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Article

Effects of Seasonal Variability on the Physicochemical, Biochemical, and Nutritional Composition of Western Peninsular Malaysia Gracilaria manilaensis

by
Abdul Qudus Aroyehun
1,3,
Kishneth Palaniveloo
3,*,
Farid Ghazali
2,
Mohammed Rizman-Idid
3 and
Shariza Abdul Razak
1,*
1
Nutrition and Dietetics Program, School of Health Sciences, Health Campus. Universiti Sains Malaysia, Kubang Kerian 16150, Kelantan, Malaysia
2
Biomedicine Program, School of Health Sciences, Health Campus. Universiti Sains Malaysia, Kubang Kerian 16150, Kelantan, Malaysia
3
Institute of Ocean and Earth Sciences, University of Malaya, Jalan Universiti, Kuala Lumpur 50603, Wilayah Persekutuan Kuala Lumpur, Malaysia
*
Authors to whom correspondence should be addressed.
Molecules 2019, 24(18), 3298; https://doi.org/10.3390/molecules24183298
Submission received: 18 August 2019 / Revised: 2 September 2019 / Accepted: 3 September 2019 / Published: 10 September 2019
(This article belongs to the Special Issue Physicochemical Properties of Food)

Abstract

:
This study evaluated the effect of seasonal variation on the physicochemical, biochemical, and nutritional composition of Gracilaria manilaensis. Sampling was designed during the main monsoon seasons in Malaysia—the Southwest monsoon (SWM) and Northeast monsoon (NEM)—to understand the intraspecific variation (p < 0.05). Carbohydrates, protein, and dietary fiber were found to be higher in NEM–G. manilaensis, whereas a higher ash content was quantified in SWM–G. manilaensis. No significant differences were found in crude lipid and moisture content (p > 0.05). Vitamin B2 was calculated as (0.29 ± 0.06 mg 100 g−1) and (0.38 ± 0.06 mg 100 g−1) for the NEM and SWM samples, respectively (p < 0.05). The fatty acid profile showed the dominance of saturated fatty acids (SFAs)—palmitic acids, stearic acid, and myristic acid—while the mineral contents were found to be good sources of calcium (1750.97–4047.74 mg 100 g−1) and iron (1512.55–1346.05 mg 100 g−1). Tryptophan and lysine were recorded as the limiting essential amino acids (EAAs) in NEM G. manilaensis, while leucine and phenylalanine were found to be the limiting EAAs in the SWM samples. None of the extracts exhibited antibacterial properties against the screened strains. The study concluded that seasonal changes have a great effect on the biochemical composition of G. manilaensis.

1. Introduction

Food security is a global concern due to the increasing human population amid dwindling natural resources in a fragile natural environment [1]. An estimated 1 billion people currently suffer from malnutrition due to insufficient dietary energy, accessibility, and micronutrient undernourishment [2,3]. However, in a renewed interest to exploit new resources to meet the growing demand for food and value-added nutritional ingredients, marine macroalgae (commonly referred to as seaweed) seem to meet the requirements [4].
The red seaweed, phylum Rhodophyta, is abundant, with nearly 6000 species globally [5]. The genus Gracilaria Greville (Gracilariales, Rhodophyta) is the second-largest commercially important agarophyte with 160 taxonomically accepted species found distributed in tropical climates and temperate regions [6,7]. It is an important source of food and agar, exceeding the capacity of the genus Porphyra, Gelidium, and Pterocladia due to its tolerance to a wide range of environmental conditions [8]. Gracilaria species is a benthic flora, existing in a diverse range of forms with a majority inhabiting the intertidal and subtidal zones in depths of 0.5 m and 10 m [9]. However, many species are still poorly known and have very limited distribution globally [10].
Seaweed contains essential macro- as well as micronutrients, consisting of high-quality protein, dietary fiber, vitamins, minerals, phytochemicals, and lipid content rich in mono and polyunsaturated fatty acids (PUFAs), which offer protection against different neurodegenerative pathologies [11]. Seaweed is an important food component in traditional Japanese, Chinese, South Korean, and Filipino cuisines [12]. Brown algae is the most consumed (66.5%), followed by red algae (33%) and green algae (5%) [13]; however, global commercial production is low.
Seaweed is consumed as both raw or processed food [14]. However, in Western countries, raw consumption is recent due to it being culturally consumed for its polysaccharides (carrageenans, agars, and alginates)—as a stabilizer, additive, and gelling and thickening agent [15]. The polysaccharides in red seaweed contain high agarose content made of polymers with D-galactose and 3,6-anhydro-L-galactopyranose subunits, which are crucial for biofuel bioconversion [16]. Seaweeds occur in abundance along the Malaysian coasts. However, seaweed horticulture is exclusive to Sabah, mainly off the coast of Semporna, Kudat, Kunak, and Lahad Datu [17]. Currently, there is an emphasis on the production of red seaweed and development of new products with keen interest in the genus Glacilaria. The abundance of Gracilaria spp. in Western Peninsular Malaysia and knowledge of their biochemical variations might offer useful information that is important to sustain the seaweed industry.
The genus Gracilaria is known for its low lipid content rich in PUFAs, as well as significant levels of essential amino acids (EAAs) and non-essential amino acids (NEAAs), making them highly favorable for human health [18,19,20] and comparable to other conventional protein sources, such as meat, eggs, cereal, soybean, and milk [21]. In addition to its vast nutritional properties, the genus Gracilaria is also known for polysaccharides, commonly referred to as dietary fiber that is not degraded by enzymes in the gastrointestinal tract [22]. Dietary fiber such as agar and carrageenans offer beneficial health outcomes, such as increasing the volume of fecal bulk and regulating cholesterol serum levels [18,22,23]. These physiological effects might be attributed to the hydrocolloid properties of seaweeds [24]. Interestingly, these properties propel the use of Gracilaria in food technology to produce low-calorie food products [25] that are relevant for weight control, as well as prevention of cardiovascular and gastrointestinal diseases [26,27].
The extensive coastline and numerous islands of Malaysia provide suitable habitats for the growth of diverse seaweed flora. A total of 24 species of Gracilaria have been recorded [28,29], and G. manilaensis is one of the most prolific agarophytes. Presently, G. manilaensis is the only species cultivated at Lumut, Perak, as feed for abalone [29] with annual production of 200 metric tonnes (Department of Fisheries Malaysia, 2018). Reports on the nutritional properties of Gracilaria spp. is mostly from East Malaysia [19]. However, there is no study on the effect of seasonal variations on the chemical and nutritional properties of G. manilaensis. To the best of our knowledge, only the fatty acids profile of G. manilaensis harvested from Kuala Muda, Kedah, has been reported [30] and investigations of its biological activities have shown promising antimicrobial, antioxidant, cytotoxic, and neuritogenic properties [31,32].
The chemical composition of seaweeds varies with species, maturity stage, sampling, and ecological conditions (habitat, temperature, and season), which could either stimulate or inhibit the biosynthesis of its nutrient composition [33]. The current study sought to examine the effects of seasonal variations on the biomass composition of the red macroalgae G. manilaensis collected from Western Peninsular, Malaysia. The proximate and nutritional composition was fully expounded to also assess its potential application as a food source.

2. Results

2.1. Chemical Composition of Seaweeds

The seasonal variation in the proximate composition of G. manilaensis based on dry weight (w.w.) is summarized in Table 1. The moisture content showed no statistical significant (p > 0.05) differences between the two seasons. However, the proximate composition showed significant difference between the NEM and SWM samples. In general, carbohydrates, dietary fiber, and crude protein contents were most abundant in the NEM-G. manilaensis sample, while ash content was significantly higher in the SWM sample. No significant differences were found in crude lipid content. For gross energy, G. manilensis collected in November displayed a higher value at (2721.67 ± 10.69 cal g−1) than those harvested in August (2348.33 ± 9.87 cal g−1).

2.2. Fatty Acids Compositions

The total fatty acid profile, expressed as g fatty acids methyl esters (FAME)/100 g total fat, for NEM–G. manilaensis and SWM-G. manilaensis was (99.97 ± 0.06 g 100 g−1) and (99.99 ± 0.06 g 100 g−1), respectively (Table 2). The main SFAs of both NEM- and SWM-G. manilaensis were palmitic acid (C16:0), followed by stearic acid (C18:0), and myristic acid (C14:0). With respect to MUFAs, only oleic acid (C18:1) was detected in both samples, but was much higher (6.19 ± 0.32 g 100 g−1 DW) in SWM-G. manilaensis. As for the PUFAs, a small fraction of eicosadienoic acid (C20:2) was noticed only in NEM–G. manilaensis. Overall, SFAs made up to 97.57 g 100 g−1 DW of total fatty acids, followed by MUFAs at 1.47 g 100 g−1 DW and PUFAs at 0.97 g 100 g−1 DW of total fatty acids, for NEM-G. manilaensis. Likewise, SFAs and MUFAs were quantified as 93.8 g 100 g−1 DW and 6.23 g 100 g−1 DW of total fatty acids, respectively, in SWM-G. manilaensis.

2.3. Amino Acids Compositions

The seasonal variation in the amino acids (AAs) composition of G. manilaensis is summarized in Table 3. The total AAs content in the NEM and SWM samples were (16.36 ± 1.31 g 100 g−1 DW) and (12.24 ± 1.26 g 100 g−1 DW), respectively (p < 0.05). No significant difference was found in the non-protein nitrogenous (NPN) fraction between the NEM and SWM samples (Table 1). This showed that the NPN-fraction of G. manilaensis, comprising of nucleic acids, nitrate, nitrite, ammonium compounds, chlorophyll, and phycoerythrine, as well as free AA, was negligible [19,34]. All the nine essential amino acids (EAAs) and non-essential amino acids (NEAAs) were found in NEM–G. manilaenisis. The results differed for SWM-G. manilaensis, which presented only six EAAs and eight NEAAs. Similarly, the total EAAs for NEM samples was higher (2840.20 ± 0.31 mg 100 g−1 DW) than those (665.02 ± 0.07 mg 100 g−1 DW) obtained from the SWM samples (p < 0.05). Furthermore, total NEAAs was found to be higher for NEM-G. manilaensis (13517.96 ± 1.13 mg 100 g−1 DW) than SWM-G. manilaensis (11578.01 ± 1.33 mg 100 g−1 DW). The EAAs/total AA ratio found in the SWM and NEM samples accounted for 5.73 and 17.36 g 100 g−1 of the EAAs, respectively. Besides, a much higher concentration of the EAAs threonine (400.74 ± 0.29 mg 100 g−1 DW) > leucine (331.67 ± 0.17 mg 100 g−1 DW) > isoleucine (285.34 ± 0.12 mg 100 g−1 DW) > valine (282.21 ± 0.10 mg 100 g−1 DW) > Phenylalanine (282.07 ± 0.09 mg 100 g−1 DW) > lysine (239.69 ± 0.06 mg 100 g−1 DW) was found in NEM–G. manilaensis than in the SWM sample. In the NEAAs fraction, glutamic and aspartic acids were most abundant, accounting for (57.05–58.94 g 100 g−1) and (9.68–11.63 g 100 g−1) in the NEM and SWM samples, respectively. Further observations also indicated variation in NEAA composition, as the NEM samples contain seven AAs in the order of arginine > tyrosine > alanine > serine > glycine > cysteine > proline. In contrast, five were obtained from the SWM samples in descending order alanine > arginine > serine > glycine > tyrosine > proline.

2.4. Mineral Composition

The mineral concentration of the 16 elements (mg 100 g−1 dry wt.) analyzed in G. manilaensis is shown in Table 4. ICP-MS analysis detected significant levels of macroelements in the order of Ca (1750.97–4047.74 mg 100 g−1 DW) > K (21.05–39.21 mg 100 g−1 DW) > Na (1.33−7.02 mg 100 g−1 DW) in G. manilaensis (p < 0.05). Seaweed contains higher Na and K concentrations, but a low Na/K ratio [35]. However, the Na (1.33–7.02 mg 100−1 DW) and K (21.05–39.21 mg 100−1 DW) of G. manilaensis were significantly low in the samples analyzed. The Na+/K+ ratio of G. manilaensis (0.03 and 0.33) conforms to the WHO dietary recommendation. Moreover, the total macroelement concentration noticed in the NEM-G. manilaensis was found to be higher (4076.97 mg 100 g−1 DW) than (1793.6 mg 100−1 DW) the SWM samples. Alternatively, total microelement concentration (1672.02 mg 100−1 DW) was slightly lower in NEM-G. manilaensis when compared to 1753.17 mg 100 g−1 DW recorded for SWM-Gracilaria spp. The order of trace elements in NEM-G. manilaensis were (Fe > Mn > Zn > Cu > Cr > Co > Mo > Se). As for the SWM samples, trace elements occurred in the order of Fe > Mn > Zn > Cu > Co > Cr > Se > Mo. Fe (1512.55 mg 100 g−1 DW) and Zn (16.40 mg 100−1 DW) were found to be higher in NEM-G. manilaenisis. In contrast (401.81 mg 100 g−1 DW), Mn was found to be higher in SWM-G. manilaensis. Assessment of heavy metals shows Al, Pb, As, and Cd varied widely between seasons, and the order of concentrations was Al (137.98–188.83 mg 100−1 DW) > Pb (0.536–1.38 mg 100−1 DW) > As (0.46–0.58 mg 100−1 DW) > Cd (0.004–0.009 mg 100−1 DW) in descending order (p < 0.05). Considering FAO/WHO dietary guidelines, the concentration of Al and Pb might be toxic and therefore, to minimize exposure from dietary consumption, G. manilaensis can be subjected to depurination to eliminate any form of impurity.

2.5. Vitamin Composition (mg g−1), and Chlorophyll Content (µg g−1).

The concentration of vitamins and chlorophyll contents is shown in Table 5. In this study, vitamin B2 (riboflavin) was 0.29 ± 0.06 mg g−1 and 0.38 ± 0.06 mg g−1 for NEM- G. manilaensis and SWM-G. manilaensis, respectively (p < 0.05). The methanolic extracts for NEM-G. manilaensis presented higher chlorophyll a (9.57 ± 0.01 µg g−1) and chlorophyll b (5.54 ± 0.02, µg g−1) than SWM-G. manilaensis with chlorophyll a (7.07 ± 0.03 µg g⁻1) and chlorophyll b (4.26 ± 0.02 µg g⁻1).

2.6. Physicochemical Properties

Table 6 illustrates the swelling capacity (SWC), water-holding (WHC), and oil-holding capacity (OHC) of NEM-G. manilaensis and SWM-G. manilaensis. In this study, SWC and WHC were significantly increased (p < 0.05, one-way ANOVA, Post Hoc Test using Duncan) as temperatures increased from 25 °C to 37 °C due to increase in solubility of the fibers and protein presence in G. manilaensis. SWC for the NEM and SWM samples increased from (7.15 ± 0.57 mL g−1 vs. 7.92 ± 0.98 mL g−1 DW) at 25 °C to (9.80 ± 0.06 vs. 9.91 ± 0.05 mL g−1 DW) after incubation at 37 °C (p < 0.05). Similarly, WHC for the NEM and SWM-G. manilaensis also showed a significant increase from (9.81 ± 0.76 vs. 9.94 ± 0.67) at 25 °C to (11.89 ± 0.37 g g−1 DW vs. 11.07 ± 0.57 g g−1 DW) at 37 °C. The mean OHC for NEM-G. manilaensis (1.97 ± 0.20 g oil g−1 DW) was significantly higher than that for SWM-G. manilaensis (1.59 ± 0.21 g oil g−1 DW) (p < 0.05).

2.7. Antimicrobial Properties

The antibacterial activity of the ethyl acetate extracts of G. manilaensis was done via standard disc diffusion assay against four pathogenic Gram-negative bacteria strains, including Pseudomonas aeriginosa, Klebsiella pneumoniae, Escherichia coli, and Salmonella serovar typhi, as well as two Gram-positive bacteria, strain Staphylococcus aureus and Bacillus subtilis, as described by Baur et al. [37]. However, in this experiment, all extract dilutions and their replicates were not able to inhibit the growth of bacteria.

3. Discussion

This study shows that the proximate and nutritional composition of G. manilensis changes according to seasons [38]. Being marine in nature, the moisture content of seaweed can reach up to (70–90 g 100 g−1) fresh weight, depending largely on the phylum and species [39,40], making them highly perishable in their fresh state a few days after harvesting. The drying process plays an important role in the preservation of seaweed products and could affect their nutritional value [41,42]. It helps reduce the water activity level, which retards microbial growth, thus ensuring the conservation of desirable qualities [43]. Similarly, in industries, drying is essential because crude extracts of wet seaweed do not gel [44]. The results obtained were similar to recent data found for G. corticata (8.40 ± 0.65 g 100 g−1 DW) and G. edulis (10.40 ± 0.69 g 100 g−1 DW) [23]. Moreover, our finding is comparable to data reported by Lorenzo et al. [45], which observed the moisture content of different edible brown seaweeds species ranging from (7.95 ± 0.06 g 100 g−1 DW) in dried Bifurcaria bifurcate to (11.23 ± 0.08 g 100 g−1 DW) in dried Fucus vesiculosus. However, another study reported lower moisture content of (5.32 ± 0.10 g 100 g−1 DW) for G. changii seaweed [19].
Crude ashes are inorganic constituents found in the cell sap of seaweed. They are an essential characteristic of seaweed, contributing between (8–40 g 100 g−1 DW) of the mineral constituents required for human and animal nutrition [46]. In this study, G. manilaensis was found to have a high percent of crude ash during the SWM in August, which is consistent with previous data that linked variation in the ash content of seaweeds to changes in environmental conditions and seasons [47,48,49]. Besides, the high crude ash content shows the presence of appreciable amounts of diverse minerals found in G. manilaensis. This result is also in agreement with data reported by Etemadian et al. [50], high ash content of (33.16 ± 2.45 g 100 g−1 DW and 33.62 ± 0.61 g 100 g−1 DW) for Sirophysalis trinodis and Polycladia myrica, respectively.. Similarly, previous authors have also reported a higher ash content (between 20.4 ± 0.1 g 100 g−1 DW and 31.7 ± 0.6 g 100 g−1 DW) for green, brown and red seaweed (aquaculture species) from Europe [51]. However, G. corticata and G. edulis contained a lower ash content 8.10 ± 0.49% DW and 7.36 ± 0.39% DW, respectively [23]. Similarly, a lower ash content of 8.70% was reported for G. edulis [18]. The crude ash content found in seaweed is higher than the common edible terrestrial vegetables—(5–10 g 100 g−1 DW), i.e., potatoes (10.4), carrots (7.1 g 100 g−1 DW), tomatoes (7.1 g 100 g−1 DW), and sweet corn (2.6 g 100 g−1 DW) [52], but comparable to the green vegetable, spinach (20.4 g 100 g−1 DW) (USDA, 2001).
The majority of edible seaweeds have very low crude fat content (0.3–7 g 100 g−1 DW), revealing a low source of nutritional energy comparable with land vegetables [53]. The fat content, as observed in G. manilaensis, presented no statistical differences between the NEM and SWM season. Evidence of low-fat content (less than 3 g 100 g−1) has been reported for most Gracilaria spp. [18,19]. Marinho-Soriano et al. [54] reported a similar pattern wherein the lipids content of G. cervicornis did not vary significantly throughout the year of harvest. Alternatively, Benjama et al. [55] reported that the lipid content of G. tenuistipitata spikes during the rainy season with a value of (3.6 g 100 g−1 DW) in December in contrast to G. fisheri, which had lower lipids content during the rainy season with a value of 1.7% in April. Those fluctuations are due to variations in environmental conditions such as temperature, salinity, and nutrients [56,57]. The crude lipids content presented for G. manilaensis was lower when compared to (7.07 ± 0.33 g 100 g−1 DW) and (4.76 ± 0.73 g 100 g−1 DW) reported for G. corticata and G. edulis, respectively [23]. Similarly, a lower range of crude lipid content (1.7 g 100 g−1 DW) and (3.6 100 g−1 DW) was found for G. fisheri and G. tenuistipitata, respectively [55]. Interestingly, crude lipid of NEM and SWM-G. manilaensis from Johor was higher compared to (0.175 g 100 g−1 DW) observed in G. manilaensis collected in Kedah [30]. Thus, fat content in Gracilaria can widely vary, depending on the source and species [23].
The phylum Rhodophyta contains high protein content (10–30 g 100 g−1 DW) [58] comparable to high-protein plant foods such as soybean and wheat [33]. In the present study, protein content showed highly significant differences (p < 0.05) for both samples. This result agreed with previous studies by Marinho et al. [54] and Benjama and Masniyom [59] on Graclaria spp., which describes that protein content varies depending on season and environment. A comparable trend demonstrating fluctuations in algal protein content was recorded for red seaweed Palmaria palmata [58], which showed a higher protein content of (21.9 ± 3.5 g 100 g−1 DW) in the winter-spring season than (11.9 ± 2.0 g 100 g−1 DW) found in summer-early autumn. In this study, protein content for the NEM and SWM samples were higher than G. corticata and G. edulis, which was (22.84 ± 0.87 g 100 g−1 DW) and (25.29 ± 0.67 mL g−1 DW), respectively [23], despite reports of a lower crude protein content of (6.68 ± 0.94 g 100 g−1 DW) and (12.57 ± 1.31 g 100 g−1 DW) in G. edulis and G. changii, respectively [18,19]. Regardless, the high protein content recorded in G. manileansis suggests that it might be considered a potential marine plant source of protein [54,55].
Plant carbohydrate content is often influenced by biomass, which suggests that macroalgal carbohydrate synthesis is related to periods of maximum growth, and increased in photosynthesis activity [9,54]. The total carbohydrate content of both the NEM and SWM samples was markedly higher than those reported for G. edulis (10.2 g 100 g−1 DW) and G. changii 29.44 g 100 g−1 DW [18,19]. Other authors also found much lower carbohydrate content 8.30 ± 1.89 and 4.71 ± 0.60 in G. corticata and G. edulis, respectively. The fluctuations in the carbohydrate content of G. manilaensis might be due to the influence of factors such as temperature, salinity, and nutrient concentration [9,60]. Besides being an energy source, carbohydrate content is an important nutritive component of metabolic processes in seaweed [61].
Seaweeds contain a substantial quantity of polysaccharides, which comprise of soluble and insoluble dietary fibers [62]. In this study, G. manilaensis presented very high dietary fiber in both seasons. On the other hand, a lower dietary fiber content was found for G. edulis and G. acerosa, which had (8.9 ± 0.62 g 100 g−1 DW) and (13.45 ± 1.076 g 100 g−1 DW), respectively. Meanwhile, markedly higher dietary fiber, 64.74 ± 0.82 g 100 g−1 DW and 56.54 ± 7.42 g 100 g−1 DW, was found in G. changii and G. cervicornis [19,54]. Dietary fiber plays a crucial role in the growth and protection of beneficial intestinal flora, which helps prevent the risks of colon cancer [34]. Overall, seaweeds contain relatively low energy density due to low crude lipid content, high protein content, as well as non-digestible polysaccharides [63]. Similarly, the gross caloric content of G. manilaensis was found to be low in both NEM and SWM samples.
Red seaweeds are predominantly rich in SFAs and PUFAs, which offer extensive nutritional applications in the food and feed, biotechnological, cosmetic, and pharmaceutical industries [26,64]. In this study, total fatty acids content was significantly higher than those obtained by previous authors, who found (97.03 g 100 g−1 DW) in G. changii and (11.41 g 100 g−1 DW) in G. edulis [18,19]. However, a higher proportion was reported by Neto et al. [51], who found 117.15% in Gracialaria spp. A fatty acid profile revealed that the most abundant fatty acids in seaweeds are palmitic, followed by stearic acid, and myristic acid. A similar finding was reported for G. changii as the percentage of palmitic acid and stearic acid accounted for (81 g 100 g−1 DW) of the total SFAs [19].
Other authors, including Khotimchenko et al. [65] and Bhaskar, Narayan et al. [64], also reported the total percentage of palmitic acid and stearic acid at (85–94 g 100 g−1 DW) of the total SFAs in the genus Gracilaria spp. In contrast, pentadecanoic acid 5.12% and palmitic acid (4.45 g 100 g−1 DW) was recorded as the dominant SFAs found in G. manilaensis [30]. In general, the presence of high palmitic acid (C16:0) composition is due to the distinct character traits of individual genera [66]. Overall, the G. manilaensis analyzed possesses a substantial quantity of SFAs and variation in content might be attributed to the influence of abiotic factors such as light, salinity, and nutrients; as well as seasonality [57,66,67].
In the EAAs fraction, the high level found in NEM-G. manilaensis might be associated with the high nutrient concentration present in water bodies during the rainy season [54,55,56,59]. A similar trend was reported for Palmaria palmata containing substantial levels of glutamic acid, serine, and alanine during winter and early spring, but absent in summer [58]. Specimens of G. fisheri and G. tenuistipitata collected in the rainy season had significantly higher levels of EAAs in contrast to a summer harvest [55]. Amongst the EAAs, histidine was quantified as the most limiting in NEM samples at 620.98 ± 22.99 mg 100 g−1 followed by threonine 400.74 ± 29.12 mg 100 g−1. An equally similar pattern was noticed by Sakthivel et al. [18] and Syad et al. [68], as obtained in G. edulis and Sargassum wightii with histidine levels at 3.3 ± 0.16 mg g−1 and 7.44 ± 0.44 mg g−1, respectively. Our data identified threonine and lysine as the highest EAAs in the SWM species with 231.73 ± 8.66 mg 100 g−1 and 129.62 ± 6.45 mg 100 g−1, respectively. These findings differ from other studies, which reported arginine and leucine as the most limiting AAs in G. changii and Bifurcaria bifurcata at 18.69% and 7.42%, respectively [19,45].
The EAAs/total amino acid ratio (0.05–0.17) was lower than those previously reported for Gracilaria spp. [23,68]. As for NEAAs, glutamic and aspartic acids were the most abundant, accounting between (57.05–58.94 g 100 g−1 DW) and (9.68–11.63 g 100 g−1 DW) in the NEM and SWM samples, respectively. The high proportion of acidic AA (aspartic and glutamic acids) compared to basic AA is a characteristic of red seaweed [21,69]. Total acidic AA in the present study was higher than the data found in G. salicornia and G. changii [19,56]. The distinctive flavor and characteristic ‘umami’ taste of seaweeds are linked to aspartic and glutamic acids [70]. In terms of protein quality, NEM- G. manilaensis is greater due to the presence of histidine, tryptophan, and AAs bearing sulfur quantified at (2.4 g 100 g−1) (sum of Met and Cys) found lacking in the SWM samples. Histidine is known to contribute to antioxidant and anti-inflammatory properties [71]. The concentration of lysine, methionine, cysteine, tryptophan, and threonine is low in plants. In seaweed, cysteine is often reported to be deficient, but, when present, they are found in low concentrations [18,72]. Estimating their chemical score is essential in other to determine protein quality [73].
The protein quality and order of the restrictive AAs of G. manilaensis was measured by the chemical score for each EAAs using reference protein as proposed by Food and Agriculture Organization of the United Nations (FAO)/World Health Organization (WHO)/United Nations (UNU) for humans (children from 1-3-year-old, and adults) [74]. The AAs chemical score found in G. manilaensis during NEM and SWM were in the range of (3.22–200.16 g 100 g−1) to (5.98–90.35 g 100 g−1), respectively (Table 3). In the NEM samples, tryptophan and lysine were the limiting AAs, whereas leucine and phenylalanine contributed to the lowest AAs score in SWM-G. manilaensis. A similar data was reported in edible red seaweeds G. changii and Porphyra spp. [21,75]. Methionine was the most limiting AAs (64.44 g 100 g−1 DW) found in G. changii [19]. As for the total EAAs requirement, G. manilaensis recorded a protein value of 41.49 mg g−1 and 146.59 mg g−1 during SWM and NEM monsoon, respectively. Therefore, consumption of G. manilaensis will offer a measurable quantity of the required essential amino acids.
The cell wall polysaccharides of macroalgae contain multiple functional groups, i.e., anionic carboxyl, amino, sulfhydryl, sulfate, and phosphate responsible for the high complexation of metallic cation from its surroundings [76]. They accumulate most of these metals without suffering any cell damage [77]. The macro, trace, and toxic elements differ widely in seaweed [78]. In this study, Ca content is higher than the level reported by Neto et al. [51] for different seaweeds: Ulva rigida 414.3 ± 33.8 g 100−1 g, Gracilaria spp. 200.4 ± 24.3g 100−1 g, Fucus vesiculosus 1382.0 ± 5.1 g 100−1 g, and Saccharina latissimi 919.4 ± 32.5 g 100−1 g. However, lower Ca contents were reported for G. edulis 89.38 ± 17.87 mg 100−1 g and G. changii 625.92 ± 17.87 mg 100−1 g [18,19]. Seaweed is an important source of calcium, containing up to (7 g 100 g−1 DW) [79] and could provide an alternative source of calcium for young, pre-, post-menopausal women and expectant mothers prone to calcium deficiency disorders such as osteoporosis and preeclampsia [80].
Seaweeds are known to be rich sources of Na and K, however, with a low Na/K ratio [35]. These elements—Na (1.33–7.02 mg 100−1 DW) and K (21.05–39.21 mg 100−1 DW)—were significantly lower in both samples in comparison to the higher values found in Gracilaria spp [18,51]. The Na+/K+ ratio of G. manilaensis (0.03 and 0.33) conforms with WHO dietary recommendations. Some studies have also reported low Na/K ratios in Gracilaria spp [18,68] suggesting that they can help neutralize modern dietary habits that are characterized by a high intake of Na/K ratio diets [19,67]. The consumption of a high Na/K ratio diet is linked to cardiovascular diseases and early death [78].
A significant amount of trace metal was recorded in G. manilaensis regardless of seasonal variation, and these might be attributed to the influence of growth dynamics [81]. Studies have shown that seaweed with low biomass corresponds to a high concentration of mineral elements and vice verse [82]. The Fe (1346.05 vs. 1512.55 mg 100−1 g) and Mn (142.34 vs. 401.81 mg 100−1 g) concentration was high between the two harvest seasons. Similarly, Fe content, 1072.48 ± 20.97 mg 100−1 g and 557.36 ± 0.57 mg 100−1 g, was found to be higher in G. corticata and G. edulis, respectively [23]. Some authors reported a much lower Fe content of 436.13 mg 100−1g DW and 0.46 mg−1g DW in G. changii and G. edulis, respectively [18,19]. In general, the iron content in G. manilaensis is higher than most terrestrial crops (2–4 mg 100−1 g), such as legumes, cereal grains, nuts, and green leafy vegetables [83].
The estimated daily intakes (EDIs) of each trace metal was calculated assuming daily consumption of 8 g of dried seaweed based on a daily intake for an average adult (70 kg) in Asian cuisines [36]. In this regard, consumption of 8 g portion of G. manilaensis provides between (598 g 100 g−1 and 672 g 100 g−1) of the recommended daily amount (RDA) of Fe in women 19–50 years, 18 mg/day FNB / IOM (2001). Seaweed is also used as a dietary source of iron to prevent anemia caused by iron deficiency [84]. Manganese is beneficial for its metalloenzymes activities [72], and 8 g of G. manilaensis exceeded 100% of RDA required for adult male and female.
Studies have shown that red seaweed can accumulate heavy metals [81,85]. Based on PTWI health risk standards, daily consumption of SWM and NEM G. manilaensis samples (12.5 g/adult/day) contributed to (172.48 g 100 g−1) and (236.04 g 100 g−1) of Al intake, respectively. It is noteworthy that the Al concentration found in Gracilaria spp. during the two harvest seasons is well above the specified provisional tolerable weekly intake (PTWI) of 1 ppm of body weight (BW) [86,87]. These values were higher than those recorded by Larrea-Marín et al. [88] for Porphyra spp. (15.0 ± 2.55–220.8 ± 7.95 µg g−1 DW) and Laminaria spp. (32.3 ± 0.91–580.0 ± 22.10 µg g−1 DW) from Europe and Asia. The high Al content in G. manilaensis may be due to acidification of the surrounding soils in the area of harvest [89,90].
The growing number of industries in Shoal, Johor, might be responsible for these elements entering the surrounding aquatic bodies [91,92,93]. Al toxicity may lead to pathophysiology of several neurodegenerative syndromes, i.e., Alzheimer, Parkinsonism, and dementia [94]. The level of Cd in NEM and SWM samples contributed less than 2% of PTWI, suggesting no health risk to potential consumers. The concentration of Pb and total As in both samples contributed between (25–70 g 100 g−1) of PTWI. In particular, large dietary consumption of Pb content might lead to health complications in the nervous system and other vital organs, such as kidney cancer and blood disorders [95]. The assessment of As toxicity depends on its chemical form; they exist in different forms, such as arsenic (III), arsenic (V) or other derivatives; arsenocholine, arsenobetaine, and arsenosugars [96]. Interestingly, about (60 g 100 g−1) of the total As concentration is lost during processing activities [97].
Vitamin analysis revealed vitamin B in a measurable concentration, while the other vitamin components were below the detection level. In contrast, other authors reported measurable quantities of different vitamins component in genus Gracilaria spp. [18,68]. The chlorophyll contents detected in G. manilaensis is low and in agreement with studies conducted by other authors [18,68], who found that chlorophyll a and b of Gracilaria spp. range from (3.06 ± 0.28 µg g−1 vs. 1.583 ± 0.049 µg g−1 DW) and (2.8 ± 0.08 µg g−1 vs. 1.896 ± 0.10 µg g−1 DW), respectively. Similarly, G. edulis and G. corticata also presented chlorophyll a and b in the range of (17.14 µg/g vs. 8.96 µg/g) and (8.44 µg/g vs. 7.74 µg/g), respectively [23].
Numerous studies have demonstrated the effect of temperature variations on the physicochemical properties of edible seaweed [19,23,50,55]. The SWC of G. manilaensis was in the range of some edible seaweeds, i.e., Sargassum wightii (10 ± 0 mL g−1 DW), G. changii (9.01 ± 0.06–10.91 ± 0.06 mL g−1 DW) and G. edulis (20.0 mL/g DW) [18]. Likewise, WHC indicates a significant interaction between seaweed samples and temperature. These properties could be related to the hydrophilic nature of the charged polysaccharides (agar and carrageenan) and higher neutral sugar content found in the soluble dietary fibers of red seaweed [25]. A positive correlation between water retention has previously been observed in edible seaweed [23,98]. Similarly, our results were comparable to (9.81 ± 0.55 g g−1–9.97 ± 0.12 g g−1 DW) found for G. edulis and (9.93 ± 0.08 g g−1 DW–11.59 ± 0.04 g g−1 DW) reported for G. changii [18,19]. However, values of WHC are difficult to compare, because they depend on experimental conditions (temperature, time, and centrifugation) and sample preparation [99,100]. The higher values of WHC in G. manilaensis indicate they might be used as a functional ingredient for producing low-calorie food such as snacks, corn flakes, crackers, and cookies [100]. Oil holding capacity (OHC) is also a functional property, and food ingredients with high OHC values allow for the stabilization of food emulsions and high-fat food products. In this study, there were variations in OHC between the seaweed samples, which might be due to the physical entrapment of oil by capillary attraction [101]. The OHC in G. manilaensis was comparable to other Gracilaria spp. [18,19,55]. The hydrophobicity of proteins also plays a significant role in fat absorption [55,98]. Overall, the results of physicochemical properties confirmed that G. manilaensis could be consumed as a source of food ingredients, dietary fibers, and proteins.
Studies have reported the antibacterial properties of seaweed extracts [102,103,104]. In this study, extracts dilutions from G. manilaensis did not inhibit the growth of the bacteria screened. Arulkumar, et al. [105] related antimicrobial activity from G. corticata and G. edulis to the presence of unsaturated fatty acids, organic acids, and phenol compounds. However, the fatty acid profile of G. manilaensis lacked PUFAs and did not show a zone of inhibition against the tested pathogenic organism. These results are not in conformity with Deepak et al. [106] and Narasimhan et al. [107], who reported seasonal variation in the antibacterial activities of Gracilaria against different Gram-positive and Gram-negative bacteria. Variability in the production of metabolites in seaweed, which is linked to seasonal variation, could have affected the antibacterial properties of the studied seaweed [108]. Seaweed collected in the summer has been reported to exhibit higher physiological activities due to active metabolites, including fatty acids, phlorotannins, pigments, lectins, alkaloids, terpenoids, and halogenated compounds found in them as a form of adaptation [109]. In this experiment, the samples were collected in August and November, where water temperature was colder at 28 °C, which might attribute to the absence of activity. However, there is no data on seasonal variation of seaweed bioactivity in Malaysia for comparison. As such, further study is required to confirm these findings.

4. Materials and Methods

4.1. Biomass sampling and Preparation

The Malaysian climate is modulated primarily by the Southeast Asian monsoon with a cycle of two opposite regimes, i.e., winter monsoon [locally known as the northeast monsoon (NEM)] and the summer monsoon [locally known as the southwest monsoon (SWM)]. The SWM begins in late May and ends in late September, while the NEM commences around November and retreats in March of the subsequent year [29]. The country receives substantial rainfall all year-round, but the amount peaks during the NEM period [110]. The SWM season between brings less rainfall, with a recorded total monthly rainfall as low as 4.8 mm. According to available reports, the average annual total rainfall and evaporation were 1862 mm and 1098 mm, respectively [111]. However, the rate of evaporation is affected by temperature and cloudiness, and when it is cloudy, there is less sunshine, resulting in less solar radiation and lower temperature. The drier months have higher evaporation, while the rainy months have lower, influencing water body salinity [112,113,114]. The salinity of Malaysian waters ranges between 28 and 34 [115,116], while surface water temperature also fluctuates between 25.0 °C and 30.5 °C [117].
Specimens of G. manilaensis (Rhodophyta, Rhodophyceae) were collected twice by hand in August 2018 and November 2018 during the SWM and NEM, respectively, from Merambong shoal (1°20′14.53′′ N, 103°36′08.70′′ E) in the southern tip of Peninsular Malaysia in the Straits of Johor. These are periods of optimal harvesting, as they signal the end of the growth season of some seaweeds in Malaysia [118,119]. Besides, the growth of seaweeds reacts to a broad variety of ever-changing biotic and physical abiotic factors [120]. Approximately 3 to 5 kg of tissue was collected in each harvest. To prevent physiological injury during harvesting, the algae stem was not separated. Within 24 h of collection, they were transported to the laboratory in an ice-cold box containing seawater to prevent evaporation, thoroughly washed and cleaned with distilled water to remove contaminants (epiphytes, sand, and debris), and dried at room temperature [104]. Voucher specimens were identified by Prof Siew-Moi Phang and deposited at the Institutes of Earth and Ocean Sciences, University of Malaya. The dried sample was milled to powder using a Waring blender and stored airtight under −20 °C for further analysis.

4.2. Estimation of Moisture and Ash

Moisture content was determined gravimetrically by measuring sample (3 g) weight loss by drying in a hot air oven (Memmert UFP 600, Schwabach, Germany) at 105 °C until a constant weight was obtained (AOAC 934.01) [121]. Moisture content is expressed either as a percent of the oven-dry mass or of the as-received mass (A5TM D 2974-87). Ash content was quantified gravimetrically after incineration of dried algal material at 550 °C for 18 h using an electric muffle furnace (Barnstead Thermolyne) (AOAC 930.05) [122]. The leftover residue after incineration is ash. The ash content is expressed as a percentage of the mass of the oven-dried sample.

4.3. Estimation of Total Crude Protein

Crude protein percentage was quantified according to the classical micro-Kjeldahl method (N × 6.25) [121] using a Foss Kjeltec system as described by Zhou et al. [123]. Five-hundred mg of freeze-dried algae samples wrapped in nitrogen-free paper were oxidized in a long neck 250-mL digestion flask containing concentrated sulphuric acid (15 mL), and a mixture of potassium sulfate (7 g) and cupric sulfate (0.5 g). They were digested using a Gerhardt Kjeldatherm digester at 420 °C until a clear and colorless liquid was obtained, which indicates the complete breakdown of all organic matter. Neutralization, distillation, and titration were done simultaneously in a Foss Kjeltec 8400 Analyser unit, as the results were obtained in percent of dry weight. The content of non-protein nitrogen (NPN) fraction in G. manilaensis was obtained after precipitation of the proteins with trichloracetic acid (10%) [34]. Pure protein content resulted from the difference between crude protein and NPN contents.

4.4. Amino Acid Profile

The amino acid (AA) content of G. manilaensis was determined based on AOAC 999.13 with automatic online OPA/FMOC derivatization by RP-HPLC using a Shimadzu LC system (Shimadzu Corporation, Kyoto, Japan) equipped with an LC-20AD pump, DGU-20AS degasser and photodiode array SPD-M20A (PAD), and fluorescence RF-10AXL (FLD) detectors on line [20]. About 2 g of powdered G. manilaensis samples (total and free amino acid extracts) were derivatized with o-phthalaldehyde (OPA) and 9-fluorenylmethyl chloroformate (FMOC) (Sigma-Aldrich (Steinheim, Germany), agreeing to a protocol by Heems et al. [124]. The derivatized amino acid solutions were filtered through a 0.22μm microfiltration membrane, and the filtrates (20.0 μL) were injected onto the RP-HPLC system equipped with an HPLC column (Zorbax Eclipse XDB-C18 (4.6 × 250 mm) conditioned at 27 ± 0.1 °C. The OPA-3-MPA derivatives were detected by a programmable fluorimeter with excitation (λex) and emission (λem) wavelengths set at 338 and 262 nm, respectively, while the FMOC derivatives were identified at λex 260nm and λem 315 nm; wavelength change occurred at 18.5 min. The mobile phase used was a combination of 10 mM disodium hydrogen phosphate buffer: 10mM disodium tetraborate and 5 mM sodium azide adjusted to pH 8.2 eluent (A), and a mixture of acetonitrile, methanol, and water with a ratio of 45:45:10 (v/v/v) as eluent B, at a flow rate of 1.0 mL min−1. The amino acid standards mix (AAS18, Sigma Aldrich, MO, USA) was dissolved in 0.1 M hydrochloric acid and diluted appropriately to obtain a working solution with norvalin (Merck, MO, USA) used as the internal standard.

Chemical Score

The amino acid (AA) contents was then compared with the FAO reference pattern as described by FAO [74]. The AA score of essential amino acids (EAAs) was calculated using the following equation:
AA score (%) = (mg EAA in 1 g of test protein)/(mg EAA in 1 g of reference protein) × 100

4.5. Estimation of Crude Lipids

The total weight of the lipid extract was determined using the modified Folch Extraction method, as described by Gosch et al. [125]. Two-hundred milligram of the freeze-dried algae sample, weighed into a Teflon capped glass vial, was homogenized in 5 mL chloroform: methanol (2:1, v/v) mixture at 60 °C for 1 h. The mixture was filtered using a vacuum pump, while an additional 4 mL of the chloroform-methanol mixture was used to rinse both the filter paper and the vacuum flask to recover all lipids. The filtered crude extract was washed with 1.8 mL of 0.9% NaCl into a pre-weighed vial and centrifuged to enable phase separation with lower organic phase (chloroform); it contained the lipids collected and evaporated to dryness using a Speed Vac Concentrator. The total lipid content was determined gravimetrically.

Fatty Acid Composition

The fatty acid (FA) composition of G. manilaensis was quantified using Gas Chromatography (Hydrogen Flame Ionization Detector) GC FID, according to standard method AOAC 996.06, as described by Petrović et al. [126]. Inputs for the instrument were temperature injector—225 °C; carrier gas—helium; flow rate—0.75mL/min using a capillary column (Rt-2560, 100 m, 0.25 mm ID, 0.2 um df). Aliquots of the extracted lipids samples were saponified and methylated to fatty acid methyl esters (FAME Mix C4-C24 (18919 Supelco) using Boron trifluoride (BF3) in 0.5N methanolic solution against C11.0 triglycerides internal standard (Tokyo, Japan).

4.6. Estimation of Total Carbohydrate

Total carbohydrate content (%) was estimated by weight difference (100 − [moisture + ash + crude protein + crude lipid]) [127].

4.7. Estimation of Gross Calorific Value

The gross calorific value was estimated using the Isoperibol oxygen bomb calorimeter (IKA Calorimeter System C 2000 basic) standardized with benzoic acids. Two-hundred mg of dried algae samples were made into pellets, combusted in oxygen at 200 bar (2900 PSI) and a core temperature of up to 1000 °C (1800 °F). The total calories were calculated on an ash-free basis [128,129].

4.8. Estimation of Total Dietary Fiber

The total dietary fiber content in seaweeds was determined according to the (AOAC, 1995) enzymatic-gravimetric method AOAC 985.29 [99].

4.9. Estimation of Chlorophyll A and B

Spectrophotometric determination of Chlorophyll (A and B) was estimated according to a method by Rosemary et al. [23] with slight modification. One gram of freeze-dried seaweed was dissolved and homogenized in 96% methanol (Glas-col High-speed homogenizer) at 1000 rpm for one minute. The seaweed extract was centrifuged at 1000 rpm for 1 min. The filtered supernatant was centrifuged (Eppendorf Centrifuge 5810R) at 2500 rpm for 10 min and the absorbance measured at a range of 400–700 nm on a Shimadzu UV-Vis 1800 spectrophotometer. Chlorophyll A and B content was expressed as (µg/g of dry weight), calculated according to the following equations:
Chlorophyll A = 15.65 (A666) − 7.340 (A653)
Chlorophyll B = 27.05 (A653) − 11.21 (A666)

4.10. Estimation of Vitamin Content

Vitamin content of G. manilaensis was evaluated using HPLC (LC, Agilent, USA) method BS EN 14130:2003 and nutrition labelling analysis 1993 No. 992.06 with slight modification [130], based on the following conditions: column (Zorbax Eclipse -C18 (4.6 × 250 mm) and injection volume 20 µL. Mobile phase methanol: water (95:5) and 0.05 M ammonium acetate for Vit B1 and B2 set at UV 270 nm—1.0mL/min. Hexane and Isopropanol: 100 + 0.25 mL for Vit A and E set at UV 336 nm (flow rate 0.5 mL/min for B1 and B2) and UV 264 nm for D (flow rate 1.0 mL/min). For Vitamin C, the method used was BS EN 14130:2003 Mobile Phase 0.85% Orthophosphoric Acid with UV detector 265 nm and flow rate 0.7 mL/min. Standards include Retinyl acetate and Retinyl Palmitate (7.5 µg/mL), α-tocopherol (2 mg/mL), and (Vitamin A, E, C, D at 1 mg/mL).

4.11. Mineral and Heavy Metal Analysis

The mineral and heavy metal content was quantified using ICP-MS (Agilent 7700) with slight modification. About 0.5 g freeze-dried Gracilaria spp. was subjected to wet hydrolysis using a high-pressure polytetrafluoroethylene (PTFE) vessel containing 6 mL of 65% HNO3 and 2 mL of 35% H2O2, and digested in an Anton Paar microwave. After digestion, the samples were filtered and diluted with Milli-Q water to a final volume of 50 mL and analyzed in an Agilent 7700 series ICP-MS for multi-mineral elements, as adopted by NMKL (Nordic Committee on Food Analysis) method 22, as well as a CEN (European Normalization Organization) method EN 15763:2009.23. The total concentrations of freeze-dried seaweed minerals were then quantified from the calibration curves of their respective standard elements [131].

4.12. Physicochemical Properties of Seaweeds

Swelling capacity (SWC) and water holding capacity (WHC) were determined as per the method described by Sakthivel and Devi [18], while oil holding capacity (OHC) was measured according to Yaich et al. [98].

4.12.1. Swelling Capacity (SWC)

SWC was measured by the bed volume technique, as per Sakthivel and Devi [18]. About 200 mg of Gracilaria spp. was dissolved in 20 mL of distilled water; the mixture was stirred vigorously and conditioned separately at two different temperatures—25 °C and 37 °C—separately to measure its effect on SWC. The swelling volume was measured and expressed as ml of swollen sample per g of sample dry weight (DW):
SWC = Initial volume of water (mL) − volume of water after incubation (mL)

4.12.2. Water Holding Capacity (WHC)

Water absorption of Gracilaria spp. was measured by the centrifugation method, according to Sakthivel and Devi [18]. About 200 mg of seaweed sample was dissolved in 20 mL of distilled water and kept in an incubator shaker at RPM 250 (IKA KS 4000I) for 24 h before it was conditioned separately at two different temperatures—25 °C and 37 °C. The supernatant was discarded after centrifugation for 25 min at 3000 g and the moisture content estimated by dehydration in an oven at 160 °C for two h. WHC is expressed as the grams of water held by 1 g of dry weight of the sample.
WHC = Wet weight of the sample (g) – Dry weight of the sample (g)

4.12.3. Oil Holding Capacity (OHC)

The oil holding capacity of Gracilaria spp. was measured according to a method described by Yaich et al. [98]. About 0.5 g of seaweed sample was dissolved in 6.0 mL of corn oil in a centrifugation tube. The tubes were agitated for 30 min in an incubator shaker (RPM 250) (IKA KS 4000I) at 25 °C and 37 °C. Then the oil supernatant was measured at 2500 g for 30 min (Eppendorf Centrifuge 5810R) at room temperature. The OHC of seaweed was measured as the number of grams of oil held by 1 g of dry weight of the sample:
OHC = Initial volume of oil (g) − Volume of oil after incubation (g)

4.12.4. Antimicrobial Properties

About 1350–1500 g of freshly harvested red seaweed G. manilaensis was soaked separately in 7500 mL of methanol (100%) at a ratio of 1:5 (powder/solvent) for seven days. The mixture was agitated multiple times during the soaking period to ensure maximum homogeneity and extraction of macroalgae constituents. The mixtures were first filtered by cheese cloth and then by Whatman No. 1 filter paper. The filtrate was then concentrated under reduced pressure by using a rotary evaporator at 40 °C to complete dryness, yielding 12–15 g (0.8–1.0%) of crude methanolic extract [132]. The crude methanolic extract was subjected to partitioning in a separating funnel with a mixture of two solvents—water and ethyl acetate (EtOAc)—at a ratio of 3:1, and then concentrated in vacuo to produce both water and EtOAc concentrate. The G. manilaensis from NEM produced 1.97 g, a higher yield than G. manilaensis obtained from SWM (1.02 g).
The solid crude extracts (31.5–500 µg), obtained from the lyophilised G. manilaensis were dissolved and diluted with EtOAc solvent. Sterilised 6-mm filter paper discs loaded with 20 µL of the seaweed extract were transferred to sterile petri dishes. The discs were allowed to remain at room temperature until complete diluent evaporation and kept under refrigeration until use. The antibacterial activity was evaluated by standard disc diffusion assay against four pathogenic Gram-negative bacterial strains—Pseudomonas aeruginosa, Klebsiella pneumoniae, Escherichia coli, and Salmonella serovar typhi—as well as two Gram-positive bacterial strains—Staphylococcus aureus and Bacillus subtilis—on Mueller Hilton agar (Difco, US), as described by Bauer et al. [37]. Pure bacterial strains were obtained from the Department of Microbiology, School of Health Sciences, Universiti Sains Malaysia, and were subsequently grown at 37 °C and maintained on nutrient agar (Merck, Germany). Bacterial isolates were grown overnight in Mueller Hilton broth (Merck, Germany) at 30 °C. Before inoculation, bacterial cell density was adjusted to turbidity equalling the standard McFarland 0.5 at 600 nm. Discs loaded with extracts were placed onto the Mueller Hilton agar (MHA) containing 100 µL standardized bacterial suspension and incubated at 30 °C for 24 h under aerobic conditions. Prior to incubation, all Petri dishes were placed in the refrigerator for 40 min to retard microbial growth. Imipenem was used as a positive control, and analytical EtOAc was used as negative control. The inhibition zone was expressed as the diameter of the inhibition zone around the discs in mm after overnight incubation. Tests were performed in duplicate.

4.13. Statistical Analysis

All of the analyses were performed in triplicates (n ≥ 3) and the results are presented as means ± S.D. except Dietary Fiber (n ≥ 2). Paired sample t-test was used to compare composition values and significant difference between the mean values of NEM and SWM specimen harvested in the two seasons. One-way analysis of variance (ANOVA) and Duncan’s test was used to compare the effects of temperature on the physicochemical properties. All determinations were performed using SPSS 24.0 (Statistical Package for the Social Sciences, SPSS Inc., Chicago, IL, USA). A significant positive variation was defined at the significance level of p < 0.05.

5. Conclusions

This study discovered pronounced seasonal variation in the biochemical composition of G. manilaensis for future exploitation as sustainable sources of food ingredients. Currently, there is no published data on harvest time and its relation to the biochemical and nutritional composition of the edible G. manilaensis species in Malaysia. Regarding the biochemical composition of G. manilaensis, NEM samples presented the maximum values for almost all the components investigated when compared to the SWM samples, with a significant difference. The EAAs and NEAAs were significantly higher in NEM samples, as well as proximate and gross energy value. However, high ash content was observed in the SWM, which was also reflected in the total mineral content. The lipids components showed no statistically significant difference; however, the SWM samples contained higher amounts of monounsaturated oleic acid. With respect to physicochemical properties, both samples from NWM and SWM could be considered as sources of food ingredients, including proteins, and dietary and soluble fiber. In view of these results, this study suggests that NWM and SWM samples contains important nutritive components that may significantly contribute to both human and animal nutritional requirements. Furthermore, they could serve as potential sources of mineral supplements, although the presence of high levels of aluminum and lead, which is perhaps attributed largely to the presence of human activities in coastal areas, may discourage its utilization as food and feed purposes. However, the beneficial or detrimental health effects of specific nutrients available in food depend on their absorption in the gut (which is also a function of the body’s processing conditions) and interaction with other components.

Author Contributions

Conceptualization, S.A.R. and K.P.; methodology, A.Q.A.; software, S.A.R.; validation, F.G., K.P.; formal analysis, A.Q.A.; investigation, A.Q.A.; resources, S.A.R.; data curation, A.Q.A.; writing—original draft preparation, A.Q.A.; writing—review and editing, S.A.R. and K.P.; supervision, S.A.R.; project administration, M.R.-I.; funding acquisition, M.R.-I. and S.A.R.

Funding

This research is funding by RP018A-16SUS University Malaya Research Grant (UMRG), Institution Centre of Excellence (HiCOE) Phase II Fund, Ministry of Higher Education (IOES-2014D) and the Universiti Sains Malaysia, School of Health Sciences Research Incentive Grant.

Acknowledgments

The authors thanks Affendi Yang Amri, Jillian Ooi, Kelab Alami Mukim Tg Kupang and Serina Rahman for help with the collection of samples off the Merambong Shoales Johore Straits, Western Peninsular Malaysia.

Conflicts of Interest

The authors declare that there are no conflict of interest.

References

  1. Fan, S.; Brzeska, J. Sustainable food security and nutrition: Demystifying conventional beliefs. Glob. Food Secur. 2016, 11, 11–16. [Google Scholar] [CrossRef]
  2. FAO, U. How to feed the world in 2050. In Proceedings of the Rome High-Level Expert Forum, Rome, Italy, November 2017. [Google Scholar]
  3. Godfray, H.C.J.; Beddington, J.R.; Crute, I.R.; Haddad, L.; Lawrence, D.; Muir, J.F.; Pretty, J.; Robinson, S.; Thomas, S.M.; Toulmin, C. Food Security: The Challenge of Feeding 9 Billion People. Science 2010, 327, 812–818. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  4. Wan, A.H.L.; Davies, S.J.; Soler-Vila, A.; Fitzgerald, R.; Johnson, M.P. Macroalgae as a sustainable aquafeed ingredient. Rev. Aquac. 2019, 11, 458–492. [Google Scholar] [CrossRef]
  5. Kadam, S.U.; Tiwari, B.K.; O’Donnell, C.P. Application of Novel Extraction Technologies for Bioactives from Marine Algae. J. Agric. Food Chem. 2013, 61, 4667–4675. [Google Scholar] [CrossRef] [PubMed]
  6. Barros, F.C.; da Silva, D.C.; Sombra, V.G.; Maciel, J.S.; Feitosa, J.P.; Freitas, A.L.; de Paula, R.C. Structural characterization of polysaccharide obtained from red seaweed Gracilaria caudata (J Agardh). Carbohydr. Polym. 2013, 92, 598–603. [Google Scholar] [CrossRef] [PubMed]
  7. Guiry, M. AlgaeBase. World-wide electronic publication. Available online: http://www.algaebase.org (accessed on 09 March 2019).
  8. McHugh, D.J. Worldwide distribution of commercial resources of seaweeds including Gelidium. In International Workshop on Gelidium; Springer: Dordrecht, the Netherlands, 1991; Volume 21, pp. 19–29. [Google Scholar]
  9. Torres, P.; Santos, J.P.; Chow, F.; dos Santos, D.Y. A comprehensive review of traditional uses, bioactivity potential, and chemical diversity of the genus Gracilaria (Gracilariales, Rhodophyta). Algal Res. 2019, 37, 288–306. [Google Scholar] [CrossRef]
  10. Guiry, M. AlgaeBase. World-Wide Electronic Publication, National University of Ireland, Galway. Available online: http://www.algaebase.org/ (accessed on 15 March 2019).
  11. Fleurence, J. Seaweeds as food. In Seaweed in Health and Disease Prevention; Elsevier: Amsterdam, The Netherlands, 2016; pp. 149–167. [Google Scholar]
  12. Yang, L.-E.; Lu, Q.-Q.; Brodie, J. A review of the bladed Bangiales (Rhodophyta) in China: History, culture and taxonomy. Eur. J. Phycol. 2017, 52, 251–263. [Google Scholar] [CrossRef]
  13. Radulovich, R.; Umanzor, S.; Cabrera, R.; Mata, R. Tropical seaweeds for human food, their cultivation and its effect on biodiversity enrichment. Aquaculture 2015, 436, 40–46. [Google Scholar] [CrossRef] [Green Version]
  14. Chapman, A.S.; Stévant, P.; Larssen, W.E. Food or fad? Challenges and opportunities for including seaweeds in a Nordic diet. Bot. Mar. 2015, 58, 423–433. [Google Scholar] [CrossRef]
  15. Garcia-Vaquero, M.; Hayes, M. Red and green macroalgae for fish and animal feed and human functional food development. Food Rev. Int. 2016, 32, 15–45. [Google Scholar] [CrossRef]
  16. Meinita, M.D.N.; Marhaeni, B.; Winanto, T.; Jeong, G.-T.; Khan, M.N.A.; Hong, Y.-K. Comparison of agarophytes (Gelidium, Gracilaria, and Gracilariopsis) as potential resources for bioethanol production. J. Appl. Phycol. 2013, 25, 1957–1961. [Google Scholar] [CrossRef]
  17. Sade, A.; Ali, I.; Ariff, M.R.M. The seaweed industry in Sabah, east Malaysia. Jati-J. Southeast. Asian Stud. 2006, 11, 97–107. [Google Scholar]
  18. Sakthivel, R.; Devi, K.P. Evaluation of physicochemical properties, proximate and nutritional composition of Gracilaria edulis collected from Palk Bay. Food Chem. 2015, 174, 68–74. [Google Scholar] [CrossRef] [PubMed]
  19. Chan, P.T.; Matanjun, P. Chemical composition and physicochemical properties of tropical red seaweed, Gracilaria changii. Food Chem. 2017, 221, 302–310. [Google Scholar] [CrossRef] [PubMed]
  20. Vieira, E.F.; Soares, C.; Machado, S.; Correia, M.; Ramalhosa, M.J.; Oliva-teles, M.T.; Carvalho, A.P.; Domingues, V.F.; Antunes, F.; Oliveira, T.A.C. Seaweeds from the Portuguese coast as a source of proteinaceous material: Total and free amino acid composition profile. Food Chem. 2018, 269, 264–275. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  21. Norziah, M.H.; Ching, C.Y. Nutritional composition of edible seaweed Gracilaria changgi. Food Chem. 2000, 68, 69–76. [Google Scholar] [CrossRef]
  22. Jiménez-Escrig, A.; Sánchez-Muniz, F. Dietary fibre from edible seaweeds: Chemical structure, physicochemical properties and effects on cholesterol metabolism. Nutr. Res. 2000, 20, 585–598. [Google Scholar] [CrossRef]
  23. Rosemary, T.; Arulkumar, A.; Paramasivam, S.; Mondragon-Portocarrero, A.; Miranda, J.M. Biochemical, Micronutrient and Physicochemical Properties of the Dried Red Seaweeds Gracilaria edulis and Gracilaria corticata. Molecules 2019, 24, 2225. [Google Scholar] [CrossRef] [PubMed]
  24. Roohinejad, S.; Koubaa, M.; Barba, F.J.; Saljoughian, S.; Amid, M.; Greiner, R. Application of seaweeds to develop new food products with enhanced shelf-life, quality and health-related beneficial properties. Food Res. Int. 2017, 99, 1066–1083. [Google Scholar] [CrossRef] [PubMed]
  25. Gómez-Ordóñez, E.; Jiménez-Escrig, A.; Rupérez, P. Dietary fibre and physicochemical properties of several edible seaweeds from the northwestern Spanish coast. Food Res. Int. 2010, 43, 2289–2294. [Google Scholar] [CrossRef]
  26. Bocanegra, A.; Bastida, S.; Benedi, J.; Rodenas, S.; Sanchez-Muniz, F.J. Characteristics and nutritional and cardiovascular-health properties of seaweeds. J. Med. Food 2009, 12, 236–258. [Google Scholar] [CrossRef] [PubMed]
  27. Lahaye, M.; Kaeffer, B. Seaweed dietary fibres: Structure, physico-chemical and biological properties relevant to intestinal physiology. Sci. Des Aliment. (Fr.) 1997, 17, 563–584. [Google Scholar]
  28. Phang, S. Seaweed resources in Malaysia: Current status and future prospects. Aquat. Ecosyst. Health Manag. 2006, 9, 185–202. [Google Scholar] [CrossRef]
  29. Phang, S.-M.; Yeong, H.-Y.; Lim, P.-E. The seaweed resources of Malaysia. Botanica Mar. 2019, 62, 265. [Google Scholar] [CrossRef]
  30. Abdullah, N.S.; Muhamad, S.; Omar, I.C.; Abdullah, H. Fatty acids profiles of red seaweed, Gracilaria manilaensis. Exp. 2013, 11, 726–732. [Google Scholar]
  31. Andriani, Y.; Syamsumir, D.F.; Yee, T.C.; Harisson, F.S.; Herng, G.M.; Abdullah, S.A.; Orosco, C.A.; Ali, A.M.; Latip, J.; Kikuzaki, H. Biological activities of isolated compounds from three edible Malaysian red seaweeds, Gracilaria changii, G. manilaensis and Gracilaria Spp. Nat. Prod. Commun. 2016, 11, 1117–1120. [Google Scholar]
  32. Pang, J.-R.; Goh, V.M.-J.; Tan, C.-Y.; Phang, S.-M.; Wong, K.-H.; Yow, Y.-Y. Neuritogenic and in vitro antioxidant activities of Malaysian Gracilaria manilaensis Yamamoto & Trono. J. Appl. Phycol. 2018, 30, 3253–3260. [Google Scholar]
  33. Mæhre, H.K.; Malde, M.K.; Eilertsen, K.E.; Elvevoll, E.O. Characterization of protein, lipid and mineral contents in common Norwegian seaweeds and evaluation of their potential as food and feed. J. Sci. Food Agric. 2014, 94, 3281–3290. [Google Scholar] [CrossRef]
  34. Dawczynski, C.; Schubert, R.; Jahreis, G. Amino acids, fatty acids, and dietary fibre in edible seaweed products. Food Chem. 2007, 103, 891–899. [Google Scholar] [CrossRef]
  35. MacArtain, P.; Gill, C.I.; Brooks, M.; Campbell, R.; Rowland, I.R. Nutritional value of edible seaweeds. Nutr. Rev. 2007, 65, 535–543. [Google Scholar] [CrossRef]
  36. Mišurcová, L.; Machů, L.; Orsavová, J. Seaweed minerals as nutraceuticals. In Advances in food and nutrition research; Elsevier: Amsterdam, The Netherlands, 2011; Volume 64, pp. 371–391. [Google Scholar]
  37. Bauer, A.; Kirby, W.; Sherris, J.C.; Turck, M. Antibiotic susceptibility testing by a standardized single disk method. Am. J. Clin. Pathol. 1966, 45, 493–496. [Google Scholar] [CrossRef] [PubMed]
  38. Rødde, R.S.H.; Vårum, K.M.; Larsen, B.A.; Myklestad, S.M. Seasonal and geographical variation in the chemical composition of the red alga Palmaria palmata (L.) Kuntze. Bot. Mar. 2004, 47, 125–133. [Google Scholar] [CrossRef]
  39. Ito, K.; Hori, K. Seaweed: Chemical composition and potential food uses. Food Rev. Int. 1989, 5, 101–144. [Google Scholar] [CrossRef]
  40. Naidoo, K.; Maneveldt, G.; Ruck, K.; Bolton, J.J. A comparison of various seaweed-based diets and formulated feed on growth rate of abalone in a land-based aquaculture system. J. Appl. Phycol. 2006, 18, 437–443. [Google Scholar] [CrossRef]
  41. Cox, S.; Gupta, S.; Abu-Ghannam, N. Effect of different rehydration temperatures on the moisture, content of phenolic compounds, antioxidant capacity and textural properties of edible Irish brown seaweed. LWT 2012, 47, 300–307. [Google Scholar] [CrossRef]
  42. Patarra, R.F.; Paiva, L.; Neto, A.I.; Lima, E.; Baptista, J. Nutritional value of selected macroalgae. J. Appl. Phycol. 2011, 23, 205–208. [Google Scholar] [CrossRef]
  43. Gupta, S.; Cox, S.; Abu-Ghannam, N. Effect of different drying temperatures on the moisture and phytochemical constituents of edible Irish brown seaweed. LWT-Food Sci. Technol. 2011, 44, 1266–1272. [Google Scholar] [CrossRef] [Green Version]
  44. FAO. FAO Yearbook: Fishery and Aquaculture Statistics; Fao: Rome, Italy, 2016. [Google Scholar]
  45. Lorenzo, J.M.; Agregán, R.; Munekata, P.E.; Franco, D.; Carballo, J.; Şahin, S.; Lacomba, R.; Barba, F.J. Proximate composition and nutritional value of three Macroalgae: Ascophyllum nodosum, Fucus vesiculosus and Bifurcaria bifurcata. Mar. Drugs 2017, 15, 360. [Google Scholar] [CrossRef] [PubMed]
  46. Mabeau, S.; Fleurence, J. Seaweed in food products: Biochemical and nutritional aspects. Trends Food Sci. Technol. 1993, 4, 103–107. [Google Scholar] [CrossRef]
  47. Ansari, A.A.; Ghanem, S.M. Growth attributes and biochemical composition of Padina pavonica (L.) from the Red Sea, in response to seasonal alterations of Tabuk, Saudi Arabia. Egypt. J. Aquat. Res. 2019, 45, 139–144. [Google Scholar] [CrossRef]
  48. Adams, J.; Ross, A.á.; Anastasakis, K.; Hodgson, E.; Gallagher, J.; Jones, J.; Donnison, I. Seasonal variation in the chemical composition of the bioenergy feedstock Laminaria digitata for thermochemical conversion. Bioresour. Technol. 2011, 102, 226–234. [Google Scholar] [CrossRef] [PubMed]
  49. Paiva, L.; Lima, E.; Neto, A.; Baptista, J. Seasonal variability of the biochemical composition and antioxidant properties of Fucus spiralis at two Azorean Islands. Mar. Drugs 2018, 16, 248. [Google Scholar] [CrossRef] [PubMed]
  50. Etemadian, Y.; Shabanpour, B.; Ramzanpour, Z.; Shaviklo, A.R.; Kordjazi, M. Nutritional and Functional Properties of Two Dried Brown Seaweeds Sirophysalis trinodis and Polycladia myricab. J. Aquat. Food Prod. Technol. 2018, 27, 219–235. [Google Scholar] [CrossRef]
  51. Neto, R.T.; Marçal, C.; Queirós, A.S.; Abreu, H.; Silva, A.M.S.; Cardoso, S.M. Screening of Ulva rigida, Gracilaria sp., Fucus vesiculosus and Saccharina latissima as Functional Ingredients. Int. J. Mol. Sci. 2018, 19, 2987. [Google Scholar] [CrossRef] [PubMed]
  52. Rupérez, P. Mineral content of edible marine seaweeds. Food Chem. 2002, 79, 23–26. [Google Scholar] [CrossRef]
  53. Darcy-Vrillon, B. Nutritional aspects of the developing use of marine macroalgae for the human food industry. Int. J. Food Sci. Nutr. (UK) 1993, 44, S23–S35. [Google Scholar]
  54. Marinho, S.; Fonseca, P.; Carneiro, M.; Moreira, W. Seasonal variation in the chemical composition of two tropical seaweeds. Bioresour. Technol. 2006, 97, 2402–2406. [Google Scholar] [CrossRef]
  55. Benjama, O.; Masniyom, P. Biochemical composition and physicochemical properties of two red seaweeds (Gracilaria fisheri and G. tenuistipitata) from the Pattani Bay in Southern Thailand. Sonklanakarin J. Sci. Technol. 2012, 34, 223–230. [Google Scholar]
  56. Tabarsa, M.; Rezaei, M.; Ramezanpour, Z.; Waaland, J.R. Chemical compositions of the marine algae Gracilaria salicornia (Rhodophyta) and Ulva lactuca (Chlorophyta) as a potential food source. J. Sci. Food Agric. 2012, 92, 2500–2506. [Google Scholar] [CrossRef]
  57. Schmid, M.; Guihéneuf, F.; Stengel, D.B. Fatty acid contents and profiles of 16 macroalgae collected from the Irish Coast at two seasons. J. Appl. Phycol. 2014, 26, 451–463. [Google Scholar] [CrossRef]
  58. Galland-Irmouli, A.-V.; Fleurence, J.; Lamghari, R.; Luçon, M.; Rouxel, C.; Barbaroux, O.; Bronowicki, J.-P.; Villaume, C.; Guéant, J.-L. Nutritional value of proteins from edible seaweed Palmaria palmata (Dulse). J. Nutr. Biochem. 1999, 10, 353–359. [Google Scholar] [CrossRef]
  59. Benjama, O.; Masniyom, P. Nutritional composition and physicochemical properties of two green seaweeds (Ulva pertusa and U. intestinalis) from the Pattani Bay in Southern Thailand. Sonklanakarin J. Sci. Technol. 2011, 33, 575–583. [Google Scholar]
  60. Juneja, A.; Ceballos, R.; Murthy, G. Effects of environmental factors and nutrient availability on the biochemical composition of algae for biofuels production: A review. Energies 2013, 6, 4607–4638. [Google Scholar] [CrossRef]
  61. Khairy, H.M.; El-Shafay, S.M. Seasonal variations in the biochemical composition of some common seaweed species from the coast of Abu Qir Bay, Alexandria, Egypt. Oceanologia 2013, 55, 435–452. [Google Scholar] [CrossRef] [Green Version]
  62. Lahaye, M.; Jegou, D. Chemical and physical-chemical characteristics of dietary fibres from Ulva lactuca (L.) Thuret and Enteromorpha compressa (L.) Grev. J. Appl. Phycol. 1993, 5, 195. [Google Scholar] [CrossRef]
  63. Rupérez, P.; Saura-Calixto, F. Dietary fibre and physicochemical properties of edible Spanish seaweeds. Eur. Food Res. Technol. 2001, 212, 349–354. [Google Scholar] [CrossRef]
  64. Kumari, P.; Bijo, A.; Mantri, V.A.; Reddy, C.; Jha, B. Fatty acid profiling of tropical marine macroalgae: An analysis from chemotaxonomic and nutritional perspectives. Phytochemistry 2013, 86, 44–56. [Google Scholar] [CrossRef]
  65. Bhaskar, N.; Kinami, T.; Miyashita, K.; Park, S.-B.; Endo, Y.; Fujimoto, K. Occurrence of conjugated polyenoic fatty acids in seaweeds from the Indian Ocean. Z. Für Nat. C 2004, 59, 310–314. [Google Scholar] [CrossRef]
  66. Khotimchenko, S.; Vaskovsky, V.; Titlyanova, T. Fatty acids of marine algae from the Pacific coast of North California. Bot. Mar. 2002, 45, 17–22. [Google Scholar] [CrossRef]
  67. Francavilla, M.; Franchi, M.; Monteleone, M.; Caroppo, C. The red seaweed Gracilaria gracilis as a multi products source. Mar. Drugs 2013, 11, 3754–3776. [Google Scholar] [CrossRef]
  68. Syad, A.N.; Shunmugiah, K.P.; Kasi, P.D. Seaweeds as nutritional supplements: Analysis of nutritional profile, physicochemical properties and proximate composition of G. acerosa and S. wightii. Biomed. Prev. Nutr. 2013, 3, 139–144. [Google Scholar] [CrossRef]
  69. Cian, R.E.; Fajardo, M.A.; Alaiz, M.; Vioque, J.; González, R.J.; Drago, S.R. Chemical composition, nutritional and antioxidant properties of the red edible seaweed Porphyra columbina. Int. J. Food Sci. Nutr. 2014, 65, 299–305. [Google Scholar] [CrossRef] [PubMed]
  70. Watson, R.R.; Zibadi, S. Bioactive Dietary Factors and Plant Extracts in Dermatology; Springer: Berlin, Germany, 2013. [Google Scholar]
  71. Hong, D.D.; Hien, H.M.; Son, P.N. Seaweeds from Vietnam used for functional food, medicine and biofertilizer. J. Appl. Phycol. 2007, 19, 817–826. [Google Scholar] [CrossRef]
  72. Cofrades, S.; López-Lopez, I.; Bravo, L.; Ruiz-Capillas, C.; Bastida, S.; Larrea, M.T.; Jiménez-Colmenero, F. Nutritional and antioxidant properties of different brown and red Spanish edible seaweeds. Food Sci. Technol. Int. 2010, 16, 361–370. [Google Scholar] [CrossRef] [PubMed]
  73. Kolb, N.; Vallorani, L.; Stocchi, V. Chemical composition and evaluation of protein quality by amino acid score method of edible brown marine algae Arame (Eisenia bicyclis) and Hijiki (Hijikia fusiforme). Acta Aliment. 1999, 28, 213–222. [Google Scholar] [CrossRef]
  74. FAO; WHO; UNU. Amino acid requirements of adults. In Protein and Amino Acids Requirements in Human Nutrition; World Health Organization: Rome, Italy, 2007; Volume 7, pp. 135–159. [Google Scholar]
  75. Mišurcová, L.; Buňka, F.; Ambrožová, J.V.; Machů, L.; Samek, D.; Kráčmar, S. Amino acid composition of algal products and its contribution to RDI. Food Chem. 2014, 151, 120–125. [Google Scholar] [CrossRef] [PubMed]
  76. Feng, Q.; Bo, F.; Lu, Y. Influence of copper ions and calcium ions on adsorption of CMC on chlorite. Trans. Nonferrous Met. Soc. China 2013, 23, 237–242. [Google Scholar] [CrossRef]
  77. El-Din, N.S.; Mohamedein, L.; El-Moselhy, K.M. Seaweeds as bioindicators of heavy metals off a hot spot area on the Egyptian Mediterranean Coast during 2008–2010. Environ. Monit. Assess. 2014, 186, 5865–5881. [Google Scholar] [CrossRef]
  78. Astorga-España, M.; Galdón, B.R.; Rodríguez, E.R.; Romero, C.D. Mineral and trace element concentrations in seaweeds from the sub-Antarctic ecoregion of Magallanes (Chile). J. Food Compos. Anal. 2015, 39, 69–76. [Google Scholar] [CrossRef]
  79. Moreiras, O.; Carbajal, A.; Cabrera, L.; Cuadrado, C. Tablas de composición de alimentos (Food Composition Tables); Piramide Ediciones Sa: Madrid, Spanish, 2004. [Google Scholar]
  80. Burtin, P. Nutritional value of seaweeds. Electron. J. Environ. Agric. Food Chem. 2003, 2, 498–503. [Google Scholar]
  81. Rubio, C.; Napoleone, G.; Luis-González, G.; Gutiérrez, A.J.; González-Weller, D.; Hardisson, A.; Revert, C. Metals in edible seaweed. Chemosphere 2017, 173, 572–579. [Google Scholar] [CrossRef] [PubMed]
  82. Arulkumar, A.; Nigariga, P.; Paramasivam, S.; Rajaram, R. Metals accumulation in edible marine algae collected from Thondi coast of Palk Bay, Southeastern India. Chemosphere 2019, 221, 856–862. [Google Scholar] [CrossRef] [PubMed]
  83. Coultate, T.P. Food: The chemistry of its components; Royal Society of Chemistry: London, UK, 2009. [Google Scholar]
  84. Flores, S.R.; Dobbs, J.; Dunn, M.A. Mineral nutrient content and iron bioavailability in common and Hawaiian seaweeds assessed by an in vitro digestion/Caco-2 cell model. J. Food Compos. Anal. 2015, 43, 185–193. [Google Scholar] [CrossRef]
  85. Chen, Q.; Pan, X.-D.; Huang, B.-F.; Han, J.-L. Distribution of metals and metalloids in dried seaweeds and health risk to population in southeastern China. Sci. Rep. 2018, 8, 3578. [Google Scholar] [CrossRef] [PubMed]
  86. FAO; WHO. Evaluation of Certain Food Additives and Contaminants: Sixty-Ninth Report of the Joint FAO/WHO Expert Committee on Food Additives; World Health Organization: Rome, Italy, 2009. [Google Scholar]
  87. FAOWHOEvaluation of Certain Food Additives and Contaminants: Seventy-Fourth Report of the Joint FAO/WHO Expert Committee on Food Additives; World Health Organization: Rome, Italy, 2011.
  88. Larrea-Marín, M.; Pomares-Alfonso, M.; Gómez-Juaristi, M.; Sánchez-Muniz, F.; De La Rocha, S.R. Validation of an ICP-OES method for macro and trace element determination in Laminaria and Porphyra seaweeds from four different countries. J. Food Compos. Anal. 2010, 23, 814–820. [Google Scholar] [CrossRef]
  89. Krewski, D.; Yokel, R.A.; Nieboer, E.; Borchelt, D.; Cohen, J.; Harry, J.; Kacew, S.; Lindsay, J.; Mahfouz, A.M.; Rondeau, V. Human health risk assessment for aluminium, aluminium oxide, and aluminium hydroxide. J. Toxicol. Environ. HealthPart. B 2007, 10, 1–269. [Google Scholar] [CrossRef]
  90. Singh, S.; Tripathi, D.K.; Singh, S.; Sharma, S.; Dubey, N.K.; Chauhan, D.K.; Vaculík, M. Toxicity of aluminium on various levels of plant cells and organism: A review. Environ. Exp. Bot. 2017, 137, 177–193. [Google Scholar] [CrossRef]
  91. Ismail, A. A need for monitoring of heavy metals and organotin compounds in the east coast of Johor. In Research and information series of Malaysian coast of Malaysia marine ecosystem; Che Abdul Rahim, M., Masri, M.A., Zaidi, C.K., Norhayati, A., Eds.; Marine Ecosystem Research Centre UKM: Bangi, Malaysia, 2008; pp. 163–176. [Google Scholar]
  92. Ismail, N.A.H.; Wee, S.Y.; Aris, A.Z. Bisphenol A and alkylphenols concentrations in selected mariculture fish species from Pulau Kukup, Johor, Malaysia. Mar. Pollut. Bull. 2018, 127, 536–540. [Google Scholar] [CrossRef]
  93. Sidi, N.; Aris, A.Z.; Mohamat Yusuff, F.; Looi, L.J.; Mokhtar, N.F. Tape seagrass (Enhalus acoroides) as a bioindicator of trace metal contamination in Merambong shoal, Johor Strait, Malaysia. Mar. Pollut. Bull. 2018, 126, 113–118. [Google Scholar] [CrossRef]
  94. Verstraeten, S.V.; Aimo, L.; Oteiza, P.I. Aluminium and lead: Molecular mechanisms of brain toxicity. Arch. Toxicol. 2008, 82, 789–802. [Google Scholar] [CrossRef] [PubMed]
  95. Chamannejadian, A.; Sayyad, G.; Moezzi, A.; Jahangiri, A. Evaluation of estimated daily intake (EDI) of cadmium and lead for rice (Oryza sativa L.) in calcareous soils. Iran. J. Environ. Health Sci. Eng. 2013, 10, 28. [Google Scholar] [CrossRef] [PubMed]
  96. Medeiros, R.J.; dos Santos, L.M.G.; Freire, A.S.; Santelli, R.E.; Braga, A.M.C.; Krauss, T.M.; Jacob, S.d.C. Determination of inorganic trace elements in edible marine fish from Rio de Janeiro State, Brazil. Food Control. 2012, 23, 535–541. [Google Scholar] [CrossRef] [Green Version]
  97. Almela, C.; Clemente, M.J.; Vélez, D.; Montoro, R. Total arsenic, inorganic arsenic, lead and cadmium contents in edible seaweed sold in Spain. Food Chem. Toxicol. 2006, 44, 1901–1908. [Google Scholar] [CrossRef]
  98. Yaich, H.; Garna, H.; Besbes, S.; Paquot, M.; Blecker, C.; Attia, H. Chemical composition and functional properties of Ulva lactuca seaweed collected in Tunisia. Food Chem. 2011, 128, 895–901. [Google Scholar] [CrossRef]
  99. Wong, K.; Cheung, P.C. Nutritional evaluation of some subtropical red and green seaweeds: Part I—proximate composition, amino acid profiles and some physico-chemical properties. Food Chem. 2000, 71, 475–482. [Google Scholar] [CrossRef]
  100. Carvalho, A.; Portela, M.; Sousa, M.; Martins, F.; Rocha, F.; Farias, D.; Feitosa, J. Physiological and physico-chemical characterization of dietary fibre from the green seaweed Ulva fasciata Delile. Braz. J. Biol. 2009, 69, 969–977. [Google Scholar] [CrossRef]
  101. Fleury, N.; Lahaye, M. Chemical and physico-chemical characterisation of fibres from Laminaria digitata (kombu breton): A physiological approach. J. Sci. Food Agric. 1991, 55, 389–400. [Google Scholar] [CrossRef]
  102. Pina-Pérez, M.C.; Rivas, A.; Martínez, A.; Rodrigo, D. Antimicrobial potential of macro and microalgae against pathogenic and spoilage microorganisms in food. Food Chem. 2017, 235, 34–44. [Google Scholar] [CrossRef]
  103. Darah, I.; Tong, W.Y.; Nor-Afifah, S.; Nurul-Aili, Z.; Lim, S.H. Antimicrobial effects of Caulerpa sertularioides extract on foodborne diarrhea-caused bacteria. Eur Rev. Med. Pharm. Sci 2014, 18, 171–178. [Google Scholar]
  104. Lima-Filho, J.V.M.; Carvalho, A.F.F.U.; Freitas, S.M.; Melo, V.M.M. Antibacterial activity of extracts of six macroalgae from the Northeastern Brazilian coast. Braz. J. Microbiol. 2002, 33, 311–314. [Google Scholar] [CrossRef]
  105. Arulkumar, A.; Rosemary, T.; Paramasivam, S.; Rajendran, R.B. Phytochemical composition, in vitro antioxidant, antibacterial potential and GC-MS analysis of red seaweeds (Gracilaria corticata and Gracilaria edulis) from Palk Bay, India. Biocatal. Agric. Biotechnol. 2018, 15, 63–71. [Google Scholar] [CrossRef]
  106. Deepak, P.; Sowmiya, R.; Kamaraj, C.; Josebin, M.P.D.; Aiswarya, D.; Balasubramani, G.; Amutha, V.; Perumal, P. Gc-Ms Profiling, Chemical Characterization, Antioxidant, Î ‘-Amylase And Î ‘-Glucosidase Inhibition Of Selected Seaweeds From Southeast Coast Of India: An In Vitro Approach. J. Drug Deliv. Ther. 2018, 8, 60–72. [Google Scholar] [CrossRef]
  107. Narasimhan, M.K.; Pavithra, S.K.; Krishnan, V.; Chandrasekaran, M. In vitro analysis of antioxidant, antimicrobial and antiproliferative activity of Enteromorpha antenna, Enteromorpha linza and Gracilaria corticata extracts. Jundishapur J. Nat. Pharm. Prod. 2013, 8, 151–159. [Google Scholar] [CrossRef] [PubMed]
  108. García-Bueno, N.; Decottignies, P.; Turpin, V.; Dumay, J.; Paillard, C.; Stiger-Pouvreau, V.; Kervarec, N.; Pouchus, Y.-F.; Marín-Atucha, A.A.; Fleurence, J. Seasonal antibacterial activity of two red seaweeds, Palmaria palmata and Grateloupia turuturu, on European abalone pathogen Vibrio harveyi. Aquat. Living Resour. 2014, 27, 83–89. [Google Scholar] [CrossRef]
  109. Pérez, M.J.; Falqué, E.; Domínguez, H. Antimicrobial Action of Compounds from Marine Seaweed. Mar. Drugs 2016, 14, 52. [Google Scholar] [CrossRef] [PubMed]
  110. Juneng, L.; Tangang, F.T. Level and source of predictability of seasonal rainfall anomalies in Malaysia using canonical correlation analysis. Int. J. Climatol. A J. R. Meteorol. Soc. 2008, 28, 1255–1267. [Google Scholar] [CrossRef]
  111. Awang, H.; Daud, Z.; Hatta, M.Z.M. Hydrology properties and water quality assessment of the Sembrong Dam, Johor, Malaysia. Procedia-Soc. Behav. Sci. 2015, 195, 2868–2873. [Google Scholar] [CrossRef]
  112. Wong, C.L.; Liew, J.; Yusop, Z.; Ismail, T.; Venneker, R.; Uhlenbrook, S. Rainfall Characteristics and Regionalization in Peninsular Malaysia Based on a High Resolution Gridded Data Set. Water 2016, 8, 500. [Google Scholar] [CrossRef]
  113. Baharim, N.B.; Yusop, Z.; Yusoff, I.; Tahir, W.; Askari, M.; Othman, Z.; Abidin, M.R.Z. The relationship between heavy metals and trophic properties in Sembrong Lake, Johor. Sains Malays. 2016, 45, 43–53. [Google Scholar]
  114. Malaysia, M.D. Climate change scenarios for Malaysia 2001–2099. Malaysia Meteorological Department: Petaling Jaya, Malaysia; p. 2009.
  115. Daryabor, F.; Ooi, S.H.; Samah, A.A.; Akbari, A. Dynamics of the water circulations in the southern South China Sea and its seasonal transports. PLoS ONE 2016, 11, e0158415. [Google Scholar] [CrossRef] [PubMed]
  116. Guest, J.R.; Baird, A.H.; Maynard, J.A.; Muttaqin, E.; Edwards, A.J.; Campbell, S.J.; Yewdall, K.; Affendi, Y.A.; Chou, L.M. Contrasting patterns of coral bleaching susceptibility in 2010 suggest an adaptive response to thermal stress. PLoS ONE 2012, 7, e33353. [Google Scholar] [CrossRef]
  117. Daryabor, F.; Tangang, F.; Juneng, L. Simulation of southwest monsoon current circulation and temperature in the east coast of Peninsular Malaysia. Sains Malays. 2014, 43, 389–398. [Google Scholar]
  118. Hurd, C.L.; Harrison, P.J.; Bischof, K.; Lobban, C.S. Seaweed Ecology and Physiology; Cambridge University Press: Cambridge, UK, 2014. [Google Scholar]
  119. May-Lin, B.Y.; Ching-Lee, W. Seasonal growth rate of Sargassum species at Teluk Kemang, Port Dickson, Malaysia. J. Appl. Phycol. 2013, 25, 805–814. [Google Scholar] [CrossRef]
  120. Kraufvelin, P.; Lindholm, A.; Pedersen, M.F.; Kirkerud, L.A.; Bonsdorff, E. Biomass, diversity and production of rocky shore macroalgae at two nutrient enrichment and wave action levels. Mar. Biol. 2010, 157, 29–47. [Google Scholar] [CrossRef]
  121. AOAC. Official methods of analysis of AOAC International; Association of Official Analytical Chemists: Rockville, MD, USA, 2000. [Google Scholar]
  122. Tibbetts, S.M.; Milley, J.E.; Lall, S.P. Nutritional quality of some wild and cultivated seaweeds: Nutrient composition, total phenolic content and in vitro digestibility. J. Appl. Phycol. 2016, 28, 3575–3585. [Google Scholar] [CrossRef]
  123. Zhou, A.Y.; Robertson, J.; Hamid, N.; Ma, Q.; Lu, J. Changes in total nitrogen and amino acid composition of New Zealand Undaria pinnatifida with growth, location and plant parts. Food Chem. 2015, 186, 319–325. [Google Scholar] [CrossRef] [PubMed]
  124. Heems, D.; Luck, G.; Fraudeau, C.; Verette, E. Fully automated precolumn derivatization, on-line dialysis and high-performance liquid chromatographic analysis of amino acids in food, beverages and feedstuff. J. Chromatogr. A 1998, 798, 9–17. [Google Scholar] [CrossRef]
  125. Gosch, B.J.; Magnusson, M.; Paul, N.A.; de Nys, R. Total lipid and fatty acid composition of seaweeds for the selection of species for oil-based biofuel and bioproducts. Gcb Bioenergy 2012, 4, 919–930. [Google Scholar] [CrossRef] [Green Version]
  126. Petrović, M.; Kezić, N.; Bolanča, V. Optimization of the GC method for routine analysis of the fatty acid profile in several food samples. Food Chem. 2010, 122, 285–291. [Google Scholar] [CrossRef]
  127. James, C.S. Analytical chemistry of foods; Springer Science & Business Media: Berlin, Germany, 2013. [Google Scholar]
  128. Carefoot, T. Calorimetry. Handbook of Phycological Methods. Ecological Field Methods: Macroalgae; Cambridge Univ. Press: Cambridge, UK, 1985; pp. 479–491. [Google Scholar]
  129. McDermid, K.J.; Stuercke, B. Nutritional composition of edible Hawaiian seaweeds. J. Appl. Phycol. 2003, 15, 513–524. [Google Scholar] [CrossRef]
  130. Jaworska, G.; Pogoń, K.; Bernaś, E.; Skrzypczak, A.; Kapusta, I. Vitamins, phenolics and antioxidant activity of culinary prepared Suillus luteus (L.) Roussel mushroom. LWT–Food Sci. Technol. 2014, 59, 701–706. [Google Scholar] [CrossRef]
  131. Pan, Y.; Wernberg, T.; de Bettignies, T.; Holmer, M.; Li, K.; Wu, J.; Lin, F.; Yu, Y.; Xu, J.; Zhou, C. Screening of seaweeds in the East China Sea as potential bio-monitors of heavy metals. Environ. Sci. Pollut. Res. 2018, 25, 16640–16651. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  132. Waheed, A.; Chohan, M.M.; Ahmed, D.; Ullah, N. The first report on the in vitro antimicrobial activities of extracts of leaves of Ehretia serrata. Saudi J. Biol. Sci. 2018. [Google Scholar] [CrossRef]
Sample Availability: Samples of the compounds are not available from the authors.
Table 1. Variation in Proximate Composition (g 100 g−1 DW) and Gross Calorific Value (cal g−1) Of G. manilaensis Collected in Johor, Malaysia.
Table 1. Variation in Proximate Composition (g 100 g−1 DW) and Gross Calorific Value (cal g−1) Of G. manilaensis Collected in Johor, Malaysia.
CompositionG. manilaensis
(NEM)
G. manilaensis
(SWM)
Moisture9.59 ± 0.409.06 ± 0.10
Ash30.26±0.13 b38.48 ± 0.23 a
Crude Lipids1.20 ± 0.151.13 ± 0.18
Crude Protein19.39 ± 0.12 a16.03 ± 0.26 b
Pure protein16.38 ± 0.24 a12.34 ± 0.31 b
NPN3.01 ± 0.503.69 ± 0.11
Carbohydrate39.56 ± 0.26 a35.30 ± 0.34 b
Total Dietary Fiber31.07 ± 1.08 a22.16 ± 0.11 b
Caloric Value (cal g−1)2721.67 ± 10.69 a2348.33 ± 9.87 b
NEM, samples from Northeast Monsoon (Straits of Johor). SWM, samples from Southwest Monsoon (Straits of Johor). Results are expressed as Mean ± SD (n = 3). Means with different superscripts (a,b) within the same line were significantly different (p < 0.05).
Table 2. Variation in the Fatty Acid Composition (g Fatty Acid Methyl Esters/100 g Total Fat) of G. manilaensis.
Table 2. Variation in the Fatty Acid Composition (g Fatty Acid Methyl Esters/100 g Total Fat) of G. manilaensis.
Fatty Acids (g 100 g−1 DW)G. manilaenisis (NEM)G. manilaensis (SWM)
SFAs
Myristic acid (C14:0)2.6 b3.73 ± 0.06 a
Pentadecanoic acid (C15:0)0.9ND
Palmitic acid (C16:0)89.27 ± 0.21 a83.87 ± 0.64 b
Heptadecanoic acid (C17:0)0.77 ± 0.06ND
Stearic acid (C18:0)3.97 ± 0.06 b6.2 ± 0.7 a
Total97.5 ± 0.05 a93.8 ± 0.15 b
% of SFA in total FAs97.57 ± 0.05 a93.8 ± 0.03 b
MUFAs
Oleic acid (C18:1ῳ9 cis)1.47 ± 0.06 b6.19 ± 0.32 a
% of MUFAs in total FAs1.47 ± 0.03 b6.19 ± 0.18 a
PUFAs
Eicosadienoic acid (C20:2 ∆11,14)0.97 ± 0.06ND
% of PUFAs in total FAs0.97 ± 0.03-
Total fatty acids99.97 ± 0.0699.99 ± 0.06
Mean ± standard deviation of three replicates. Different lowercase letters within the same row indicate statistical differences between groups (p < 0.05). “ND” indicates “not detected”; polyunsaturated fatty acids (PUFA); monounsaturated fatty acids (MUFA); saturated fatty acids (SFA).
Table 3. Variation in the Amino Acids Composition (mg 100 g⁻1 DW) of G. manilaensis.
Table 3. Variation in the Amino Acids Composition (mg 100 g⁻1 DW) of G. manilaensis.
Amino acidsG. manilaensis
(NEM)
mg g−1
Protein/(AA Score (g 100 g−1)
G. manilaensis
(SWM)
mg 100 g−1
Protein/AA Score (g 100 g−1)
FAO/WHO/UNU (2007)
Essential Amino acids
Histidine (His)620.98 ± 0.2332.03 (200.16)NDND16
Threonine (Thr)400.74 ± 0.29 a20.67 (82.67)231.73 ± 8.66 b14.46 (90.35)25
Valine (Val)282.21 ± 0.10 a14.56 (36.39)96.39 ± 11.80 b6.01 (15.03)40
Methionine (Met)393.13 ± 0.1620.28 (88.15)NDND23
Tryptophan (Try)4.37 ± 0.020.2254*(3.22)NDND7
Phenylalanine (Phe)282.07± 0.09 a14.55 (35.48)85.85 ± 2.35 b5.36 (13.06)41
Isoleucine (Ile)285.34 ± 0.12 a14.72 (49.05)62.90 ± 4.30 b3.92 (13.08)30
Leucine (Leu)331.67 ± 0.17 a17.19 (28.04)58.51 ± 1.99 b3.65 (5.98)61
Lysine (Lys)239.69 ± 0.06 a12.36 (25.75)129.62 ± 6.45 b8.09 (16.85)48
TEAAs2840.20 ± 0.31 a146.59665.02 ± 0.07 b41.49291
Non-essential acids
Aspartic acid (Asp)9640.82 ± 0.22 a 6984.12 ± 0.18 b
Glutamic acid (Glu)1583.21 ± 0.54 a 1423.74 ± 1.10 b
Asparagine (Asn)ND ND
Serine (Ser)304.44 ± 0.18 a 289.97 ± 0.16 b
Glutamine (Gln)ND ND
Glycine (Gly)216.77 ± 0.06 b 364.15 ± 0.11 a
Arginine (Arg)573.41 ± 0.27 b 830.29 ± 0.15 a
Alanine (Ala)314.29 ± 0.18 b 1366.05 ± 0.12 a
Tyrosine (Tyr)499.26 ± 0.22 a 196.47 ± 0.15 b
Cysteine (Cys)200.82 ± 0.33 ND
Proline (Pro)185.14 ± 0.09 a 123.23 ± 0.03 b
∑∑NEAA13517.96 ± 1.13 a 11578.01 ± 1.33 b
∑AA16358.37 ± 1.31 a 12243.04 ± 1.26 b
EAAs/Total AA0.17 ± 0.14 a 0.05 ± 0.12 b
∑EAAS/Total AAs(%)17.36 ± 0.14 a 5.43 ± 0.12 b
∑EAAs/∑NEAAs0.2101 ± 0.0021 a 0.0573 ± 0.0011 b
The FAO requirement protein pattern referenced is amino acid scoring pattern for use in schoolchild/adolescent (3–10) year of age (WHO/FAO/UNU 2007). AA = Total Amino acids. (mean ± standard deviation values) (n = 3). expressed as mg/g seaweed on a dry weight basis. * EAAs: Essential amino acids; NEAAs: Non-essential amino acids. a,b values with different superscripts within the same line are significantly different.
Table 4. Seasonal Variation in the Mineral Composition (mg 100 g1 DW) of Edible G. manilaensis as Compared With the Dietary Reference Intake Values (RNI) (8 g Day1) of Australia.
Table 4. Seasonal Variation in the Mineral Composition (mg 100 g1 DW) of Edible G. manilaensis as Compared With the Dietary Reference Intake Values (RNI) (8 g Day1) of Australia.
Minerals
(mg 100 g−1)
G. manilaensis (NEM)G. manilaensis (SWM)Australia (RDIs)
Macro Metals
Calcium (Ca)4047.74 (32.38)1750.97 (14.01)1000 mg/day
Magnesium (mg)1.16 (0.023)2.09 (0.042)400 mg/day
Potassium (K)21.05(0.06)39.21 (0.11)2.8 & 3.8 g/day AI
Sodium (Na)7.02 (0.02)1.33 (0.01)2.3 g/day UL
Na/K0.330.03 <0.49
Total4076.971793.60
Trace Metals
Copper (Cu)0.31 (0.25)0.39 (0.31)10 mg/day UL
Iron (Fe)1512.55 (672.24)1346.05 (598.24)8–18 mg/day
Manganese (Mn)142.34 (207040)401.81 (584455)5.0 & 5.5 µg/day AI
Molybdenum (Mo)0.05 (8.89)0.03 (5.33)0.045mg/day
Selenium (Se)0.048 (5.5)0.057 (6.2)60 &70 µg/day
Zinc (Zn)16.40 (9.4)4.42 (2.5)0.8 &14 mg/day
Chromium (Cr)0.26 (59.44)0.19 (43.43)25 & 35 µg/day AI
Cobalt (Co)0.060.22
Total1672.021753.17
Heavy Metal/
EDIs (g 100 g−1)
WHO/FAO TWIs
Arsenic (As)0.46 (38.33)0.58(48.33)15 µg/kg BW
Cadmium (Cd)0.004 (0.71) 0.009 (1.61)7 µg/kg BW
Aluminium (Al)188.83 *(236.04)137.98*(172.48)1000µg/d body BW
Lead (Pb)1.38 (69)0.536 (26.8)25µg/kg BW
Triplicate measurements of each sample with RSD is less than 10 g 100 g−1 Values indicated in () represents the approximate % of estimated daily intakes (EDIs) in comparison to the Recommended Dietary Allowances (RDA) [36]. Method Detection Limit (MDL). Nutrient reference values for Australia and New Zealand for men and women (Australia New Zealand Food Authority, 2005). Recommended Daily Intake (RDI); Tolerable Upper Intake Level (UL); Adequate Intake (AI); Body Weight (BW), provisional tolerable weekly intakes (PTWIs) (FAO/ WHO, 2011).
Table 5. Variation in Vitamin Composition (mg g1 DW), Chlorophyll A and B Content (µg g−1 DW) of G. manilaensis.
Table 5. Variation in Vitamin Composition (mg g1 DW), Chlorophyll A and B Content (µg g−1 DW) of G. manilaensis.
Composition
(mg 100 g−1 DW)
G. manilaensis (NWM)G. manilaensis (SWM)
Vitamin A (IU g−1)Below detectable level (<1)ND (<1)
Vitamin B1Below detectable level (<1)ND (<1)
Vitamin B20.29 ± 0.060.38 ± 0.06
Vitamin D (mcg 100 g−1)Below detectable level (<5)ND (<5)
Chlorophyll a1.25 ± 0.06 a1.29 ± 0.06 b
Chlorophyll b9.57 ± 0.01 a7.07 ± 0.03 b
Results are expressed as Mean ± SD (n = 3). a,b values with different superscripts within the same line are significantly different.
Table 6. Variation in The Physicochemical Properties of Edible G. manilaensis at 25 °C and 37 °C.
Table 6. Variation in The Physicochemical Properties of Edible G. manilaensis at 25 °C and 37 °C.
SeaweedSWC (mL g−1)WHC (g g−1)OHC (g g−1)
25 °C37 °C25 °C37 °C25 °C
G. manilaensis (NEM)7.15 ± 0.57 bB9.91 ± 0.05 aA 9.81 ± 0.76 bB11.89 ± 0.37 aA1.97 ± 0.20 a
G. manilaensis (SWM)7.92 ± 0.98 aB 9.80 ± 0.06 bA 9.94 ± 0.67 aA11.07 ± 0.57 bB1.59 ± 0.21 b
Values are Mean ± SEM, n = 2 on DW. a,b values with different superscripts within the same column are significantly different between seaweeds. A,B values with different superscripts within the same line shows significant differences between temperatures.

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Aroyehun, A.Q.; Palaniveloo, K.; Ghazali, F.; Rizman-Idid, M.; Abdul Razak, S. Effects of Seasonal Variability on the Physicochemical, Biochemical, and Nutritional Composition of Western Peninsular Malaysia Gracilaria manilaensis. Molecules 2019, 24, 3298. https://doi.org/10.3390/molecules24183298

AMA Style

Aroyehun AQ, Palaniveloo K, Ghazali F, Rizman-Idid M, Abdul Razak S. Effects of Seasonal Variability on the Physicochemical, Biochemical, and Nutritional Composition of Western Peninsular Malaysia Gracilaria manilaensis. Molecules. 2019; 24(18):3298. https://doi.org/10.3390/molecules24183298

Chicago/Turabian Style

Aroyehun, Abdul Qudus, Kishneth Palaniveloo, Farid Ghazali, Mohammed Rizman-Idid, and Shariza Abdul Razak. 2019. "Effects of Seasonal Variability on the Physicochemical, Biochemical, and Nutritional Composition of Western Peninsular Malaysia Gracilaria manilaensis" Molecules 24, no. 18: 3298. https://doi.org/10.3390/molecules24183298

APA Style

Aroyehun, A. Q., Palaniveloo, K., Ghazali, F., Rizman-Idid, M., & Abdul Razak, S. (2019). Effects of Seasonal Variability on the Physicochemical, Biochemical, and Nutritional Composition of Western Peninsular Malaysia Gracilaria manilaensis. Molecules, 24(18), 3298. https://doi.org/10.3390/molecules24183298

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