Bienvenida
Gilbert-López
a,
José A.
Mendiola
a,
Javier
Fontecha
b,
Lambertus A. M.
van den Broek
c,
Lolke
Sijtsma
c,
Alejandro
Cifuentes
a,
Miguel
Herrero
a and
Elena
Ibáñez
*a
aFoodomics Laboratory, Bioactivity and Food Analysis Department, Institute of Food Science Research (CIAL-CSIC), Campus de Cantoblanco, Calle Nicolás Cabrera 9, 28049 Madrid, Spain. E-mail: elena.ibanez@csic.es
bBioactivity and Food Analysis Department, Lipid Group, Institute of Food Science Research (CIAL-CSIC), Campus de Cantoblanco, Calle Nicolás Cabrera 9, 28049 Madrid, Spain
cWageningen UR Food & Biobased Research, P.O. Box 17, 6700 AA Wageningen, The Netherlands
First published on 16th July 2015
An algae-based biorefinery relies on the efficient use of algae biomass through its fractionation of several valuable/bioactive compounds that can be used in industry. If this biorefinery includes green platforms as downstream processing technologies able to fulfill the requirements of green chemistry, it will end-up with sustainable processes. In the present study, a downstream processing platform has been developed to extract bioactive compounds from the microalga Isochrysis galbana using various pressurized green solvents. Extractions were performed in four sequential steps using (1) supercritical CO2 (ScCO2), (2) ScCO2/ethanol (Gas Expanded Liquid, GXL), (3) pure ethanol, and (4) pure water as solvents, respectively. The residue of the extraction step was used as the raw material for the next extraction. Optimization of the ScCO2 extraction was performed by factorial design in order to maximize carotenoid extraction. During the second step, different percentages of ethanol were evaluated (15%, 45% and 75%) in order to maximize the extraction yield of fucoxanthin, the main carotenoid present in this alga; the extraction of polar lipids was also an aim. The third and fourth steps were performed with the objective of recovering fractions with high antioxidant activity, eventually rich in carbohydrates and proteins. The green downstream platform developed in this study produced different extracts with potential for application in the food, pharmaceutical and cosmetic industries. Therefore, a good approach for complete revalorization of the microalgae biomass is proposed, by using processes complying with the green chemistry principles.
Isochrysis galbana is a small marine flagellate (Phylum: Haptophyta) widely used in aquaculture as a PUFA-rich microalga.5 It is commercially produced as feed for the early larval stages of mollusks, fish, and crustaceans. In fact, I. galbana cells produce antibacterial substances, which increase the toxicity of free fatty acids such as eicosapentanoic acid (EPA) to several pathogens, without the use of chemicals that might harm organisms under culture conditions or the environment.6 Besides polyunsaturated fatty acids, I. galbana is a valuable source of proteins, carbohydrates and photosynthetic pigments such as chlorophyll a and fucoxanthin.7
Fucoxanthin, a major carotenoid present in the chloroplasts of brown seaweeds, contributes to more than 10% of the estimated total production of carotenoids in nature. Although fucoxanthin is clearly a valuable pigment with various health benefits, its use has been limited due to the low extraction efficiency from marine materials and the difficulty to synthesize it. In this respect, algae, such as I. galbana, can be considered as a potential source of fucoxanthin.8
In order to fully develop the microalgae-based biorefinery concept, new aspects related to technologies for extraction, isolation and fractionation of the biomass into multiple products (lipids, proteins, polysaccharides, bioactives, etc.) should be studied. Also, steps into integrated approaches for multi-product biorefinery should be taken into account to improve the efficiency and minimize the energy and resource consumption,9 especially when green chemistry principles and sustainability issues are to be considered.
Traditionally, extraction of lipophilic compounds from algae, such as carotenoids and lipids, has been performed by means of toxic organic solvents like hexane. Nowadays there is a demand for fast, selective, efficient and greener processes able to provide extractions with high yields; besides, the costs associated have to be reduced, for instance, by minimizing the removal of solvent residues.
High-pressure extractions such as supercritical fluid extraction (SFE) and pressurized liquid extraction (PLE) using GRAS (generally recognized as safe) solvents such as CO2, ethanol or water, have emerged as promising alternatives to face these challenges.10 This was the subject of a specifically devoted workshop on Supercritical Fluids and Energy that was conducted in Brazil in December 2013,11 with the idea of assessing the potential of supercritical (pressurized fluids in general) technologies in the fields of energy, materials science, process technology, green chemistry and sustainable technologies.
SFE offers a fast extraction rate, high selectivity and is an ecofriendly technology with minimal or no use of organic solvents, although the low polarity of supercritical CO2 (ScCO2) limits its applications. ScCO2 has been reported as an interesting approach for the extraction of lipids with antimicrobial activity from the microalgae Chaetoceros muelleri,12 n-3 fatty acids from the seaweed Hypnea charoides,1 lutein and β-carotene from Scenedesmus almeriensis13 and fucoxanthin from the seaweed Undaria pinnatifida14 and Sargassum muticum,15 among others. In this latter application, the addition of ethanol as a co-solvent improved the yield of fucoxanthin in both algal species.15,16
Ethanol is often used as a modifier or a co-solvent of ScCO2 in order to overcome the CO2 limitations towards the extraction of medium polarity bioactive compounds. For instance, CO2 modified with ethanol has been applied for the extraction of astaxanthin from Haematococcus pluvialis17 and various pigments from Spirulina platensis.18 The use of a co-solvent at a higher concentration allows working in the region of gas-expanded liquids (GXLs),19 which is a promising intermediate between PLE and SFE for the extraction of medium or high-polarity compounds. Carbon dioxide expanded ethanol (CXE) has been recently used to obtain astaxanthin enriched extracts from H. pluvialis.20
Pressurized liquid extraction has demonstrated an interesting potential for extracting bioactive compounds from macro- and microalgae.10,20 This extraction technique allows obtaining higher yields than those achieved by conventional extraction techniques, in a shorter time and with less solvent consumption.10 PLE using ethanol has been reported for the extraction of carotenoids from Neochloris oleoabundans,22Dunaliella salina2 and Chlorella ellipsoidea.3 In addition, 90% ethanol was used for the extraction of fucoxanthin from Eisenia bicyclis23 and the mixture of ethanol/limonene (1:
1, v/v) has been proposed as a green approach for PLE extraction of lipids from microalgae.9
In the present study, we propose an integrated sequential extraction process based on the use of green compressed fluids, in increasing order of polarity, for the fractionation of bioactive compounds from the microalga I. galbana, as an approach to develop a microalgae biorefinery procedure.21 The developed process comprises the sequential extraction with ScCO2, CO2-expanded ethanol, PLE using ethanol and subcritical water extraction. Finally, different tools are employed for the chemical and functional characterization of the obtained fractions.
Freeze-dried samples of I. galbana (T-ISO) were obtained from Fitoplancton Marino S.A. (Cadiz, Spain), and stored under dry and dark conditions until further use. I. galbana was grown in outdoor vertical 400 L reactors. Air containing 2% CO2 is injected into the reactors, while natural light–dark cycles and ambient temperature are used (10–11 h of light, temperatures ranging from 10 to 22 °C). These reactors are inoculated with cultures grown in growth chambers under the standard conditions of Fitoplancton Marino S.A.
Extractions were performed in four sequential steps using (1) supercritical CO2 (ScCO2), (2) ScCO2/ethanol (CXE), (3) pure ethanol (PLE), and (4) pure water (PLE) as solvents, respectively.
The different extraction steps were selected in increasing order of polarity (ScCO2 < CXE < ethanol < water), to exhaust the microalgae biomass of extractable compounds, fractionating its components in order to give valuable isolated fractions.
Step 1: ScCO2 extraction conditions were optimized using a response surface methodology (RSM) to reveal the functional relationship between the extraction responses (extract yield, total carotenoids and total chlorophylls of extracts) and independent variables (extraction pressure and extraction temperature). A three-level factorial design (32) was used. The studied factors were pressure (100–300 bar) and temperature (40–60 °C). To determine the extraction time of this step, a kinetic study was performed at the central point of the experimental design (200 bar, 50 °C), collecting the extract every 20 min and calculating the percentage of the extractable material. The parameters of the model were estimated by multiple linear regression using the Statgraphics Centurion XVI software (Statpoint Technologies, Warrenton, Virginia, USA), which allows both the creation and the analysis of experimental designs.
Step 2: The second step involved a carbon dioxide expanded ethanol (CXE) extraction in order to increase the polarity of the extracted fraction. This step was carried out in the residual biomass from the first step. The pressure was set at 70 bar, while the temperature was maintained at 50 °C to match the optimum temperature used in the first step in order to avoid unnecessary heating or cooling of the system and thus, minimizing operational costs. Three different percentages of ethanol were tested, 15%, 45% and 75%; the extraction time selected was 1 h. The extraction in the center point (45% EtOH) was performed in triplicate for the precision study.
Step 3: The residue from the previous extractions was extracted again using PLE at 100 bar and 80 °C for 30 min, using pure ethanol as an extracting solvent.
Step 4: In the fourth and last step, PLE was employed using water as a solvent under the same extraction conditions employed in step 3 (100 bar and 80 °C for 30 min).
All the collection recipients were protected from light and 0.1% (w/v) BHT was added to the extracts. Finally, the solvent (ethanolic extracts) was evaporated in a rotary evaporator (Buchi, Flawil, Switzerland) or the samples were freeze-dried (water extracts). The extracts were stored at −80 °C to prevent degradation until analysis.
For the calibration curve, twelve different concentrations of fucoxanthin in ethanol, ranging from 0.97 × 10−4 to 0.2 mg mL−1, were analyzed using the LC-DAD instrument.
The neutral sugar composition was determined according to de Keijzer et al.29 by high performance anion exchange chromatography (HPAEC) using an ICS-3000 ion chromatography HPLC system equipped with a CarboPac PA-1 column (2 × 250 mm) in combination with a CarboPac PA guard column (2 × 25 mm) and a pulsed electrochemical detector in pulsed amperometric detection mode (Dionex, Sunnyvale, USA). A flow rate of 0.3 mL min−1 was used and the column was equilibrated with 17 mM NaOH. Elution was performed in two steps: 0–0.5 min, 17–0 mM NaOH and 0.5–35 min, 0–35 mM NaOH in 0–350 mM sodium acetate. Detection of the monomers was possible after the post column addition of 0.5 M sodium hydroxide (0.2 mL min−1). Before analysis samples were diluted (1:
3) in water and to a 1 mL sample, 2.5 μL 0.1% (w/v) bromophenol blue in ethanol was added. To adjust the pH, solid barium carbonate was added until a clear magenta color was obtained. Subsequently, the solution was filtered using a 0.45 μm PTFE filter. Fucose was used as an internal standard in the case where fucose was not present in the sample. Analysis was performed in duplicate.
Experimental conditions of the different extraction steps were either optimized or selected according to the previous results obtained in our laboratory for the extraction of similar compounds in other microalgae samples. Moreover, minimization of operational and energy costs was also considered in the integrated process, thus minimizing heating/cooling operations and collection or treatment of the microalgae biomass.
Extract (P.T) | P, bar | T, °C | Yield (%) | mg carotenoids per g ext. | mg chlorophylls per g ext. |
---|---|---|---|---|---|
100.40 | 100 | 40 | 0.52 | 2.2 ± 0.2 | 3.1 ± 0.4 |
100.50 | 100 | 50 | 0.31 | 2.1 ± 0.2 | 3.3 ± 0.1 |
100.60 | 100 | 60 | 0.56 | 1.8 ± 0.1 | 2.7 ± 0.2 |
200.40 | 200 | 40 | 2.56 | 6.39 ± 0.09 | 4.6 ± 0.2 |
200.50 | 200 | 50 | 2.49 | 5.45 ± 0.08 | 1.9 ± 0.0 |
200.50 | 200 | 50 | 2.41 | 5.0 ± 0.2 | 1.22 ± 0.02 |
200.50 | 200 | 50 | 2.35 | 5.64 ± 0.07 | 1.24 ± 0.04 |
200.60 | 200 | 60 | 2.55 | 5.76 ± 0.06 | 0.8 ± 0.0 |
300.40 | 300 | 40 | 1.11 | 4.9 ± 0.2 | 1.09 ± 0.04 |
300.50 | 300 | 50 | 5.00 | 16.2 ± 0.3 | 4.5 ± 0.0 |
300.60 | 300 | 60 | 1.77 | 15.8 ± 0.8 | 2.70 ± 0.04 |
After performing the ANOVA (evaluation of the experimental design with Statgraphics Centurion XVI software) for each of the responses (data not shown), the statistical model was fitted and optimized. Considering that the goal of the first step was to maximize the yield and carotenoid content, while minimizing chlorophylls, a desirability function was selected for meeting these goals and giving to all responses the same weight. As shown in Fig. 1, this function provided an optimum of 299 bar and 51 °C to increase the extraction yield and carotenoid content while minimizing the chlorophyll content. The optimization desirability was equal to 0.66, while the values predicted by the model under the optimum extraction conditions were 4.41% for extraction yield, carotenoid content of 16.4 mg carotenoids per g extract and 4.3 mg chlorophylls per g extract for total chlorophylls. Experiments under the optimum conditions provided experimental values close to that predicted by the statistical model (Table 1, experiment 300.50).
![]() | ||
Fig. 1 Surface of the desirability function in terms of pressure and temperature obtained to maximize the yield and carotenoid content, while minimizing the chlorophyll content. |
Steps 3 and 4 were performed under PLE conditions, using ethanol and water, respectively, which implies an increasing order of polarity. At this point, different bioactive compounds were sought such as polar lipids, proteins and carbohydrates. Moreover, the final objective was to extract all the valuable components contained in the microalgae biomass attaining different fractions and minimizing the leftovers. The extraction values selected included a pressure of 100 bar and a temperature of 80 °C. These values were maintained relatively low in order to avoid degradation of compounds.
The scheme of the overall extraction process, along with the target compounds expected in each step is depicted in Fig. 2.
Peak # | t R (min) | Identification | UV-Vis max wavelength (nm) | Parent ion(s) | Main fragments |
---|---|---|---|---|---|
a Identification confirmed by comparison with commercial standards. | |||||
3 | 6.79 | Fucoxanthinol | 442 | — | |
4 | 7.63 | E-Fucoxanthina | 448 | 641.7 [M + H–H2O]+ | 641.6, 549.7 |
581.9 [M + H–H2O-60]+ | 563.5, 489.5 | ||||
5 | 8.13 | 13(′)Z-Fucoxanthin | 332, 442 | — | |
6 | 8.43 | 13(′)Z-Fucoxanthin | 332, 438 | — | |
7 | 10.61 | 9(′)Z-Fucoxanthin | 442 | — | |
9 | 13.82 | Carotenoid | 322, 422, 448 | — | |
10 | 15.07 | Carotenoid | 422, 446, 472 | — | |
11 | 15.64 | Diadinoxanthin | 428, 446, 474 | — | |
12 | 16.55 | Diadinoxanthin 5,8-epoxy derivative | 404, 428, 456 | 506.8 | 268.6 |
583.5 [M + H]+ | 565.6 | ||||
13 | 17.18 | Diadinoxanthin 5,8-epoxy derivative | 404, 428, 456 | 583.7 [M + H]+ | 565.6 |
14 | 18.85 | Carotenoid | 400, 424, 450 | — | |
16 | 19.35 | Carotenoid | 426, 450, 476 | — | |
17 | 22.90 | Carotenoid | 460 | — | |
18 | 25.92 | Carotenoid | 460 | — | |
19 | 26.70 | Carotenoid | 405, 426, 454 | — | |
20 | 28.31 | Carotenoid | 424, 450, 478 | — | |
21 | 29.14 | Carotenoid | 340, 420, 444, 470 | — | |
23 | 30.7 | Pheophytin a′ | 408, 666 | 871.9 [M]+ | 593.7 |
593.5 [M − C20H38]+ | 533.6 | ||||
25 | 32.99 | Carotenoid | 452, 476 | — | |
27 | 34.5 | Carotenoid | 446, 472 | — |
Peak # | t R (min) | Identification | UV-Vis max. wavelengths (nm) | Parent ion(s) | Main fragments |
---|---|---|---|---|---|
a Identification confirmed by comparison with commercial standards. | |||||
3 | 6.57 | Fucoxanthinol | 448 | 600.0 [M + H–H2O]+ | 581.6, 563.5 |
617.7 [M + H]+ | 599.5, 581.6 | ||||
4 | 7.63 | E-Fucoxanthina | 448 | 641.7 [M + H-18]+ | 641.6, 623.6, 581.6, 563.6, 549.6 |
581.6 [M + H–H2O-60]+ | 563.5, 489.5 | ||||
5 | 8.13 | 13(′)Z-Fucoxanthin | 332, 442 | 641.7 [M + H–H2O]+ | 641.6, 549.6 |
6 | 8.43 | 13(′)Z-Fucoxanthin | 581.9 [M − H2O-60 + H]+ | 563.5, 489.5 | |
8 | 13.36 | Carotenoid | 454 | — | |
11 | 15.57 | Diadinoxanthin | 420, 445, 475 | 583.6 [M + H]+ | 565.6, 547.6, 491.5 |
565.6 [M − H2O]+ | 547.6 | ||||
12 | 16.48 | Diadinoxanthin 5,8-epoxy derivative | 404, 428, 456 | 583.7 [M + H]+ | 565.6, 547.6, 491.5 |
13 | 17.10 | Diadinoxanthin 5,8-epoxy derivative | 565.7 [M − H2O]+ | 547.6 | |
15 | 18.88 | Chlorophyll aa | 432, 664 | 894.0 [M + H]+ | 615.7 |
567.8 | 549.6 | ||||
17 | 20.37 | Chlorophyll a′ | 432, 664 | 894.6 [M + H]+ | 615.5 |
22 | 29.72 | Pheophytin a | 408, 668 | 872.0 [M]+ | 593.6 |
593.6 [M − C20H38]+ | 533.6 | ||||
23 | 30.40 | Pheophytin a′ | 408, 666 | 871.9 [M]+ | 593.5, 533.5 |
593.5 [M − C20H38]+ | 533.6 | ||||
24 | 32.79 | Chlorophyll c1-like | 448, 582, 632 | — | |
26 | 33.39 | Chlorophyll c2-like | 456, 584, 634 | — | |
28 | 38.18 | Chlorophyll c2-like | 456, 584, 632 | — |
Since the percentage of ethanol in the CXE step did not affect the chromatographic profile, the HPLC-DAD chromatogram obtained for 45% ethanol in CO2 has been used to illustrate the identification of carotenoids and chlorophylls in the second step of the sequential extraction (see Fig. S1, step 2, ESI†). Fucoxanthin was again the main compound present in the extracts, but several chlorophylls and chlorophyll derivatives were also detected (see Table 3). The protonated molecule [M + H]+ was not observed for any of the fucoxanthin isomers. Interestingly, E- and 13(′)Z-fucoxanthin isomers showed the same parent ions, corresponding to the dehydrated molecule ([M + H–H2O]+) and a fragment corresponding to a loss of 78 Da consistent with the sequential losses of the C-3 carbomethoxy group (acetic acid) and a water molecule. MS/MS analyses of these ions exhibited a loss of 92 Da that could be attributed to the loss of toluene from the polyene chain. Fucoxanthin metabolite fucoxanthinol (Table 3, peak 3) was tentatively identified by its protonated molecule. MS/MS analysis of fucoxanthinol led to dehydration of the molecule.
Diadinoxanthin (peak 11) was also identified in the extracts by the presence of its typical ions at m/z 583.6 ([M + H]+) and m/z 565.6 ([M + H–H2O]+). The same MS spectrum was obtained for peaks 12 and 13, but for these peaks, a hypsochromic shift of 15–20 nm was observed in all UV maxima. Therefore, these compounds can be tentatively identified as 5,8-epoxy derivatives of diadinoxanthin, according to Crupi et al.34
Chlorophyll a and its epimer chlorophyll a′ (peaks 15 and 17) lost the phytyl group (C20H39)35 and showed the same fragment, m/z 615.5, which corresponds to the chlorophyllides a and a′, respectively. Besides, the loss of the phythyl group (C20H39) can also be used for the identification of pheophytins a and a′ (peaks 22 and 23).36 The identification of chlorophyll a in the extract was confirmed by using a commercial standard, and thus peak 10 was assigned to chlorophyll a′. The same elution order was considered for pheophytins a and a′. Several chlorophyll c pigments were tentatively identified in the extracts, although no information could be obtained from the MS in this case. Nevertheless, they were grouped in chlorophyll c1-like (peak 24) and chlorophyll c2-like (peaks 26 and 28) compounds, on the basis of their UV-VIS spectra, since the band ratios (II/III) and the position of maxima are different. The ratios of band II (at ∼630 nm) to band III (at ∼580 nm) intensities are >1 for Chl c1-like chromophores, ≈1 for Chl c2-like chromophores and <1 for Chl c3-like chromophores.37
The vast majority of total fucoxanthin is formed by E-fucoxanthin, while the amount of the other isomers remains very low under the different extraction conditions, except for extractions at 300 bar and 60 °C (data not shown). Under these conditions, the sum of 13(′)Z isomer concentration is higher, although still extremely low compared to E-isomers, which could be due to an increase in their solubility under these extraction conditions. In general, the highest extraction of fucoxanthin occurred at 300 bar and 50 °C, over the experimental range that was explored.
Table 4 shows the quantification of fucoxanthin isomers, the total carotenoid amount and the total chlorophyll content of the extracts obtained after each step of the sequential integrated process. The highest total chlorophyll content (expressed as chlorophyll a) was found in the CXE extract obtained using 15% ethanol, while the highest content of total carotenoids (expressed as fucoxanthin) was obtained in the CXE extract containing 75% ethanol. In any case, total carotenoids and chlorophylls extracted with carbon dioxide expanded ethanol were higher than total carotenoids and chlorophylls extracted with acetone (146.58 vs. 57.19 mg per g extract and 96.56 vs. 44.48 mg per g extract, respectively, for carotenoids and chlorophylls). On the other hand, the highest content of E-fucoxanthin was found in the CXE extract containing 45% ethanol (40.69 ± 2.28 mg per g extract), and is comparable to the concentration of E-fucoxanthin obtained with acetone conventional solid-liquid extraction (44.60 ± 2.68 mg per g extract). Regarding Z isomers, the sum of 13Z + 13′Z isomers, as well as the amount of 9(′)Z isomers, is higher in acetone extracts, compared to CXE extracts. The content of fucoxanthinol, however, is comparable between acetone and CXE extracts. On the other hand, pooling both ethanol containing extracts (steps 2 and 3), the content of fucoxanthin isomers surpasses acetone extractions, thus validating the use of this new type of green technology for extraction of high value-added compounds.
Samplea (%Step) | Yield (%) | Fucoxanthin isomers, mg per g extract | Total carotenoids, mg per g extract | Total chlorophylls, mg per g extract | TEAC (mmol g−1) | |||
---|---|---|---|---|---|---|---|---|
E-Fucox | 13Z + 13′Z-fucox | Fucoxanthinol | 9(′)Z-Fucox (2) | |||||
a The name of the extracts corresponds to the %EtOH in the second step. Sequential steps have been named as 1 (ScCO2), 2 (CXE), 3 (PLE EtOH) and 4 (PLE water). b Average results from three independent extractions under the same conditions. | ||||||||
15.1 | 3.5 | 5.6 ± 0.4 | 0.22 ± 0.01 | 0.005 ± 0.001 | 0.026 ± 0.002 | 8.6 ± 0.2 | 3.0 ± 0.1 | |
15.2 | 6.3 | 36.8 ± 0.4 | 1.0 ± 0.1 | 0.26 ± 0.03 | — | 66.2 ± 0.7 | 65.4 ± 0.4 | |
15.3 | 15.0 | 21.8 ± 0.2 | 1.46 ± 0.03 | 0.20 ± 0.02 | <LOQ | 42.2 ± 1.2 | 39 ± 1 | 0.639 ± 0.006 |
15.4 | 5.8 | 0.870 ± 0.002 | 0.055 ± 0.003 | <LOQ | 0.0206 ± 0.0003 | 1.05 ± 0.07 | 1.10 ± 0.04 | 0.33 ± 0.01 |
45.1b | 4.4 ± 0.5 | 8 ± 2 | 0.23 ± 0.08 | 0.014 ± 0.006 | 0.033 ± 0.022 | 11 ± 1 | 5.6 ± 0.1 | |
45.2b | 11 ± 1 | 41 ± 2 | 1.2 ± 0.1 | 0.25 ± 0.04 | <LOQ | 62 ± 2 | 53 ± 11 | |
45.3b | 4.8 ± 0.4 | 21 ± 2 | 1.6 ± 0.3 | 0.22 ± 0.05 | 0.07 ± 0.01 | 49 ± 10 | 41 ± 5 | 0.54 ± 0.04 |
45.4b | 4.4 ± 0.5 | 0.7 ± 0.5 | 0.05 ± 0.03 | <LOQ | 0.011 ± 0.005 | 1.4 ± 0.9 | 1.6 ± 0.9 | 0.29 ± 0.05 |
75.1 | 3.9 | 4.61 ± 0.04 | 0.144 ± 0.003 | 0.004 ± 0.001 | 0.023 ± 0.0002 | 5.856 ± 0.2 | 3.8 ± 0.1 | |
75.2 | 14.7 | 38.2 ± 0.3 | 1.12 ± 0.07 | 0.216 ± 0.005 | — | 91.9 ± 0.8 | 58.1 ± 0.4 | |
75.3 | 2.0 | 9.00 ± 0.02 | 0.99 ± 0.01 | 0.041 ± 0.004 | 0.053 ± 0.002 | 45.2 ± 0.7 | 32.8 ± 0.2 | 0.482 ± 0.006 |
75.4 | 3.1 | 1.18 ± 0.02 | 0.093 ± 0.007 | 0.004 ± 0.0003 | 0.03 | 3.6 ± 0.2 | 1.918 ± 0.124 | 0.30 ± 0.02 |
Acetone extractsb | 22.41 ± 0.09 | 44 ± 3 | 2.6 ± 0.4 | 0.23 ± 0.04 | 0.06 ± 0.04 | 57 ± 6 | 44 ± 4 |
It is worth mentioning that the content of E-fucoxanthin in any of the CXE extracts (36–43 mg g−1) was higher than that previously reported for I. galbana using acetone extraction39 and for Isochrysis sp., using conventional extraction with methanol.34
The sugar composition of ethanol and water PLE extracts was similar. Detailed results are shown in Table 5. Fucose, glucuronic acid, galacturonic acid, N-acetylglucosamine, N-acetylgalactosamine, glucosamine and galactosamine were not detected. Xylose (only present in CXE75-water) and mannose were found only in water extracts. A slightly higher amount of total sugars can be observed in the extracts obtained after CXE-75% ethanol compared to the extracts obtained after 15% and 45% ethanol. In any case, the total amount of sugars did not exceed 10% of the extract weight (see Fig. 4). Galactose is the main sugar in ethanol extracts, ranging from 5.69 to 6.68% of dry weight. In water extracts, galactose is present in a smaller amount (1.44–2.83% dry weight), while glucose is the main sugar found (3.91–4.11% dry weight).
15C | 15Da | 45Cb | 45Db | 75C | 75D | |
---|---|---|---|---|---|---|
a Duplicate sample was lost during analysis. b Average results from three independent extractions under the same conditions. c Ara is arabinose, Gal is galactose, Glc is glucose, Man is mannose, Rib is ribose and xyl is xylose. | ||||||
Arac | 0.19 ± 0.01 | 1.1 | 0.18 ± 0.01 | 1.0 ± 0.2 | 0.21 ± 0.01 | 1.6 ± 0.1 |
Galc | 5.7 ± 0.8 | 1.4 | 6.0 ± 0.1 | 2.1 ± 0.2 | 6.7 ± 0.1 | 2.8 ± 0.2 |
Glcc | 0.56 ± 0.03 | 4.1 | 0.5 ± 0.1 | 4.1 ± 0.3 | 1.16 ± 0.04 | 3.9 ± 0.4 |
Manc | 0 | 0.6 | 0 | 0.55 ± 0.07 | 0 | 0.59 ± 0.05 |
Ribc | 0.47 ± 0.01 | 0.4 | 0.45 ± 0.04 | 0.46 ± 0.01 | 0.54 ± 0.03 | 0.53 ± 0.04 |
Xylc | 0 | 0 | 0 | 0 | 0 | 0.69 ± 0.04 |
Total sugars | 6.9 ± 0.9 | 8.0 | 7.2 ± 0.1 | 8 ± 1 | 8.6 ± 0.2 | 10.1 ± 0.7 |
The results corresponding to the antioxidant capacity assay (expressed as TEAC, mmol of Trolox per g sample), are shown in Table 4. As can be seen, ethanol extracts contained twice the activity as water extracts. This observation cannot be directly related to the total content of sugars, which was similar in both water and ethanol extracts. However, a different composition of sugars in ethanol and water extracts can be expected. Since ethanol is commonly used to precipitate polymeric sugars, monomers or oligomers may be preferably present in ethanol extracts, while oligomeric and polymeric sugars can be expected in water extracts. The total content of protein was lower in ethanol extracts, but proteins extracted in ethanol can be different from proteins present in water extracts, and therefore the activity can be different, too. On the other hand, the amount of fucoxanthin and total carotenoids in ethanol extracts is more than two times higher than the concentration of carotenoids in water extracts. Consequently, despite the fact that there is no linear relationship between the carotenoid content and antioxidant activity, data seem to indicate that higher antioxidant activity in ethanol extracts might be related to the fucoxanthin and fucoxanthin isomer content; Zhang et al.40 and Sachindra et al.41 previously confirmed the potent antioxidant activity of these compounds by using different methods.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c5gc01256b |
This journal is © The Royal Society of Chemistry 2015 |