CO2 concentration decreased [46].

3.2. Effect of CO2 Content on Biomass Concentration

The effect of CO2 on the concentration of the S. almeriensis and on biomass productivity, i.e., the biomass produced per reactor liter and per day, are shown in Figure 2 and Figure 3, respectively.
By increasing the cultivation time, the biomass concentration increased until the achievement of a maximum value (Figure 2). By increasing CO2 content, an increase of both biomass productivity, with the consequence reduction of the cultivation time required for the achievement of the maximum value, and of the concentration of the biomass were observed, despite the concentration of the microalgae fed with a gaseous mixture with a CO2 content of 1.5 %v/v and the one fed with a gaseous mixture with a CO2 content of 3.0 %v/v being comparable, even if the cultivation time decreased. The observed increase in biomass concentration reflected an efficient photosynthesis rate, promoting an upregulated expression of RuBisCO in the presence of a determined inorganic carbon content [47]. However, the optimum CO2 content also contributed to maintain pH close to the neutral value. For high CO2 adaptation, cells temporarily reduced the synthesis of organic carbon and provided more ATP to assure intracellular pH stability through gene regulation and increasing the energy allocation proportion PSI/PSII [29].
With a CO2 content of 0 %v/v (O2 = 21 %v/v − N2 = 79 %v/v), a maximum concentration of biomass equal to 0.07 g·L−1 after 11 days of cultivation was observed, while it increased to 0.72 g·L−1 after 18 days with a content of CO2 of 0.5 %v/v. With CO2 contents of 1.5 %v/v and of 3 %v/v, the maximum biomass concentrations equal to 0.95 g·L−1 after a cultivation time of 16 days, and to 0.92 mg·L−1 after a cultivation time of 10 days, were measured, respectively. By increasing CO2 content from 0 to 3 %v/v, biomass productivity increased from about 4 mg·L−1·d−1 to about 130 mg·L−1·d−1, with productivities of about 39 mg·L−1·d−1 and 65 mg·L−1·d−1 at CO2 contents of 0.5 %v/v and 1.5 %v/v, respectively. Passing from 0 %v/v to 3 %v/v, biomass productivity increased of about 32-fold.
Cheng et al. [48] reported that the amount of CO2 present in the air (0.04%) is inadequate to achieve high cell density and on the other hand, an excess may inhibit the carbonic anhydrase enzyme, which in turn may reduce biomass productivity. Sepulveda et al. [49] reported that S. almeriensis was one of the most productive strains when using it in CO2 capture processes, with a biomass productivity of 1.0 g·L−1·day−1 and with 2.8 g·L−1·day−1 of CO2 consumed. Acién et al. [50] reported a consumption of CO2 of 2.31 gCO2·gb−1 for S. almeriensis.

3.3. Effect of CO2 Content on Carbon Content, Average CO2 Capture Rate, and CO2 Conversion Efficiency

Carbon content, average CO2 capture rate, and CO2 conversion efficiency, including biomass productivity, are shown in Table 1. As reported, the highest carbon element of microalgae cells (CC) and the highest average CO2 capture rate (RCO2) were found with the highest CO2 content (3 %v/v), while the highest CO2 conversion efficiency (ECO2) was found with the lowest CO2 content (0.5 %v/v).
Average CO2 capture rates assessed in the present work are comparable with the ones available in the literature for Scenedesmus sp.; however, it should be considered that different growth conditions and fluid dynamics were used. Chaudhary et al. [37] investigated CO2 capture rate through Scenedesmus obliquus cultivation by using an airlift bubble column photo-bioreactor (PBR) (working volume = 7 L), supplied with gas (air + CO2 5 %v/v) at a flow rate of 1.4 L·min−1 and irradiated with cool white fluorescent light (3 tubes × 24 W), finding an average CO2 capture rate of 0.13 gCO2·L−1·d−1. CO2 capture rate through Scenedesmus obliquus cultivation by using tubular-type PBR (working volume = 1.8 L), supplied with gas (air + CO2 12 %v/v) at a gas volume per liquid volume per min of 0.3 and irradiated with 3200 lux brightness provided by 40 W fluorescent daylight type lamps, was also investigated by Radmann et al. [51]; they found a biomass productivity of 0.6 gbiomass·L−1·d−1 and a CO2 capture rate of 0.11 gCO2·L−1·d−1. Jin et al. [52] investigated CO2 capture rate through Scenedesmus sp. cultivation by using a bubble column PBR (working volume = 1 L), supplied with gas (air + CO2 10 %v/v) at a gas volume per liquid volume per min of 0.2 and irradiated with a light intensity of 200 μmol·m−2·s−1, finding an average CO2 capture rate of 0.46 gCO2·L−1·d−1. Ong et al. [53] found a CO2 capture rate of 0.021 gCO2·L−1·d−1 for Chlorella sp. by using a vertical bubble column (working volume = 40 L) supplied with gas (air + CO2 5 %v/v) at a gas volume per liquid volume per min of 0.25 and irradiated with a light intensity of 1500 μmol·m−2·s−1. Hsueh et al. [53] found a CO2 capture rate of 0.141 gCO2·L−1·d−1 for Thermosynechococcus sp. by using a bubble column (working volume = 40 L) supplied with gas (air + CO2 10 %v/v) at 1 L·min−1 and irradiated with a light intensity of 10000 lux. Nayak et el. [54] reported that the CO2 biofixation rate of Scenedesmus sp., when aerated with more than 1 %v/v CO2 by using a bubble column photo-bioreactor (working volume = 0.5), was in the range of 0.27–0.37 g·L−1·d−1.
In terms of CO2 capture efficiency, S. almeriensis performance are comparable with performances of several microalgal species [55,56].

3.4. Role of CO2 Content on Nutrient Consumption

Nutrients are essential for microalgae cell growth, and a similar concentration of nutrients was kept in each growth phase. The concentration of the main ions of the growth medium at the beginning of the cultivation are reported in Table 2. The concentration of NO3 ions was the highest with respect to the rest of nutrients. It is worth highlighting that in the case of growth with a CO2 content of 0.5 %v/v, nutrient concentration was slightly lower because the growth was continued from the 0.0 %v/v CO2 content step.
Figure 4 illustrates the effect of CO2 content on nutrient consumption, measured at the end of the growth of S. almeriensis. Data highlighted a complete consumption of phosphate ions, which could limit the cell growth. The increase of CO2 content increased the nutrient consumption rate. However, the longer cultivation times (i.e., 20 days for CO2 = 0.5 %v/v; 16 days for CO2 = 1.5 %v/v; 13 days for CO2 = 3.0 %v/v) also promoted the nutrient intake. Among all the supplied nutrients, nitrate and phosphate were highly consumed during the growth phase. The possible explanation for this phenomenon is that a nitrogen source is essential for protein synthesis, and lutein exists as a nitrogenous macromolecule (i.e., light-harvesting complexes; LHCII) in microalgae [15]. NO3 and PO43− ions are the most important nutrients for cell proliferation during growth of microalgae [57], as confirmed by the present study. However, the consumption of NO3 ions was 5.0, 59.88, 77.26, and 87.22% during the growth with CO2 contents of 0.0, 0.5, 1.5, and 3.0 %v/v, respectively. This observation can be justified by considering a limited carbon source, which leads to a stress condition on microalgae growth cells, causing a lower biological consumption of nutrients. At the end of the growth, a lower consumption of both Na+ and Cl ions was observed, in comparison to the consumption of other nutrients, with a consumption below 25%. The consumption of Cl ions decreased by increasing CO2 content from 0.5 %v/v to 3.0 %v/v, which could be explained by considering a lower cultivation time. Similar results were observed during the cultivation of Chlorella vulgaris [58]. Chen et al. [15] evaluated the effect of nitrate and they reported that a sufficient amount of nitrogen in the medium was required to enhance lutein accumulation in the Chlorella sorokiniana Mb-1 strain. More importantly, it could be possible that the lutein content may depend on the residual nitrogen concentration [14].

3.5. Extraction Yield and Lutein Production from S. almeriensis

The increase of CO2 content of the gaseous mixture from 0.0 %v/v to 3.0 %v/v improved the extraction yield and the lutein content, as shown in Figure 5. The harvested S. almeriensis biomass during the growth with a content of CO2 of 0.0 %v/v showed extraction yield of about 172.28 mg·g−1 with a lutein content of 1.51 mg·g−1. With a content of CO2 of 0.5 %v/v, an increase of the extraction yield of 1.4-fold and a lutein content of 3.1-fold higher than that measured in absence of CO2 were found. The highest extraction yield and the highest lutein content, equal to 328.05 mg·g−1 and 8.54 mg·g−1, respectively, were obtained by feeding microalgae with a gaseous mixture containing a CO2 concentration of 3.0 %v/v. The increase of lutein content in biomass growth in stressed conditions might indicate that lutein could play a role in protecting cells from photodamage [20].

3.6. Comparison of Biomass Productivity and Lutein Content

Biomass productivity and lutein content under the optimal growth condition defined in this study, including the comparison with literature data, are reported in Table 3. Heterotrophic and mixotrophic cultivations support higher biomass productivity; a feasible lutein production from a mixotrophic microalgae culture, which has been rarely mentioned in the literature, is also shown—however, lutein content is lower than the one of most microalgae autotrophic cultivation (Table 3). The biomass productivity is lower during autotrophic cultivation of different microalgae strains, while a significant amount of lutein can be produced. Moreover, autotrophic cultivation brings several advantages such as capture of CO2, helping in reduction of the GHG and allowing the development of integrated biorefinery based on flue gas carbon sequestration through microalgae, and the simultaneous production of commercially valuable microalgal products, such as lutein and biodiesel [7]. Furthermore, autotrophic cultivation of microalgae might use sun as an economic source of light, which could be an effective strategy to economize the microalgal bioprocess [59]. Recently, Patel et al. [59] proposed the mixotrophic cultivation of Chlorella protothecoides, which could enhance the biomass productivity. Therefore, integration of different strategies could be a potential tool for the production of higher amounts of lutein with other bioactive compounds.
Interestingly, a significant amount of lutein was attained in this study during autotrophic cultivation of S. almeriensis, which is the highest among the ones reported in Table 3.

4. Conclusions

The present study shows the role of CO2 content on cultivation of S. almeriensis for biomass and lutein production; moreover, CO2 capture rate and CO2 conversion efficiency for S. almeriensis were also assessed. The optimal amount of inorganic carbon source improved the photosynthetic efficiency. By increasing the CO2 content, the biomass productivity increased; the highest biomass concentration of about 0.94 g·L−1 was obtained with a content of CO2 of 1.5 %v/v, with a direct correlation with the extraction yield and the lutein content. Moreover, a similar trend for nutrient consumption was also found. The nutrient chemical analysis shows that a content of CO2 of 3.0 %v/v better supports nutrient intake during the growth phase, while consumptions of nitrate and phosphate have been found as the highest ones for each test. The increase of CO2 content increased the extraction yield, as well as the lutein content. With a CO2 content of 3 %v/v, the extraction yield and lutein content were about 328 mg·g−1 and 8 mg·g−1 of dry biomass, respectively. It is worth pointing out that due to the impressive lutein content, S. almeriensis could be a suitable candidate for potential commercial production of microalgae-derived natural lutein.
This study could positively contribute to the present scientific literature showing the sustainable integration of CO2 sequestration with the concomitant microalgae cultivation for the production of lutein and of other high value-added chemicals.

Author Contributions

Conceptualization, D.M. and A.M.; Data Curation, S.M. and A.I.; Formal Analysis, A.I.; Investigation, S.M.; Methodology, S.C., D.K., A.I., P.C., and A.M.; Writing—Original Draft, S.M. and T.M.; Writing—Review and Editing, S.C. and D.M.; Project Administration, A.M.; Resources, A.M.; Supervision, D.M. and A.M.

Funding

This research was funded by a Bio Based Industries Joint Undertaking under the European Union’s Horizon 2020 research and innovation program, grant agreement No. 745695 (VALUEMAG).

Conflicts of Interest

The authors declare no conflict of interest.

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Sample Availability: Samples of the compounds are available from the authors.
Figure 1. Experimental set-up schematization.
Figure 1. Experimental set-up schematization.
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Figure 2. Effect of CO2 content on S. almeriensis biomass concentration during cultivation.
Figure 2. Effect of CO2 content on S. almeriensis biomass concentration during cultivation.
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Figure 3. Effect of CO2 content on S. almeriensis biomass productivity.
Figure 3. Effect of CO2 content on S. almeriensis biomass productivity.
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Figure 4. Effect of CO2 content on nutrient consumption efficiency during cultivation of S. almeriensis. Standard deviation was less than 5% in all operative conditions.
Figure 4. Effect of CO2 content on nutrient consumption efficiency during cultivation of S. almeriensis. Standard deviation was less than 5% in all operative conditions.
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Figure 5. Effect of CO2 content on extraction yield and lutein content from S. almeriensis.
Figure 5. Effect of CO2 content on extraction yield and lutein content from S. almeriensis.
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Table 1. Carbon elemental, average CO2 capture rate, and CO2 capture efficiency.
Table 1. Carbon elemental, average CO2 capture rate, and CO2 capture efficiency.
CO2 Content (%v/v)CC (% w/w)P (gbiomass L−1 d−1)RCO2 (gCO2 L−1 d−1)ECO2 (%)
0.543.40.0390.0644.5
1.542.40.0650.1024.3
3.049.90.1290.2428.4
Table 2. Initial concentration of nutrients during the S. almeriensis cultivation.
Table 2. Initial concentration of nutrients during the S. almeriensis cultivation.
Nutrients (mg/L)CO2 Content (%v/v)
0.00.51.53.0
Mg2+100.44100.2598.805109.13
SO42−451.28432.27459.06442.47
Na+259.45235.82265.57268.94
NO3620.58589.12680.73622.24
Ca2+99.3595.3298.4896.19
Cl165.78161.87185.80205.22
K+38.837.9847.7848.56
PO43−47.5825.6847.8847.21
Table 3. Biomass productivity and lutein content comparison.
Table 3. Biomass productivity and lutein content comparison.
Microalgal StrainOperation ModeCultivating ConditionsBiomass Productivity (g/L/day)Lutein Content (mg/g)References
Chlorella protothecoidesBatchHeterotrophic1.991.98[28]
Coccomyxa acidophilaBatchMixotrophic0.263.50[21]
Chlorella sorokinianaBatchAutotrophic0.843.0[23]
Scenedesmus sp.BatchMixotrophic0.381.05[60]
Chlorella sorokiniana Mb-1BatchMixotrophic1.033.86[15]
Scenedesmus obliquus FSP-3BatchAutotrophic0.924.52[25]
Chlorella zofingiensisBatchAutotrophic0.457.2[61]
Scenedesmus almeriensisContinuousAutotrophic0.875.5[27]
Scenedesmus almeriensisContinuousAutotrophic0.725.3[26]
Desmodesmus sp. F51Fed-batchAutotrophic0.655.5[62]
Coccomyxa onubensisSemi-continuousAutotrophic0.556.2[63]
Muriellopsis sp.BatchAutotrophic0.044.3[64]
Chlorella zofingiensisBatchAutotrophic0.883.4[64]
Chlorella minutissima MCC-27BatchAutotrophic0.576.05[24]
Chlorella minutissimaBatchAutotrophic0.676.37[7]
Scenedesmus almeriensisBatchAutotrophic0.138.54This study

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Molino, A.; Mehariya, S.; Karatza, D.; Chianese, S.; Iovine, A.; Casella, P.; Marino, T.; Musmarra, D. Bench-Scale Cultivation of Microalgae Scenedesmus almeriensis for CO2 Capture and Lutein Production. Energies 2019, 12, 2806. https://doi.org/10.3390/en12142806

AMA Style

Molino A, Mehariya S, Karatza D, Chianese S, Iovine A, Casella P, Marino T, Musmarra D. Bench-Scale Cultivation of Microalgae Scenedesmus almeriensis for CO2 Capture and Lutein Production. Energies. 2019; 12(14):2806. https://doi.org/10.3390/en12142806

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Molino, Antonio, Sanjeet Mehariya, Despina Karatza, Simeone Chianese, Angela Iovine, Patrizia Casella, Tiziana Marino, and Dino Musmarra. 2019. "Bench-Scale Cultivation of Microalgae Scenedesmus almeriensis for CO2 Capture and Lutein Production" Energies 12, no. 14: 2806. https://doi.org/10.3390/en12142806

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