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<article article-type="research-article" dtd-version="3.0" xml:lang="en" xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink">
	<front>
		<journal-meta>
			<journal-id journal-id-type="publisher-id">SCIENTIA MARINA</journal-id>
			<journal-title-group>
				<journal-title>Scientia Marina</journal-title>
				<abbrev-journal-title>Sci Mar</abbrev-journal-title>
			</journal-title-group>
			<issn pub-type="epub">0214-8358</issn>
			<publisher>
				<publisher-name>Consejo Superior de Investigaciones Científicas</publisher-name>
			</publisher>
		</journal-meta>
		<article-meta>
			 <article-id pub-id-type="publisher-id">sm4202</article-id>
			 <article-id pub-id-type="doi">10.3989/scimar.04202.16A</article-id>
			 
			
		<title-group>
			  <article-title>Seasonal variation in reproductive activity and biochemical composition of flat oyster (<italic>Ostrea edulis</italic>) in the Homa Lagoon, Izmir Bay, Turkey</article-title>
		<trans-title-group xml:lang="es">
		<trans-title>Variación estacional de la actividad reproductiva y de la composición bioquímica de ostra plana (<italic>Ostrea edulis</italic>) en Homa Lagoon, bahía de Izmir, Turquía</trans-title>
		</trans-title-group>
		<alt-title alt-title-type="running-head"></alt-title>
		</title-group>
		
		<contrib-group>
			  <contrib contrib-type="author" corresp="yes"> 
				<name>
				 <surname> Acarli</surname>
				 <given-names>Sefa</given-names>
				</name>
				<xref ref-type="aff" rid="U1"/>
				<xref ref-type="corresp" rid="cor1"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Lök</surname>
				 <given-names>Aynur</given-names>
				</name>
				<xref ref-type="aff" rid="U2"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Kirtik</surname>
				 <given-names>Ali</given-names>
				</name>
				<xref ref-type="aff" rid="U2"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Acarli</surname>
				 <given-names>Deniz</given-names>
				</name>
				<xref ref-type="aff" rid="U3"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Serdar</surname>
				 <given-names>Serpil</given-names>
				</name>
				<xref ref-type="aff" rid="U2"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Kucukdermenci</surname>
				 <given-names>Aysun</given-names>
				</name>
				<xref ref-type="aff" rid="U2"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Yigitkurt</surname>
				 <given-names>Selcuk</given-names>
				</name>
				<xref ref-type="aff" rid="U2"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Yildiz</surname>
				 <given-names>Harun</given-names>
				</name>
				<xref ref-type="aff" rid="U1"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Saltan</surname>
				 <given-names>Asiye Nur </given-names>
				</name>
				<xref ref-type="aff" rid="U1"/>
			  </contrib>
			  <aff id="U1">Canakkale Onsekiz Mart University, Faculty of Marine Sciences and Technology, Terzioglu Campus 17100 Canakkale, Turkey.</aff>
			  <aff id="U2">Ege University, Fisheries Faculty, Department of Aquaculture, Bornova, 35100, Izmir, Turkey.</aff>
			  <aff id="U3">Canakkale Onsekiz Mart University, Gökceada School of Applied Sciences, Department of Fisheries Technology, 17760 Canakkale, Turkey.</aff>
			 </contrib-group>
			 
			 <author-notes>
		<corresp id="cor1">e-mail: <email xlink:href="sefaacarli@comu.edu.tr">sefaacarli@comu.edu.tr</email>
		</corresp>
		</author-notes>
		
<pub-date pub-type="epub">
		<day>30</day>
		<month>12</month>
		<year>2015</year>
		</pub-date>
		<pub-date pub-type="collection">
		<year>2015</year>
		</pub-date>
		
		<volume>79</volume>
		<issue>4</issue>
		<fpage>487</fpage>
		<lpage>495</lpage>
		
		<elocation-id content-type="doi">10.3989/scimar.04202.16A</elocation-id>

		 <history>
		  	<date date-type="received">
				<day>7</day>
				<month>1</month>
				<year>2015</year>
			</date>
			<date date-type="accepted">
				<day>22</day>
				<month>7</month>
				<year>2015</year>
			</date>
			<date date-type="published">
				<day>16</day>
				<month>10</month>
				<year>2015</year>
			</date>
		 </history>
		 
		<permissions>
		<copyright-statement>&#x00A9; 2015 CSIC</copyright-statement>
		<copyright-year>2015</copyright-year>
		<license license-type="open-access" xlink:href="http://creativecommons.org/licenses/by-nc/3.0/">
		<license-p>This is an open-access article distributed under the Creative Commons Attribution-Non Commercial Lisence (by-nc) Spain 3.0.</license-p>
		</license>
		</permissions>
		
		<abstract xml:lang="en">
		<title>SUMMARY</title>
		<p>The reproductive cycle of the flat oyster, <italic>Ostrea edulis</italic><italic> Linnaeus, 1758</italic>, in Homa Lagoon, Izmir Bay, Turkey was examined from August 2008 to July 2009. Gonad samples were analysed histologically in order to determine the sex ratio and gonad development stage. Overall, the sex ratio was recorded as 2.2% female, 42.6% male, 37% hermaphrodite and 17.9% inactive. Glycogen content showed considerable variations between August and February, but decreased gradually thereafter. However, glycogen did not directly affect the reproductive cycle. Total lipid content was positively correlated with temperature and inversely correlated with salinity. In addition, this parameter was influenced by the reproductive activity, which is correlated with the fluctuation of the condition index and gonad index (P&lt;0.05). However, the relationship between the protein index and the gonad index was negative (P&lt;0.05). The results of this study showed that protein was the major energy resource. The condition index varied between 2.69±0.91 (February) and 12.29±1.45 (April) during the year. With respect to meat yield, oyster quality changed from “fine” to “special”, except in December and February. </p>
		</abstract>
		<trans-abstract xml:lang="es">
		<title>RESUMEN</title>
		<p>El ciclo reproductivo de la ostra plana, <italic>Ostrea edulis </italic>Linnaeus, 1758, en Homa Lagoon, Bahía de Izmir, Turquía, fue examinado entre agosto de 2008 y julio de 2009. Las gónadas se analizaron histológicamente para determinar la proporción de sexos y su estado de desarrollo. La proporción de sexos encontrada fue 2.2% hembras, 42.6% machos, 37% hermafroditas y 17.9% inactivos. El contenido de glucógeno mostró considerables variaciones entre agosto y febrero, pero después de estos meses se produjo un aumento gradual. Sin embargo el glucógeno no afectó directamente el ciclo reproductivo. El contenido total de lípidos se correlacionó positivamente con la temperatura e inversamente con la salinidad. Además, este parámetro estuvo influenciado por la actividad reproductiva, que se correlaciona con la fluctuación del índice de condición y del índice gonadal (P&lt;0,05). Sin embargo la relación entre el índice de proteína y el índice gonadal fue negativa (P&lt;0,05). Los resultados de este estudio mostraron que la proteína era la principal fuente de energía. El índice de condición varió entre 2.69±0.91 (febrero) y 12.29±1.45 (abril) durante el año. En lo que respecta a la producción de carne, la calidad de las ostras pasó de “fine” to “special”, excepto en diciembre y febrero.<br /><br /><strong>Palabras clave</strong>: ostra plana; <italic>Ostrea edulis</italic>; ciclo reproductivo; composición bioquímica; mar Egeo; Homa Lagoon.</p>
		</trans-abstract>
		<kwd-group xml:lang="en">
			<title>KEYWORDS</title>
			<kwd>flat oyster</kwd>
			<kwd><italic>Ostrea edulis</italic></kwd>
			<kwd>reproductive cycle</kwd>
			<kwd>biochemical composition</kwd>
			<kwd>Aegean Sea</kwd>
			<kwd>Homa Lagoon</kwd>			
		</kwd-group>
		<kwd-group xml:lang="es">
			<title>PALABRAS CLAVE</title>
			<kwd>ostra plana</kwd>
			<kwd><italic>Ostrea edulis</italic></kwd>
			<kwd>ciclo reproductivo</kwd>
			<kwd>composición bioquímica</kwd>
			<kwd>mar Egeo</kwd>
			<kwd>Homa Lagoon</kwd>
		</kwd-group>
	 </article-meta>
	</front>
	<body>
<sec id="S1">
<title>INTRODUCTION</title>
			
			<p>Oysters are the most common of all bivalves and they have been known as edible and as a delicacy for centuries. World oyster production was estimated at around 4.6 million metric tons in 2010 with a value of $3.7 billion (<xref ref-type="bibr" rid="CIT25">FAO 2012</xref>). Shellfish cultivation is not a common practice in Turkey and only one species (<italic>Mytilus gallopravincialis</italic>) is farmed. Oysters are traditionally harvested from wild stocks for human consumption and for export (<xref ref-type="bibr" rid="CIT34">Kumlu and Lok 2007</xref>). Turkey has an enormous potential for aquaculture development due to its geo-formations, with numerous sheltered bays and estuaries and the occurrence of important economic bivalve species such as the European flat oyster <italic>Ostrea edulis</italic> (<xref ref-type="bibr" rid="CIT26">Fischer et al. 1987</xref>) and the Pacific oyster <italic>Crassostrea gigas</italic> (<xref ref-type="bibr" rid="CIT19">Doğan et al. 2005</xref>). </p>
			<p>Homa Lagoon is a suitable lagoon for oyster aquaculture. The tidal effects and the availability of food make this lagoon one of the ten most productive lagoons in the Aegean Sea. It has large areas of salt wetlands, with a fishing area of 1800 ha whose natural population includes important commercial bivalves such as <italic>O. edulis, Ruditapes decussatus</italic> and <italic>Cerastoderma glaucum</italic>. </p>
			<p>Knowledge of the reproductive cycle of <italic>O. edulis</italic> provides essential information for aquaculture production. In addition, knowledge of meat yield (MY) and biochemical composition will be important for marketing. It is known that the reproductive cycle, MY, condition index (CI) and biochemical composition of bivalves depends essentially on water temperature (<xref ref-type="bibr" rid="CIT012">Chávez-Villalba et al. 2003</xref>, <xref ref-type="bibr" rid="CIT64">Wilson et al. 2005</xref>, <xref ref-type="bibr" rid="CIT40">Lok and Acarli 2006</xref>) and the quantity and quality of food in the water column (<xref ref-type="bibr" rid="CIT02">Abad et al. 1995</xref>, <xref ref-type="bibr" rid="CIT67">Yıldız et al. 2013</xref>). A significant relationship exists especially between the reproductive cycle, the CI and biochemical composition (<xref ref-type="bibr" rid="CIT06">Berthelin et al. 2000</xref>, <xref ref-type="bibr" rid="CIT65">Yan et al. 2010</xref>, <xref ref-type="bibr" rid="CIT15">Çelik et al. 2015</xref>). Biochemical components are used for growth and as energy reserves for reproductive activity. For gametogenesis the energy is generally stored in the form of glycogen, but when food is abundant, lipids and proteins may also serve as an energy source. The particular importance of these substrates can vary among bivalve species and among populations of the same species who have different strategies for energy storage and utilization (<xref ref-type="bibr" rid="CIT52">Pogoda et al. 2013</xref>, <xref ref-type="bibr" rid="CIT44">Matias et al. 2013</xref>).</p>
			<p>There are no studies on the reproductive cycle and biochemical composition of the flat oyster in Homa Lagoon. Therefore, the aim of this study was to determine the spawning period, MY, CI and biochemical composition of this species in Homa Lagoon.</p>
			
	</sec>
<sec id="S2">
<title>MATERIALS AND METHODS</title>
			
<sec id="S2.1">
<title>Sample collection</title>
			
		  <p>In May 2008, oyster samples (360 individuals) larger than 50 mm were collected in Gerence Bay (38°25’N; 26°30’E), Aegean Sea, at 1-5 m depth by scuba diving and the samples were transferred to Homa Lagoon (38°31’30”N; 026°50’50”E), Aegean Sea. The individuals were placed in mesh bags (20 mm mesh size) that were hung on a longline culture system on the surface, which was set up in a canal (1.5 m maximum depth) between the lagoon and the sea area (<xref ref-type="fig" rid="F1">Fig. 1</xref>). Thirty adult oysters were randomly taken monthly from August 2008 to July 2009. During each sampling, oysters were cleaned of fouling organisms and weighed to the nearest 0.01 g using an electronic scale. </p>
		  			<fig id="F1">
				<label>Fig. 1</label>
				<caption>
				<title>Location of the study area (full square) in Homa Lagoon, Izmir Bay, Turkey.</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm79n4-4202-web-resources/image/sm4202fig1_fmt.jpeg"/>
			</fig>	
</sec>
<sec id="S2.2">
<title>Environmental parameters</title>
			
		  <p>Hydrographical parameters such as temperature, salinity, chlorophyll <italic>a</italic>, particulate organic matter (POM) and particulate inorganic matter (PIM) were measured during the study. Water temperature was monitored with a temperature recorder (Star-Oddi) at six hour intervals. Salinity was measured with a light refractometer (±1‰). Chlorophyll <italic>a</italic>, POM, PIM and total particulate matter were determined according to the methods of <xref ref-type="bibr" rid="CIT60">Strickland and Parson (1972)</xref>. All of the measurements for determining environmental parameters, except temperature, were taken from the water surface at intervals of two weeks, and twice on each day.</p>
			
		</sec>
<sec id="S2.3">
<title>Meat yield and condition index</title>
			
		  <p>Thirty specimens were processed monthly for analysis of the CI and MY. The MY, or AFNOR quality index, of oysters was calculated following the method of <xref ref-type="bibr" rid="CIT14">Crosby and Gale (1990)</xref>:</p>
			
		  <p align="center">MY = [wet meat weight (g)/total weight (g)] × 100</p>
			
			<p>An index between 6.5 and 9 corresponds to “fine” oysters and greater than 9 to “spéciale” oysters (<xref ref-type="bibr" rid="CIT58">Soletchnik et al. 2001</xref>). The CI was calculated according to <xref ref-type="bibr" rid="CIT62">Walne and Mann (1975)</xref>:</p>
			
		  <p align="center">CI = [dry meat weight (g)/dry shell weight (g)] × 100</p>
			
	</sec>
<sec id="S2.4">
<title>Biochemical analysis</title>
			
		  <p>Thirty individuals for each month were freeze-dried and crushed for biochemical analysis, and the samples were analysed in triplicate. Protein content (%) was determined, according to <xref ref-type="bibr" rid="CIT41">Lowry et al. (1951)</xref>, after extraction with sodium hydroxide. Total lipid (%) was extracted with chloroform-methanol (<xref ref-type="bibr" rid="CIT07">Bligh et al. 1959</xref>). Glucide (%) and glycogen content (%) (precipitated with absolute ethanol) were analysed using the method of phenol-sulfuric acid, according to <xref ref-type="bibr" rid="CIT21">Dubois et al. (1956)</xref>. </p>
			
		</sec>
<sec id="S2.5">
<title>Histology</title>
			
		  <p>In order to observe the gonadal development, gonad tissue of 30 individuals for each month was fixed in Davidson solution. Samples were preserved in 10% formalin solution. The tissues from each sample were dehydrated and prepared for paraffin embedding. Embedded tissues of 4 µm thickness were sectioned. Sections were mounted on glass slides and stained with a solution of haematoxylin and eosin. Each histological section of gonadal tissue was observed in detail under a microscope (BX51 4×, 10×, 20×, 40×) to assess sex and to categorized the stage of gametogenesis, which was identified according to the descriptions given by <xref ref-type="bibr" rid="CIT57">Siddiqui and Ahmed (2002)</xref>; the stages are classified as inactive, early developing, developing, ripe, partly spawned and fully spawned. </p>
			
	</sec>
<sec id="S2.6">
<title>Gonad index</title>
			
		  <p>A gonad index (GI) was calculated according to <xref ref-type="bibr" rid="CIT59">Soria et al. (2002)</xref> as follows:</p>
			
		  <p align="center">GI = (sum of individuals *category)/total individuals</p>
			
		  <p>For each stage a numeric ranking (category) was assigned as follows:</p>
			<blockquote>
			  <p>- inactive (S0): 1<br/>
			    - early developing (S1): 2 <br/>
			    - developing (S2): 2<br/>
			    - ripe (S3): 3<br/>
			    - partly spawning (S4): 3<br/>
			    - fully spawning (S5): 1</p>
		  </blockquote>
</sec>
<sec id="S2.7">
<title>Data analysis</title>
			
		  <p>Percentage data was arcsine transformed before statistical treatment. Sex ratio was analysed using chi-square (χ<sup>2</sup>). The data distribution was tested using the Kolmogorov-Smirnov test to determine normality. Pearson’s correlation analysis was applied to describe the relationship between environmental factors (temperature, salinity, POM, PIM and chlorophyll <italic>a</italic>), MY, CI, GI and biochemical composition. Data were analysed and statistical analyses were carried out using the SPSS 13.0 software for Windows.</p>
			</sec>
		</sec>
<sec id="S3">
<title>RESULTS</title>
			
<sec id="S3.1">
<title>Environmental parameters</title>
			
		  <p>The mean monthly variations in sea water temperature, salinity, chlorophyll <italic>a</italic>, POM and PIM values for the Homa Lagoon for each month are given in <xref ref-type="fig" rid="F2">Figure 2</xref>. Temperature showed a clear seasonal pattern with maximum values in August of 26.3±1.54°C and minimum values in January of 9.8±3.15°C. The salinity ranged between 36.2±1.1 and 44.92±0.92. Chlorophyll a was variable throughout the year with a concentration ranging from 9.04±5.36 µg L<sup>–1</sup> in October to 1.9±1.14 µg L<sup>–1</sup> in June. A strong correlation was observed between PIM and POM (P&lt;0.01). Low values of PIM and POM were recorded as 4.85±1.74 and 2.12±1.41 mg L<sup>–1</sup> in March, respectively. Two peaks of PIM and POM were determined as 113±26.57 mg L<sup>–1</sup>; 61.53±7.57 mg L<sup>–1</sup> and 112.68±19.07 mg L<sup>–1</sup>; 63.18±8.57 mg L<sup>–1</sup> in August and November, respectively. No significant relationship was found between CI or MY and the environmental parameters.</p>
		  			<fig id="F2">
				<label>Fig. 2</label>
				<caption>
				<title>Mean monthly variation of seawater temperature (a), salinity (b), chlorophyll <italic>a</italic> (b), particulate inorganic matter (PIM) (c) and particulate organic matter (POM) (c) in Homa Lagoon from August 2008 to July 2009.</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm79n4-4202-web-resources/image/sm4202fig2_fmt.jpeg"/>
			</fig>

</sec>
<sec id="S3.2">
<title>Meat yield and condition index</title>
			
		  <p>Monthly variations in the MY and CI of <italic>O. edulis</italic> are shown in <xref ref-type="table" rid="T1">Table 1</xref>. These two parameters are positively correlated (P&lt;0.01) and the lowest values were observed in December and February. After this month, the MY and the CI increased until April, when the highest values were recorded: 20.42±3.42% and 12.29±1.45, respectively (<xref ref-type="table" rid="T1">Table 1</xref>). CI and MY were not correlated with any of the environmental parameters. During the experimental period, the oyster quality changed from fine to “spéciale”. </p>
		  	<table-wrap id="T1">
			<label>Table 1</label>
		<caption>
			<title>Monthly variation (mean±SD) meat yield, condition index, protein, total lipids, and glycogen in <italic>Ostrea edulis</italic> from August 2008 to July 2009.</title>
		</caption>
		<table frame="hsides" rules="groups">
  <thead>
		        <tr>
		          <th>Month </th>
		          <th>Meat yield (%)</th>
		          <th>Condition index</th>
		          <th>Protein (%)</th>
		          <th>Total lipids (%)</th>
		          <th>Glycogen (%)</th>
	            </tr>
	          </thead>
		      <tbody>
		        <tr>
		          <td> August </td>
		          <td>8.28±1.42</td>
		          <td>6.35±1.01</td>
		          <td>43.38±1.89</td>
		          <td>6.27±0.97</td>
		          <td>17.08±2.21</td>
	            </tr>
		        <tr>
		          <td>September</td>
		          <td>6.93±1.12</td>
		          <td>4.73±0.79</td>
		          <td>46.37±1.25</td>
		          <td>5.15±0.82</td>
		          <td>16.15±1.75</td>
	            </tr>
		        <tr>
		          <td>October</td>
		          <td>8.37±2.52</td>
		          <td>5.23±1.14</td>
		          <td>44.07±2.41</td>
		          <td>5.60.±0.92</td>
		          <td>29.39±2.19</td>
	            </tr>
		        <tr>
		          <td>November</td>
		          <td>9.63±2.85</td>
		          <td>8.72±1.12</td>
		          <td>45.77±1.12</td>
		          <td>5.10±0.94</td>
		          <td>6.30±1.27</td>
	            </tr>
		        <tr>
		          <td>December</td>
		          <td>5.8±1.72</td>
		          <td>3.84±0.77</td>
		          <td>50.35±2.12</td>
		          <td>3.34±0.67</td>
		          <td>12.65±2.25</td>
	            </tr>
		        <tr>
		          <td>January</td>
		          <td>14.74±1.68</td>
		          <td>7.88±1.24</td>
		          <td>44.49±0.56</td>
		          <td>5.58±1.11</td>
		          <td>6.97±1.75</td>
	            </tr>
		        <tr>
		          <td>February</td>
		          <td>5.21±0.65</td>
		          <td>2.69±0.91</td>
		          <td>50.56±1.11</td>
		          <td>4.39±0.82</td>
		          <td>2.26±0.25</td>
	            </tr>
		        <tr>
		          <td>March</td>
		          <td>13.17±2.1</td>
		          <td>7.75±1.53</td>
		          <td>38.97±1.32</td>
		          <td>4.69±1.45</td>
		          <td>3.75±1.07</td>
	            </tr>
		        <tr>
		          <td>April</td>
		          <td>20.42±3.42</td>
		          <td>12.29±1.45</td>
		          <td>42.39±1.14</td>
		          <td>6.15±1.01</td>
		          <td>13.21±2.1</td>
	            </tr>
		        <tr>
		          <td>May</td>
		          <td>9.96±1.14</td>
		          <td>6.39±0.88</td>
		          <td>43.91±0.89</td>
		          <td>6.52±1.25</td>
		          <td>18.80±1.33</td>
	            </tr>
		        <tr>
		          <td>June</td>
		          <td>10.15±2.2</td>
		          <td>9.62±1.76</td>
		          <td>47.50±2.82</td>
		          <td>6.13±0.88</td>
		          <td>25.39±2.99</td>
	            </tr>
		        <tr>
		          <td>July</td>
		          <td>7.97±1.12</td>
		          <td>10.16±1.3</td>
		          <td>37.97±1.06</td>
		          <td>6.14±1.12</td>
		          <td> 28.26±1.71 </td>
	            </tr>
	          </tbody>
	        </table>
	      </table-wrap>
</sec>
<sec id="S3.3">
<title>Biochemical analysis</title>
			
		  <p>Monthly variations in the protein, total lipid and glycogen content are shown in <xref ref-type="table" rid="T1">Table 1</xref>. Protein content varied during the study period, with the minimum value being determined in July (37.97±1.06%) and the maximum value in February (50.56±1.11%). This parameter was negatively correlated with CI and GI (P&lt;0.05). Total lipids and CI decreased until December, when the value was 3.34±0.67%, the lowest value of the year. Then the total lipid value increased significantly in January, when oysters had the highest proportion of individuals in the ripe and partly spawning stages. This parameter was correlated positively with CI, GI and seawater temperature and inversely with salinity (P&lt;0.05). However, the total lipid value sharply decreased one month later. At the same time, CI showed the lowest value of the year in February. These dramatic fluctuations changed in April and reached a constant rate until the end of the study (July). Glycogen value peaked in October at 29.39±2.19%, but decreased drastically after this month and reached a minimum value in February. No correlations were observed between glycogen values and other parameters (P&gt;0.05). </p>
			
			</sec>
<sec id="S3.4">
<title>Histology</title>
			
		  <p>A total of 360 individuals were studied, with mean proportions of 2.2% female, 42.6% male, 37% hermaphrodite and 17.9% inactive (<xref ref-type="fig" rid="F3">Fig. 3</xref>). However, the sex ratio varied significantly during the study period (P&lt;0.05). Female individuals were observed only in August and May, whereas males were dominant throughout the study period and hermaphrodites were observed in each month. The highest percentage of individuals in the inactive stage was recorded in December and February, but inactive individuals were not observed in January March, April and July. The annual reproductive cycle of the flat oyster is summarized in <xref ref-type="fig" rid="F4">Figure 4</xref>. The gonad development showed that gametogenesis occurred throughout the year. The highest percentage of individuals in the inactive stage occurred in December. The early developing stage for males was 16% in September. Partly spawning males were observed throughout the experimental period, except in October, December and February, and maximum values were observed in September and January (<xref ref-type="fig" rid="F5">Fig. 5</xref>). Developing and fully spawning females were not observed during the study. In August, half of the population was in the ripe stage and the other half was in the partial spawning stage. A comparison of different sex categories indicated that, in general, the population was 46% female-dominant hermaphrodites. Ambisexual and predominantly male individuals had the same proportion (<xref ref-type="fig" rid="F6">Fig. 6</xref>). Predominantly female individuals were found throughout the study period (except in December), with a maximum percentage (80%) in May. The highest percentage of the ambisexual phase was observed as 100% in December. In this month, all hermaphroditic individuals were ambisexual. The highest percentage of males in the ripe stage and partly spawning hermaphrodite individuals was observed in January (45%) and October (100%), respectively (<xref ref-type="fig" rid="F7">Fig. 7</xref>). In February, female hermaphrodite individuals were all in the developing stage (100%). In August, most gonads (80%) were in the partly spawned stage and some (20%) were in the fully spawned stage. Spawning was observed throughout the year, except in September, December and February. Female hermaphrodite gonad development began in October and reached the maximum percentage in February. The ripe stage was detected in the short term and the greatest percentage was seen in September. Spawning was observed in either male or female individuals almost all of the year. The highest percentages of the spawning stage were observed in August and September. The GI varied between 1.2 and 2.6 (<xref ref-type="fig" rid="F8">Fig. 8</xref>). The highest values were found in November (2.1), January (2.64) and March (2.28), as a result of a higher number of mature and partly spawning individuals; male and hermaphrodite male individuals were dominant. Minimal values were determined in December and February, when most of the individuals were at the inactive stage. The GI was positively correlated with total lipid value and inversely correlated with protein content, but not with glycogen (P&lt;0.05) (<xref ref-type="table" rid="T2">Table 2</xref>).</p>
		  
		 			<fig id="F3">
				<label>Fig. 3</label>
				<caption>
				<title>Monthly variations in the sex ratio of <italic>Ostrea edulis</italic> from August 2008 to July 2009.</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm79n4-4202-web-resources/image/sm4202fig3_fmt.jpeg"/>
			</fig>
 			<fig id="F4">
				<label>Fig. 4</label>
				<caption>
				<title>Percentage of different stages in total population of <italic>Ostrea edulis</italic> from August 2008 to July 2009 (inactive (S0), early developing (S1), developing (S2), ripe (S3), partly spawned (S4) and fully spawned (S5)).</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm79n4-4202-web-resources/image/sm4202fig4_fmt.jpeg"/>
			</fig>
			<fig id="F5">
				<label>Fig. 5</label>
				<caption>
				<title>Percentage of different stages in male (a) and female (b) of <italic>Ostrea edulis</italic> from August to July (early developing (S1), developing (S2), ripe (S3), partly spawned (S4) and fully spawned (S5)).</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm79n4-4202-web-resources/image/sm4202fig5_fmt.jpeg"/>
			</fig>
			<fig id="F6">
				<label>Fig. 6</label>
				<caption>
				<title>Monthly variations in predominantly female, predominantly male and ambisexual in hermaphrodite individuals from August 2008 to July 2009.</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm79n4-4202-web-resources/image/sm4202fig6_fmt.jpeg"/>
			</fig>
			<fig id="F7">
				<label>Fig. 7</label>
				<caption>
				<title>Percentage of different stages in male hermaphrodite (MH) and female hermaphrodite (FH) of <italic>Ostrea edulis</italic> from August to July (early developing (S1), developing (S2), ripe (S3), partly spawned (S4) and fully spawned (S5)).</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm79n4-4202-web-resources/image/sm4202fig7_fmt.jpeg"/>
			</fig>

			<fig id="F8">
				<label>Fig. 8</label>
				<caption>
				<title>Variation of gonad index (GI) in <italic>Ostrea edulis</italic> from August 2008 to July 2009.</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm79n4-4202-web-resources/image/sm4202fig8_fmt.jpeg"/>
			</fig>
		  	<table-wrap id="T2">
			<label>Table 2</label>
		<caption>
			<title>Matrix of Pearson correlation of temperature (T), salinity (S), particulate inorganic matter (PIM), particulate organic matter (POM), chlorophyll <italic>a</italic> (CHL), meat yield (MY), condition index (CI), gonad index (GI), protein (P), total lipids (L) and glycogen (G). * Correlation is significant at the 0.05 level (two-tailed); ** Correlation is significant at the 0.01 level (two-tailed).</title>
		</caption>
		<table frame="hsides" rules="groups">
  <thead>
					<tr>
						<th>
						</th>
						<th>T</th>
						<th>S</th>
						<th>PIM</th>
						<th>POM</th>
						<th>CHL</th>
						<th>MY</th>
						<th>CI</th>
						<th>GI</th>
						<th>P</th>
						<th>L</th>
						<th>G</th>
					</tr>
 </thead>
				<tbody>
					<tr>
						<td>
							T
						</td>
						<td>1</td>
						<td>–0.073</td>
						<td>0.511</td>
						<td>0.301</td>
						<td>–0.163</td>
						<td>–0.163</td>
						<td>0.270</td>
						<td>0.327</td>
						<td>–0.388</td>
						<td>0.685*</td>
						<td>
							0.575
						</td>
					</tr>
					<tr>
						<td>S</td>
					  <td>
							
					  </td>
						<td>1</td>
						<td>0.056</td>
						<td>0.073</td>
						<td>0.060</td>
						<td>–0.446</td>
						<td>–0.166</td>
						<td>–0.476</td>
						<td>0.187</td>
						<td>–0.641*</td>
						<td>
							0.166
						</td>
					</tr>
					<tr>
						<td>PIM</td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
						<td>1</td>
						<td>0.934**</td>
						<td>0.342</td>
						<td>–0.173</td>
						<td>0.132</td>
						<td>0.117</td>
						<td>–0.062</td>
						<td>0.373</td>
						<td>0.383</td>
					</tr>
					<tr>
						<td>POM</td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
						<td>1</td>
						<td>0.325</td>
						<td>–0.214</td>
						<td>–0.095</td>
						<td>–0.046</td>
						<td>0.062</td>
						<td>0.163</td>
						<td>0.298</td>
					</tr>
					<tr>
						<td>CHL</td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
						<td>1</td>
						<td>0.097</td>
						<td>0.064</td>
						<td>0.119</td>
						<td>–0.226</td>
						<td>0.066</td>
						<td>
							0.397
						</td>
					</tr>
					<tr>
						<td>MY</td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
						<td>1</td>
						<td>0.757**</td>
						<td>0.392</td>
						<td>–0.458</td>
						<td>0.392</td>
						<td>
							–0.147
						</td>
					</tr>
					<tr>
						<td>CI</td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
						<td>1</td>
						<td>0.567</td>
						<td>–0.614*</td>
						<td>0.585*</td>
						<td>
							–0.022
						</td>
					</tr>
					<tr>
						<td>GI</td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
						<td>1</td>
						<td>–0.612*</td>
						<td>0.606*</td>
						<td>
							–0.122
						</td>
					</tr>
					<tr>
						<td>P</td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
						<td>1</td>
						<td>–0.530</td>
						<td>
							–0.130
						</td>
					</tr>
					<tr>
						<td>L</td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
						<td>1</td>
						<td>
							0.345
						</td>
					</tr>
					<tr>
						<td>G</td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
					  <td>
							
					  </td>
						<td>1</td>
					</tr>
				</tbody>
	</table>
	</table-wrap>
</sec></sec>
<sec id="S4">
<title>DISCUSSION</title>
			
		  <p>The CI, a measure of apparent health and commercial quality of bivalves (<xref ref-type="bibr" rid="CIT49">Orban et al. 2002</xref>), is a parameter of ecophysiological and economic importance, especially with regard to industrial processing. According to <xref ref-type="bibr" rid="CIT48">Okumus et al. (1998)</xref>, fluctuations in the CI and MY have important implications for cultivation and harvesting strategy. Meat quality and biochemical composition in bivalves primarily depends on food, environmental parameters (mainly temperature) (<xref ref-type="bibr" rid="CIT08">Brown and Hartwick 1988</xref>, <xref ref-type="bibr" rid="CIT03">Austin et al. 1993</xref>, <xref ref-type="bibr" rid="CIT24">Fabioux et al. 2005</xref>) and reproductive activities (<xref ref-type="bibr" rid="CIT13">Chávez-Villalba et al. 2007</xref>). In this study, MY and CI ranged from 2.69% to 12.29% and from 5.21% to 20.42%, respectively. Meat yield and CI of <italic>O. edulis</italic> in the present study was similar to the values reported for the same species by <xref ref-type="bibr" rid="CIT01">Acarli et al. (2011)</xref> and <xref ref-type="bibr" rid="CIT66">Yıldız et al. (2011)</xref> in Turkey and by <xref ref-type="bibr" rid="CIT51">Pogoda et al. (2011)</xref> in Germany. Based on the AFNOR index for MY values recorded in this study, the oysters could be ranked as “spéciale” according to the classifications given by <xref ref-type="bibr" rid="CIT58">Soletchnik et al. (2001)</xref>. In this study, higher values than those of <italic>Crassostrea gigas </italic>in Tunisia (<xref ref-type="bibr" rid="CIT20">Dridi et al. 2007</xref>), in France (<xref ref-type="bibr" rid="CIT58">Soletchnik et al. 2001</xref>) and in Germany (<xref ref-type="bibr" rid="CIT51">Pogoda et al. 2011</xref>) were found, showing that this population has good quality for consumption nearly throughout the year. </p>
			<p>The gametogenic cycle of bivalve species is affected by endogenous rhythms such as energy reserves, hormonal cycles and genotype (<xref ref-type="bibr" rid="CIT29">Gaspar et al. 1999</xref>, <xref ref-type="bibr" rid="CIT42">Lucas and Southgate 2003</xref>), and y exogenous factors such as food availability, temperature, photoperiod and salinity (<xref ref-type="bibr" rid="CIT33">Kennedy 1983</xref>, <xref ref-type="bibr" rid="CIT47">Newell et al. 1982</xref>, <xref ref-type="bibr" rid="CIT35">Jeffs et al. 2002</xref>). Temperature is an important environmental parameter in the regulation of gametogenesis in oysters (<xref ref-type="bibr" rid="CIT11">Chávez-Villalba et al. 2002</xref>, <xref ref-type="bibr" rid="CIT31">Helm et al. 2004</xref>, <xref ref-type="bibr" rid="CIT16">da Silva et al. 2009</xref>), but the onset of gametogenesis in <italic>O. edulis</italic> occurs at different temperatures and depends on location (<xref ref-type="bibr" rid="CIT56">Shpigel 1989</xref>). In our study, gonad development was constant throughout the year, except for a decrease in December and February, when the temperature was recorded as 10°C. However, the highest value of the GI was recorded during low temperatures (February 9°C). This situation can be explained by the fact that most of the individuals in the population were males, which were faster than females to complete the reproductive process. Indeed, the water temperature in the Homa Lagoon did not limit the reproduction of the flat oyster. The same results have been reported by <xref ref-type="bibr" rid="CIT56">Shpigel (1989)</xref> for the Gulf of Eilat (Israel), <xref ref-type="bibr" rid="CIT55">Ruiz (1992)</xref> for Galicia (Spain), <xref ref-type="bibr" rid="CIT09">Cano et al. (1997)</xref> for Mar Menor (Spain) and <xref ref-type="bibr" rid="CIT10">Carlucci et al. (2010)</xref> for the Taranto Sea (Italy).</p>
			<p>Besides temperature, food availability is also affecting broodstock energy reserves and gametogenesis in bivalves (<xref ref-type="bibr" rid="CIT04">Baghurst and Mitchell 2002</xref>, <xref ref-type="bibr" rid="CIT28">Frias and Segovia 2009</xref>, <xref ref-type="bibr" rid="CIT27">Fourniera et al. 2012</xref>). In this investigation, chlorophyll a and organic matter amounts were recorded as very high in the Homa Lagoon and levels are probably sufficient for the onset of gametogenesis and gonad development throughout the year. Food amounts in the study area are continuously enhanced due to the input of nutrition from the open sea. The improved nutrient availability in the lagoon can be attributed to the inflow from the sea water environment, as well as the shallow lagoon bed which leads to an increase in chlorophyll <italic>a</italic> as a plankton biomass indicator. Chlorophyll <italic>a</italic> and organic matter levels showed no correlation with gametogenesis because food quality was always high. Nevertheless, the GI can be associated with chlorophyll <italic>a</italic> from winter to early spring; both fluctuate at the same time. </p>
			<p><italic>Ostrea edulis</italic> is a rhythmical consecutive hermaphrodite species, in which both sexes occur in the same section of a gonad. Oysters alternate between male and female sexual phases and function as males in the early spawning season (<xref ref-type="bibr" rid="CIT50">Orton 1927</xref>). Environmental conditions such as temperature, salinity and food availability also affect the sex ratio of <italic>O. edulis</italic> (<xref ref-type="bibr" rid="CIT18">Diaz-Almela 2004</xref>, <xref ref-type="bibr" rid="CIT30">González-Araya et al. 2013</xref>). High temperature and salinity, especially, lead to the increase of the male proportion, while low temperature and salinity are associated with an increased proportion of females (<xref ref-type="bibr" rid="CIT54">Rao 1956</xref>). <xref ref-type="bibr" rid="CIT53">Quayle (1969)</xref> reported that if the food supply of <italic>C. gigas</italic> is poor, there is a tendency for females to change into males. This situation is explained by <xref ref-type="bibr" rid="CIT18">Diaz-Almela (2004)</xref> using the fact that there is probably a heavier energy cost in the development of ovocytes, and thus a lower probability of becoming female. In this study, we found that the ratio of male-to-female and male-to-hermaphrodite oysters was more than 19:1 and 1.15:1, respectively. According to <xref ref-type="bibr" rid="CIT68">Yolkolu and Lök (2000)</xref>, and <xref ref-type="bibr" rid="CIT23">Eversole (1989)</xref>, a high ratio of casual hermaphroditism and maleness may be the result of physiological stress, such as sudden changes in temperature and salinity or high turbidity. Water temperature of the Homa Lagoon differed greatly between day and night time, especially in the winter season. Moreover, one gametogenic phase follows the next without undergoing complete reabsorption. The annual sex ratio in marine bivalves is nearest to 1:1 in a healthy population (<xref ref-type="bibr" rid="CIT46">Morton 1991</xref>). In this study, the female percentage was low in the Homa Lagoon, but the percentage of female hermaphrodite individuals were high. We think that this situation is quite important in terms of balancing and future sustainability of the population. Consequently, female hermaphrodite individuals are supporting the oyster population. </p>
			<p>The main energy reserves for gametogenesis in bivalves are lipid and glycogen contents (<xref ref-type="bibr" rid="CIT32">Kang et al. 2000</xref>, <xref ref-type="bibr" rid="CIT20">Dridi et al. 2007</xref>, <xref ref-type="bibr" rid="CIT52">Pogoda et al. 2013</xref>). The reserve of energy can vary according to bivalve species (<xref ref-type="bibr" rid="CIT39">Lodeiros et al. 2001</xref>, <xref ref-type="bibr" rid="CIT17">Delgado and Pérez Camacho 2003</xref>, <xref ref-type="bibr" rid="CIT61">Vite-Garía and Saucedo 2008</xref>). <xref ref-type="bibr" rid="CIT05">Bayne (1976)</xref> states that the stored energy of bivalves used for gametogenesis can be classified into two categories: conservative species that use the energy stored in various organs (adductor muscle, digestive gland and mantle) and opportunistic species that use the energy from recently ingested food. Additionally, <xref ref-type="bibr" rid="CIT36">Joaquim et al. (2008)</xref> stated that some of the bivalve species use both methods. The strategy used to provide the energy required for gametogenesis can differ even in oysters of the same species (<xref ref-type="bibr" rid="CIT37">Li et al. 2006</xref>). Being an opportunistic or a conservative species is closely related to the quality and quantity of food. Our results showed that there is no resting period for this species and glycogen was not accumulated during the study period. <xref ref-type="bibr" rid="CIT32">Kang et al. (2000)</xref> found similar results and noted that because oysters have only a very short gonadal resting stage, the relationship between gonadal development and each biochemical component used to maintain energy and for reproduction is difficult to assess. The behaviour of <italic>O. edulis</italic> was opportunistic because there was sufficient food in Homa Lagoon throughout the year.</p>
			<p>According to <xref ref-type="bibr" rid="CIT20">Dridi et al. (2007)</xref>, lipid variations are closely related to gamete development, with the highest levels of lipids in the periods of maximum ripeness (<xref ref-type="bibr" rid="CIT20">Dridi et al. 2007</xref>) and the lowest in the periods of spawning (<xref ref-type="bibr" rid="CIT38">Liu et al. 2008</xref>). Similarly, our results showed a positive relationship between lipid and GI. The minimum total lipid value was determined in December and February, during the spawning period and the resting period. On the other hand, total lipid increased in January when the gonad was mature. </p>
			<p>Recently, many authors have reported that variations in protein seem to be heavily influenced by the reproductive cycle and it is likely that the protein accumulated in the tissues at earlier stages of maturation is used for the oocyte development and growth (<xref ref-type="bibr" rid="CIT06">Berthelin et al. 2000</xref>, <xref ref-type="bibr" rid="CIT43">Marin et al. 2003</xref>).  However, <xref ref-type="bibr" rid="CIT45">Mladineo et al. (2007)</xref> reported that the use of stored protein as an energy source is widely dependant on the availability of the other sources such as carbohydrates and lipids, being lower when these other sources are used at higher levels, and vice versa. According to <xref ref-type="bibr" rid="CIT63">Whyte et al. (1990)</xref>, protein was more efficient than carbohydrate as the main contributor of energy in lean times and fed the oysters during the winter months, when food was scarce. In the present study, protein was the major organic content found in oysters and the decline in protein coincided with maturation.</p>
			</sec>
			</body>
			
		<back>
<ack>
<title>ACKNOWLEDGEMENTS</title>
			
		  <p>This study was supported by BAP Project (SUF/014)/Ege University and was conducted in Homa (Sufa) Lagoon, Fishery Faculty of Ege University. Special thanks to Sedat Tepeli, and Bayram Ceylan for their help with technical assistance during the study period. Sincere thanks are also due to two anonymous referees, whose suggestions greatly improved the manuscript.</p>
			
		 </ack>
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