Extraction of Phenolic Antioxidants From Four Selected Seaweeds Obtained From Sabah
Extraction of Phenolic Antioxidants From Four Selected Seaweeds Obtained From Sabah
Extraction of Phenolic Antioxidants From Four Selected Seaweeds Obtained From Sabah
*Corresponding author.
Email: tancp@upm.edu.my
Tel: +603-8946-8418; Fax: +603-8942-3552
2364 Fu et al./IFRJ 23(6): 2363-2369
antioxidant compounds from marine algae were time. After the extractions, seaweed extracts were
identified as phylopheophylin in Eisenia bicyclis filtered by a glass funnel with Whatman No. 1 filter
(Cahyana, Shuto and Kinoshita, 1992), phlorotannins paper (Whatman International, England). The clear
in Sargassum kjellamanianum (Yan et al. 1996) and solution of crude extract was collected in a light-
fucoxanthinin in Hijikia fusiformis (Yan et al., 1999). protected amber bottle (50 mL) for analysis without
Furthermore, there are evidences available to show further treatment. All extractions were carried out in
the potential protective effects of seaweed against replicates.
oxidative stress in target tissues and lipid oxidation
in foods (Rajamani et al., 2011). Factor 1: Ethanol concentration
Therefore, the main objective of this study was to 10 mL of ethanol and deionised water were mixed
evaluate the effect of extraction conditions (ethanol according to the ethanol concentration set in 5 levels
concentration, solid-to-solvent ratio, extraction (0, 25, 50, 75 and 100 %, v/v), added to 1 g of each
temperature and extraction time) in extracting sample. They were then placed in a water bath shaker
antioxidant compounds as well as antioxidant at 40 C at 150 rpm for 2 h.
capacities of the four selected seaweeds (Sargassum
polycystum, Eucheuma denticulatum , Kappaphycus Factor 2: Solid-to-solvent ratio
alvarezzi variance Buaya and Kappaphycus alvarezzi An amount of ethanol and deionised water (best
variance Giant) and determine the best extraction ethanol concentration obtained from section Factor
conditions for the seaweeds. 1) was added to each sample according to the solid-
to-solvent ratio set in 5 levels (1:10, 1:15, 1:20, 1:25
Materials and Methods and 1:30, w/v). They were then placed in a water bath
shaker at 40 C at 150 rpm for 2 h.
Seaweed cultivation and collection
Sargassum polycystum (SP) and Eucheuma Factor 3: Extraction temperature
denticulatum (ED) were commercially farmed An amount of ethanol and deionised water (best
seaweed in Semporna, Sabah. They were harvested ethanol concentration obtained from section Factor
at week 6 (maturity stage). Kappaphycus alvarezii 1) were added to each sample according to the best
variance Giant (KAG) and Kappaphycus alvarezii solid-to-solvent ratio obtained from section Factor 2.
variance Buaya (KAB) were tissue cultured seaweed, They were then placed in a water bath shaker at 5
grown in Universiti Malaysia Sabah (Kota Kinabalu, different temperatures (25, 35, 45, 55 and 65C) at
Malaysia). 1.0 g of explants was cultured in-vitro 150 rpm for 2 h.
for 10 - 12 weeks, producing 50.0 g of seedlings to
acclimatize in the open sea. They were harvested at Factor 4: Extraction time
week 16 (maturity stage). Seaweeds were cleaned An amount of ethanol and deionised water (best
under running water and air-dried for 2 days. Then, ethanol concentration obtained from section Factor
they were placed in oven at 60 C until they were 1) were added to each sample according to the best
completely dry. Dried seaweed were packed and solid-to-solvent ratio obtained from section Factor
delivered to Universiti Putra Malaysia (Serdang, 2. They were then placed in a water bath shaker at
Malaysia) for future analysis. the best temperature of each sample obtained from
section Factor 3 at 150 rpm for a range of time set in
Sample preparation 5 levels (1, 2, 3, 4 and 5 h).
500 g of dried seaweeds were ground in a
laboratory grinder (Mikro-Feinmuhle-Culatti. MFC Total phenolic content (TPC) assay
grinder, Janke and Kunkel GmbH and Co., Staufen,. Total phenolic content (TPC) was determined
Germany) with a particle size of 0.08 mm. Powdered using Folin-Ciocalteu (F-C) assay (Lim et al., 2007)
samples were then vacuum-packed and stored in dark 500 L of crude extracts obtained from extraction
for further research. were added into Eppendorf falcon tubes (2 mL)
followed by 500 L of Folin-Ciocalteus reagent
Sample extraction (diluted 10 times with water). After 4 min, 400 L
1 g of powdered sample of each species of of 7.5% (w/v) sodium carbonate were added. The
seaweeds was accurately weighed into conical flasks blank was prepared by replacing 500 L of sample
(50 mL). The extraction processes were carried out with 500 L of deionised water. Subsequently, the
by varying the experiment parameters for ethanol falcon tubes were vortexed for 10 s with vortex mixer
concentration, solid-to-solvent ratio, temperature and (VTS-3000L, LMS, Japan). They were incubated
Fu et al./IFRJ 23(6): 2363-2369 2365
in the dark environment at room temperature for 5, Secomam, France). Both the crude extracts and
2 h. Absorbance was measured against the blank negative control were carried out in triplicate. Trolox
reagent at 765 nm using UV light spectrophotometer solution was used to calibrate the standard curve.
(Model XTD 5, Secomam, France). Each extract The mean SD results of triplicate analyses were
was analyzed in triplicate and TPC were expressed expressed as mol trolox equivalent per 100 g dried
as gallic acid equivalent (GAE) in mg per 100 g dry sample (mol TEAC/100 g dried sample).
weight (DW).
ABTS radical scavenging capacity (%) = [1 (Ao /
Total flavonoid content (TFC) assay A1)] 100 % (1)
The determination of flavonoids was based on
the procedures described in the study (Ozsoy et Where Ao is A734 of the crude extract; A1 is A734 of
al., 2008) with slight modifications. 50 L of crude negative control in ethanolic ABTS solution.
extract added to 250 L of deionised water, followed
by the addition of 15 L of 5% sodium nitrite in 2,2-diphenyl-1-picrylhydrazyl (DPPH) radical
Eppendorf falcon tubes (2 mL). After 6 min, 30 L scavenging capacity assay
of 10% aluminium chloride hexahydrate was added Antioxidant capacity was determined by
into the mixture and was allowed to stand for further measuring the scavenging activity of the radical,
5 min. Then, 100 L of 1 M sodium hydroxide and 2-diphenyl-1-picrylhydrazyl (DPPH) based on the
55 L of deionised water were added. The blank was method (Saha et al., 2004) with slight modifications.
prepared by replacing the 50 L sample with 50 L 25 L of undiluted crude extract was added to 975
of deionised water. The falcon tubes were mixed L of ethanolic DPPH in the Eppendorf falcon
thoroughly by using a vortex mixer (VTS-3000L, tubes and vortexed for 1 min using the vortex mixer
LMS, Japan) for 10 s. Then, absorbance readings (VTS-3000L, LMS, Japan). They are allowed to
were immediately taken at 510 nm using the UV stand in a dark environment at room temperature
light spectrophotometer (Model XTD 5, Secomam, for 30 min. Absorbance was measured at 517 nm
France). Each extract was analyzed in triplicate and using UV light spectrophotometer (Model XTD 5,
TFC were expressed as catechin equivalent (CE) in Secomam, France). Absolute ethanol was used as
mg per 100 g dry weight (DW). blank. Absorbance of negative control (25 L of
absolute ethanol and 975 L of ethanolic DPPH) and
2,2-azinobis-3-ethylbenzothiazoline-6-sulfonic acid absorbance of blank were also measured at 517 nm.
(ABTS) radical scavenging capacity assay Both sample and negative control were analyzed in
Antioxidant capacity was determined by triplicate. Trolox solution was used to calibrate the
measuring the scavenging activity of the radical standard curve. The mean SD results of triplicate
2,2-azinobis-3-ethylbenzothiazoline-6-sulfonic acid analyses were expressed as mol trolox equivalent
(ABTS) based on the method (Surveswaran, 2007) per 100 g dried sample (mol TEAC/100 g dried
with slight modifications. 10 mL of 7 mM ABTS sample). The capability to scavenge the DPPH
solution and 10 mL of 2.45 mM potassium persulfate radicals was calculated by using the equation below.
(K2S2O8) solution were transferred into a 100 mL
light protected amber bottle. The solution were DPPH radical scavenging capacity (%) = [1 (Ao
mixed by vortex mixer (VTS-3000L, LMS, Japan) / A1)] 100 % (2)
for 10 s and allowed to stand in a dark environment
at room temperature for 16 h to give a dark blue Where Ac is A517 of the crude extract; A1 is A517 of
solution. This solution was diluted with 95% ethanol negative control in ethanolic DPPH solution.
until the absorbance was equilibrated to 0.7 ( 0.02)
at 734 nm. 975 L ABTS solution with equilibrated Statistical analysis
absorbance of 0.7 0.02 was added to 25 L of the The experimental results were analyzed with
undiluted extract in an Eppendorf falcon tube (2 Microsoft Office Excel 2007 (version 12.0, Microsoft
mL). Negative control was prepared by replacing Corp., USA) and Minitab statistical software (Version
25 L of undiluted crude extract with 25 L of 95% 16, Minitab Inc., USA). Every measurement of each
ethanol whereas blank was prepared by using 95% assay was performed in triplicate, and every sample
ethanol solely. The reaction was allowed to occur was duplicated. All values were expressed as the
at room temperature for 6 min and the absorbance means standard errors (SE) of six measurements
at 734 nm was immediately recorded against blank (n=6) and the calculations were performed using
using the UV light spectrophotometer (Model XTD Microsoft Office Excel 2007. One-way analysis
2366 Fu et al./IFRJ 23(6): 2363-2369
Results
seaweeds, releasing more bound phenols into the after a particular time (Pinelo et al., 2006). Results
solvent (Spigno et al., 2007). Furthermore, a higher of antioxidant compounds and antioxidant capacities
extraction temperature reduces solvent viscosity and were compatible; this is likely because the phenolic
surface tension, thus, accelerating the extraction compounds extracted are active. Prolonged extraction
process and increasing the diffusion coefficient. time leads to the decomposition of active compounds
Additionally, studies showed that the rate of recovery (Liyana-Pathirana and Shahidi, 2005) due to long
of thermally stable antioxidants at an elevated exposure to the environment (i.e., temperature, light
temperature (up to 65C) was greater than the rate and oxygen) (Lafka, Sinanoglou and Lazos, 2007),
of decomposition of less soluble phenolics (Liyana- increasing the chance that the phenolic compounds
Pathirana and Shahidi, 2005). Despite an increasing become oxidized, which decreases the antioxidant
in the amount of antioxidant compounds extracted capacity. Furthermore, undesirable reactions such as
at a higher temperature, Figure 3 shows that ABTS enzymatic oxidation and polymerization might be
does not significantly change during extraction favoured by the extended extraction time (Biesaga
at high temperature. This is likely because the and Pyrzynska, 2013). The best extraction times were
bioavailability of phenolics or bioactive compounds set as follows: for SP (2 h), KAB (4 h), KAG (5 h)
was negatively affected by the relatively high and ED (3 h).
temperature. Nevertheless, the antioxidant capacity
of the sample could experience thermal destruction Conclusions
(Spigno et al., 2007), in turn reducing its antioxidant
activities, therefore resulting in almost no change The best extraction conditions (ethanol
in ABTS. Nevertheless, DPPH was significantly concentration, solid-to-solvent ratio, extraction
increased for all four seaweeds. DPPH is known to temperature and time) for four selected seaweeds were
react well with low molecular weight compounds successfully identified by single-factor experiments.
(Paixo, 2007). Furthermore, DPPH radicals reacted However, Sargassum polycystum possessed the most
with phenolic compounds even at high temperatures. antioxidant compounds and capacities amongst the
It is concluded that the four seaweeds contain a high four species. The results obtained from this study are
proportion of heat-resistant low molecular weight important in the development of industrial extraction
active phenolic compounds. processes of phenols from seaweed. Purification and
identification of the phenolic components in seaweed
Effects of extraction time can be done to identify phenolic compounds that are
Extraction time is determined purely by the responsible for the antioxidant characteristics.
molecular size, quantity and chemical structure of
the phenolic compounds in the sample (Chirinos et Acknowledgment
al., 2007). Different species of seaweeds contain a Financial support of this work by Universiti
different composition of bioactive compounds as Putra Malaysia through research funding is gratefully
well as of phenolic compounds. For instance, some acknowledged.
phenols require a longer extraction time because
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