The species
Antioxidants are composed of numerous compounds and bioactive molecules obtained from a variety of sources (Reddy et al. 2011). Those from natural sources play an important role in the neutralization of oxidative stress (Sasikumar et al. 2009). Antioxidants are bioactive compounds that prevent the reaction of compounds or molecules with oxygen or free radicals (Abdel-Satter et al. 2007). Bivalve species are filter-feeding organisms that feed by filtering the seawater. In other words, they feed on organic and inorganic matter and microalgae (Gosling 2003). Microalgae are an important source of antioxidants (Goiris et al. 2012). Recently conducted research aimed at obtaining valuable algal metabolites from algae. Phycobiliproteins (anticancer agents) extracted from red algae and cyanobacteria, beta carotenes from
Carotenoids are a family of natural compounds in living organisms. Some studies correlate diets rich in carotenoids with minimizing the risk of several chronic and degenerative diseases, including cancer (Nishino 1998), cardiovascular disorders (Sesso et al. 2004) and age-related macular degeneration (Zeegers et al. 2001). Carotenoids are a group of yellow-orange pigments, mostly divided into two general classes: oxidized derivatives known as hydrocarbon carotenes and xanthophylls. More than 650 different natural carotenoids are found in bacteria, fungi, plants and animals (Matsuno 2001). Related studies showed that carotenoids are abundant in some mollusks such as Polyplacophora (Peebles et al. 2017), Gastropoda (Wei et al. 2019), Bivalvia (Borodina 2016) and Cephalopoda (Navarro et al. 2014). Thalassic carotenoids have different structures and most of them can be obtained from β-carotene, fucoxanthin, peridinin, diatoxanthin, alloxanthin and astaxanthin (Maoka 2011). In general, carotenoids give the skin and muscles of some fish and the soft tissues and shells of mollusks a certain glow and clarity (Li et al. 2010; Peebles et al. 2017). The total content of carotenoids (TCC) ranges from 10 to 140 μg/100 g depending on the species and tissue of mollusks. Mollusks do not synthesize carotenoids by themselves but obtain them through feeding on algae and accumulate them in their bodies. Some of the carotenoids are metabolized into retinol derivatives in the mollusk tissues (Kantha 1989). Carotenoids are responsible for tissue pigmentation, especially in aquatic animals (García-Chavarría & Lara-Flores 2013). Some carotenoids are also precursors of vitamin A (Miki et al. 1982). Carotenoids are essential for the growth and maturity of gonads and a high rate of fertilization (Sánchez et al. 2016). Carotenoids accumulated in mollusks through food intake are passed on to fish and humans who eat them (Czeczuga 1980).
The study was performed at the location referred to as Abidealtı on the Gallipoli Peninsula, the Çanakkale Province, Turkey (40°03′02″N; 26°12′54″E), between May 2011 and April 2012 (Fig. 1). The study area is 0.5–2 m deep, with the bottom structure being granular and sandy, covered sporadically with the seagrass
After being cleaned, razor clams were transported to the laboratory. Soft tissues were completely removed from shells and freeze dried.
Samples were extracted using methanol to determine free radical scavenging activity using DPPH (2,2-diphenyl-1-picrylhydrazyl). This is one of the most widely used methods to determine the antioxidant capacity by calculating the free radical scavenging effect. DPPH solution is a dark purple colored substance. It turns transparent when the extract solutions react with the DPPH solution. The absorbance of the DPPH reaction with the antioxidant substance at 515–517 nm is measured (Brand-Williams et al. 1995). For DPPH analysis, 30 min after mixing a given amount of DPPH with sample solutions, the absorbance at 515 nm is read and calculated using the following formula:
To determine the total amount of carotenoids, the extraction method by Yanar et al. (2004) and Zheng et al. (2010) was used. Freeze-dried samples were exposed to a serial extraction by acetone; the procedure was repeated three times. The extracted samples were then centrifuged and measured using a UV spectrophotometer. A review of the available literature shows that different calculation methods are used to determine the total amount of carotenoids. In order to make the results comparable with the literature data, three most common carotenoid calculation methods were used in this s tudy: 1) carotene calculation (Car 1; Formula 1) by Oliveira et al. (2010), 2) carotene calculation (Car 2; Formula 2) by Biehler et al. (2010) and 3) carotene calculation (Car 3; Formula 3) by Lichtenthaler & Buschmann (2001). Chlorophyll
The normal distribution of data was analyzed using the Kolmogorov–Smirnov normality test (
The radical elimination effect and the total amount of carotenes in the dried and dehumidified samples of razor clams were determined and compared. The DPPH method was used on razor clam samples to study the radical elimination effect. Figure 2b shows the IC50 value and its capacity for the radical elimination effect. The better the radical elimination effect, the lower the IC50 value. The lowest IC50 value of 4.04 mg g−1 was observed in February, while the highest value ranged between 32.76 mg g−1 in June and 32.82 mg g−1 in September with inhibition (%) values ranging from 81% to 95% (Fig. 2a). The IC50 value of the DPPH radical sweeping effect varied over the months (
Different UV wavelengths were used to study the total amount of carotenoids and the chlorophyll effect. The results are presented in Table 1, which shows three different carotenoid amounts calculated by three different calculation methods. The results are presented as μg g−1. A strong correlation was found between Car 1, Car 2 and Car 3 (Table 2). The first two calculations showed that the total amount of carotenoids varied from 5.16 to 32.19 μg g−1. The total amount of carotenoids varied during the year, with the highest value in December (
Monthly variation in the total carotenoid and chlorophyll content in razor clams (μg g−1)
Car 1 | Car 2 | Car 3 | Chl- |
Chl- |
Chl- |
|
---|---|---|---|---|---|---|
May | 7.29 ± 0.64 | 7.38 ± 0.64 | 3.82 ± 0.30 | 6.77 ± 0.53 | 4.98 ± 0.42 | 11.75 |
June | 5.73 ± 0.16 | 5.80 ± 0.16 | 3.36 ± 0.22 | 4.27 ± 0.78 | 3.98 ± 0.49 | 8.25 |
July | 14.49 ± 0.64 | 14.67 ± 0.64 | 5.91 ± 0.24 | 13.62 ± 0.75 | 11.82 ± 0.88 | 25.44 |
August | 5.16 ± 0.11 | 5.22 ± 0.11 | 3.18 ± 0.11 | 3.31 ± 0.08 | 2.83 ± 0.38 | 6.14 |
September | 7.74 ± 0.25 | 7.84 ± 0.26 | 3.51 ± 0.05 | 6.88 ± 0.52 | 5.23 ± 0.15 | 12.11 |
October | 25.41 ± 0.78 | 25.73 ± 0.79 | 10.83 ± 0.27 | 25.86 ± 1.38 | 17.19 ± 1.13 | 43.05 |
November | 22.78 ± 0.99 | 23.06 ± 1.00 | 9.24 ± 1.53 | 29.12 ± 1.63 | 12.58 ± 3.26 | 41.70 |
December | 32.19 ± 1.54 | 32.59 ± 1.56 | 12.00 ± 0.90 | 39.41 ± 4.24 | 27.29 ± 3.42 | 66.71 |
January | 12.78 ± 0.28 | 12.94 ± 0.29 | 5.53 ± 0.26 | 9.97 ± 0.01 | 8.87 ± 0.14 | 18.84 |
February | 9.80 ± 0.20 | 9.92 ± 0.20 | 4.07 ± 0.39 | 8.12 ± 0.65 | 8.21 ± 1.54 | 16.33 |
March | 9.76 ± 0.11 | 9.84 ± 0.18 | 3.60 ± 0.04 | 10.54 ± 0.12 | 10.85 ± 0.15 | 21.39 |
April | 8.31 ± 0.04 | 8.47 ± 0.12 | 2.72 ± 0.34 | 9.10 ± 0.08 | 9.64 ± 0.18 | 18.74 |
Pearson's correlations for the relationship between carotenoid formula 1 (Car 1), carotenoid formula 2 (Car 2), carotenoid formula 3 (Car 3), chlorophyll
Car 1 | Car 2 | Car 3 | Chl-a | Chl-b | Chl-a+b | IC50 | Inh | |
---|---|---|---|---|---|---|---|---|
Car 1 | 1 | |||||||
Car 2 | 1.000** | |||||||
Car 3 | .953** | .952** | 1 | |||||
Chl-a | .982** | .982** | .899** | 1 | ||||
Chl-b | .929** | .930** | .789** | .949** | 1 | |||
Chl-a+b | .973** | .973** | .865** | .993** | .980** | 1 | ||
IC50 | −.142 | −.141 | −.004 | −.124 | −.294 | −.194 | 1 | |
Inh | .374 | .374 | .309 | .392 | .414 | .412 | −.427 | 1 |
Correlation is significant at the 0.01 level (2-tailed).
Correlation is significant at the 0.05 level (2-tailed).
Moreover, the amount of chlorophyll
Marine invertebrates have long been studied for their pharmacological effects or other related bioactive properties used, e.g., in the production of cosmetics, food processing etc. As natural products of marine origin have become more attractive due to their potential use in the pharmaceutical industry, it is important to redefine new sources of such products (Pachaiyappan et al. 2014). Oxidative stress caused by an imbalance between prooxidants and antioxidants has been widely recognized as the main cause of chronic diseases (Urquiaga & Leighton 2000). As a result of potential cell and tissue damage caused by ROS, marine and other organisms compensate for the production of these radicals using a variety of cellular defensive mechanisms (Correia et al. 2003).
Therefore, antioxidants are very important due to their positive effects in the treatment of atherosclerosis, numerous types of cancer, cardiovascular diseases and in the anti-ageing therapy. Studies showed that the mollusk species
The IC50 (mg g−1) value is a value that measures the effect of antioxidant capacity by the DPPH radical sweeping effect. The lowest IC50 value was found in February, which was 4.04 mg g−1 and had the highest radical sweeping effect. The highest IC50 value, i.e. 32.82 mg g−1, was recorded in September, which indicates the lowest radical sweeping effect.
The lowest antioxidant capacity was observed in May, June, August, September and October. It can therefore be concluded that the low level of radical antioxidants in these months is due to seasonal changes as well as quality and quantity of food. The fact that IC50 decreased particularly after October shows an increase in radical antioxidants. Inhibition (%) is a value that measures the strength of antioxidant capacity by the DPPH radical sweeping effect. High inhibition (%) suggests that the radical sweeping effect is effective. In this sense, the highest inhibition value of 93.51% in March and the lowest IC50 value of 92.29% in February appear to be similar. The availability of food is an important factor for energy reserve and gametogenesis (Acarli et al. 2018a). Lipids and carbohydrates are used as the main energy sources in the reproduction cycle of bivalve species (Dridi et al. 2007; Pogoda et al. 2013; Acarli et al. 2018b). The spawning period of
Mollusca species, especially bivalves, are preferred by consumers because of their taste and for being a healthy source of energy. Depending on the quality of bivalves, the consumer also decides on the time of consumption. The optimum harvest time in aquaculture systems or wild stock is determined on the basis of meat yield, the gonadosomatic index or nutritional quality. In this study, the radical antioxidant capacity and the amount of carotenoids in