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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">sm4292</article-id>
			 <article-id pub-id-type="doi">10.3989/scimar.04292.09A</article-id>
			 
			
		<title-group>
			  <article-title>Identification of <italic>Chattonella</italic> (Raphidophyceae) species in long-term phytoplankton samples from Santa Giusta Lagoon, Italy</article-title>
		<trans-title-group xml:lang="es">
		<trans-title>Identificación de especies de <italic>Chattonella</italic> (Raphidophyceae) presentes en muestras de fitoplancton recogidas durante un monitoreo de larga duración en la Laguna de Santa Giusta (Cerdeña, Italia)</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> Stacca</surname>
				 <given-names>Daniela</given-names>
				</name>
				<xref ref-type="aff" rid="U1"/>
				<xref ref-type="corresp" rid="cor1"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Satta</surname>
				 <given-names>Cecilia Teodora</given-names>
				</name>
				<xref ref-type="aff" rid="U1"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Casabianca</surname>
				 <given-names>Silvia</given-names>
				</name>
				<xref ref-type="aff" rid="U2"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Penna</surname>
				 <given-names>Antonella</given-names>
				</name>
				<xref ref-type="aff" rid="U2"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Padedda</surname>
				 <given-names>Bachisio Mario</given-names>
				</name>
				<xref ref-type="aff" rid="U1"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Sechi</surname>
				 <given-names>Nicola</given-names>
				</name>
				<xref ref-type="aff" rid="U1"/>
			  </contrib>
			  <contrib contrib-type="author" corresp="no"> 
				<name>
				 <surname>Lugliè</surname>
				 <given-names>Antonella</given-names>
				</name>
				<xref ref-type="aff" rid="U1"/>
			  </contrib>
		  <aff id="U1">Dipartimento di Architettura, Design e Urbanistica, University of Sassari, Via Piandanna 4, 07100 Sassari, Italy. </aff>
			  <aff id="U2">Dipartimento di Scienze Biomolecolari, University of Urbino, Viale Trieste 296, 61100 Pesaro, Italy.</aff>
			 </contrib-group>
<contrib-group>
	<contrib contrib-type="editor">
		<name>
			<surname>Garcés</surname>
			<given-names>E.</given-names>
		</name>
		<role>Editor</role>
	</contrib>
	</contrib-group>	 
			 <author-notes>
		<corresp id="cor1">e-mail: <email xlink:href="dstacca@uniss.it">dstacca@uniss.it</email>
		</corresp>
		</author-notes>
		
<pub-date pub-type="epub">
		<day>31</day>
		<month>3</month>
		<year>2016</year>
		</pub-date>
		<pub-date pub-type="collection">
		<year>2016</year>
		</pub-date>
		
		<volume>80</volume>
		<issue>1</issue>
		<fpage>17</fpage>
		<lpage>25</lpage>
		
		<elocation-id content-type="doi">10.3989/scimar.04292.09A</elocation-id>

		 <history>
		  	<date date-type="received">
				<day>15</day>
				<month>6</month>
				<year>2015</year>
			</date>
			<date date-type="accepted">
				<day>8</day>
				<month>9</month>
				<year>2015</year>
			</date>
			<date date-type="published">
				<day>11</day>
				<month>12</month>
				<year>2015</year>
			</date>
		 </history>
		 
		<permissions>
		<copyright-statement>&#x00A9; 2016 CSIC</copyright-statement>
		<copyright-year>2016</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><italic>Chattonella</italic> species in a Mediterranean lagoon (Santa Giusta Lagoon, Sardinia, Italy) were identified by applying a molecular approach to fixed natural phytoplankton samples collected over the last two decades. Like the other raphidophytes, <italic>Chattonella</italic> cells are naked and lose their shape when fixed, making species identification difficult on the basis of their morphological characteristics. Employing species-specific primers (oBTG-005-F, oBTG-027-R, oBTG-028-R) for the amplification of the ITS-5.8S rDNA region, we established the occurrence of <italic>C. subsalsa</italic> in fixed natural phytoplankton samples collected in coincidence with fish death events. Additionally, we established the presence of the recently discovered <italic>C.</italic> cf. <italic>subsalsa</italic> Adriatic genotype by analysing cellular cultures obtained from the same lagoon in 2013. This is the second worldwide record of <italic>C.</italic> cf. <italic>subsalsa</italic> Adriatic genotype. Our results revealed that the species-specific primers oBTG-005-F and oBTG-028-R distinguished this new genotype only when present singularly. This study provides valuable data that increase knowledge of <italic>C. subsalsa</italic> genotypes and of the long-term occurrence of <italic>Chattonella</italic> blooms in a transitional ecosystem through the use of samples up to 20 years old. </p>
		</abstract>
		<trans-abstract xml:lang="es">
		<title>RESUMEN</title>
		<p>Se identificaron especies de <italic>Chattonella</italic> mediante la aplicación de técnicas moleculares en muestras naturales de fitoplancton. Las muestras fueron recogidas y fijadas durante las últimas dos décadas en una laguna litoral mediterránea (Laguna de Santa Giusta, Cerdeña, Italia). Al igual que otras rafidoficeas , las células de <italic>Chattonella</italic> no poseen teca y, por lo tanto, pierden su forma cuando se fijan lo que dificulta la identificación basada en características morfológicas. Con el uso de cebadores específicos a nivel de especie (OBTG-005-F, OBTG-027-R, OBTG-028-R) diseñados para la amplificación de la región ITS- 5.8S rDNA, se detectó la presencia de <italic>C. subsalsa</italic> en las muestras recogidas en periodos coincidentes con eventos de muerte de peces. A través del análisis de los cultivos celulares obtenidos de la misma laguna en el año 2013, se identificó la presencia, por segunda vez a nivel mundial, del recientemente descubierto genotipo Adriático de <italic>C</italic>. cf. <italic>subsalsa</italic>. Los resultados revelaron que los cebadores oBTG-005-F y oBTG-028-R amplifican este nuevo genotipo sólo cuando está presente individualmente. En este estudio se presentan datos relevantes para el conocimiento de los genotipos de <italic>C. subsalsa</italic> y sobre la presencia recurrente de proliferaciones de especies de <italic>Chatonella</italic> en un ecosistema de transición a través de la utilización de muestras recogidas durante los últimos veinte años y analizadas hoy en día.</p>
		</trans-abstract>
		<kwd-group xml:lang="en">
			<title>KEYWORDS</title>
			<kwd><italic>Chattonella subsalsa</italic> genotypes</kwd>
			<kwd>transitional ecosystems</kwd>
			<kwd>harmful algal blooms</kwd>
			<kwd>LTER-Italy</kwd>
			<kwd>ITS-5.8S rDNA</kwd>
			<kwd>LSU rDNA</kwd>			
		</kwd-group>
		<kwd-group xml:lang="es">
			<title>PALABRAS CLAVE</title>
			<kwd>genotipos de <italic>Chattonella subsalsa</italic></kwd>
			<kwd>ecosistemas de transición</kwd>
			<kwd>proliferaciones algales nocivas</kwd>
			<kwd>LTER-Italia</kwd>
			<kwd>ITS-5.8S rDNA</kwd>
			<kwd>LSU rDNA</kwd>
		</kwd-group>
	 </article-meta>
	</front>
<body>
<sec id="S1">
<title>INTRODUCTION</title>
			
			<p><italic>Chattonella</italic> Biecheler (Raphidophyceae) exhibits a worldwide distribution and includes deleterious species causing fish kills in natural environments and aquaculture systems (<xref ref-type="bibr" rid="CIT16">Imai and Yamaguchi 2012</xref> and references therein). The existing <italic>Chattonella</italic> taxonomy is still debated. <xref ref-type="bibr" rid="CIT16">Imai and Yamaguchi (2012)</xref>, in their review, recognized five species: <italic>Chattonella</italic><italic> antiqua</italic> (Hada) Ono, <italic>C. marina</italic> (Subrahmanyan) Hara et Chihara, <italic>C. minima</italic> Hara et Chihara, <italic>C. ovata</italic> Hara et Chihara, and <italic>C. subsalsa</italic> Biecheler. Previously, <xref ref-type="bibr" rid="CIT10">Demura et al. (2009)</xref> had proposed three species, determining that <italic>C. antiqua </italic>and <italic>C. ovata</italic> were varieties of <italic>C. marina</italic>. Recently, a new <italic>C.</italic> cf. <italic>subsalsa</italic> genotype was discovered in the Mediterranean Sea (Adriatic Sea; <xref ref-type="bibr" rid="CIT20">Klöpper et al. 2013</xref>), and a distinct species was recognized and related to <italic>C. subsalsa</italic> in the Oman Sea, along the southeast coast of Iran (<xref ref-type="bibr" rid="CIT02">Attaran-Fariman and Bolch 2014</xref>). </p>
			<p>Like the other raphidophytes, <italic>Chattonella</italic> species lack rigid cell walls. Consequently, their cellular shape and morphology are lost with fixation (<xref ref-type="bibr" rid="CIT03">Band-Schmidt et al. 2004</xref>, <xref ref-type="bibr" rid="CIT35">Zingone et al. 2006</xref>), making their identification particularly difficult. Instead, molecular techniques enable the identification of <italic>Chattonella</italic> species, similarly to other raphidophytes, in fixed samples. Moreover, species identification by the molecular approach can be used in retrospective studies (<xref ref-type="bibr" rid="CIT07">Bowers et al. 2006</xref>).</p>
			<p>On this basis, the first of our objectives was to identify which <italic>Chattonella</italic> species had been responsible for past blooms, in a part of the cases (four on five occasions) that coincided with fish kills in a Mediterranean lagoon (Santa Giusta Lagoon, Sardinia). In fact, although <xref ref-type="bibr" rid="CIT07">Bowers et al. (2006)</xref> have already reported <italic>C. subsalsa</italic> in Santa Giusta Lagoon (Oristano Lagoon Sardinia), we hypothesized that another species, <italic>C. marina</italic>, might also have been present, due to its morphological similarity to <italic>C. subsalsa</italic> and its overt harmfulness for fish (<xref ref-type="bibr" rid="CIT16">Imai and Yamaguchi 2012</xref> and references therein). Other mass fish and invertebrate mortalities have been attributed to a <italic>C. antiqua</italic> monospecific bloom in the Mediterranean Sea (Alexandria, Egypt; <xref ref-type="bibr" rid="CIT24">Mikhail 2007</xref>). </p>
			<p>To achieve our objective, we used a qualitative polymerase chain reaction on archived fixed natural phytoplankton samples (hereinafter named archived samples) up to twenty-years old that were collected during past summer blooms in 1994, 1998, 1999, 2010 and 2013. </p>
			<p>Until 2013, as stated above, all strains of <italic>C. subsalsa</italic> appeared to form a globally homogenous group (hereinafter named Global genotype, <xref ref-type="bibr" rid="CIT07">Bowers et al. 2006</xref>). Clear differences have been reported only recently among strains of the Global genotype and strains from the Adriatic Sea (hereinafter named the Adriatic genotype, <xref ref-type="bibr" rid="CIT20">Klöpper et al. 2013</xref>) and Oman Sea (<xref ref-type="bibr" rid="CIT02">Attaran-Fariman and Bolch 2014</xref>). Since <xref ref-type="bibr" rid="CIT07">Bowers et al. (2006)</xref> identified in Santa Giusta Lagoon <italic>C. subsalsa</italic> sequences coinciding with the Global genotype and we established the presence of the Adriatic genotype in the same lagoon in 2013, our hypothesis was that both <italic>C. subsalsa</italic> genotypes might have been present in the analysed archived samples. As a second objective of this study, we wanted to verify whether the same PCR-based assay could discriminate the two genotypes.</p>
			
</sec>
<sec id="S2">
<title>MATERIALS AND METHODS</title>
			
<sec id="S2.1">
<title>Study area</title>
			
		  <p>Santa Giusta Lagoon (Italy, western Mediterranean Sea) is located along the west central coast of Sardinia Island (<xref ref-type="fig" rid="F1">Fig. 1</xref>). It is a research station in part of the site “14 Sardinian marine ecosystems” of the LTER-Italy network (<ext-link ext-link-type="uri" xlink:href="http://www.lteritalia.it">www.lteritalia.it</ext-link>). Santa Giusta Lagoon has an area of 8 km<sup>2</sup> and a mean depth of 1 m. The two primary freshwater inputs are located on the lagoon’s east side and sea exchanges are on the western side. Santa Giusta underwent substantial human modification during the last century, resulting in profound ecosystem alterations (<xref ref-type="bibr" rid="CIT28">Sechi et al. 2001</xref>, <xref ref-type="bibr" rid="CIT22">Lugliè et al. 2002</xref>). <xref ref-type="bibr" rid="CIT28">Sechi et al. (2001)</xref> signalled its hypertrophy and reported several fish kill events associated with harmful algal blooms. Moreover, <xref ref-type="bibr" rid="CIT26">Satta et al. (2014)</xref> reported the presence of harmful dinoflagellate cysts in the sediments. </p>
		  			<fig id="F1">
				<label>Fig. 1</label>
				<caption>
				<title>Santa Giusta Lagoon and sampling stations.</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm80n1-4292-web-resources/image/sm4292fig1_fmt.jpeg"/>
			</fig>

</sec>
<sec id="S2.2">
<title>Sampling and phytoplankton analysis </title>
			
		  <p>The 27 archived samples analysed in this study (<xref ref-type="table" rid="T1">Table 1</xref>) belong to the LTER phytoplankton samples collection maintained at the Dipartimento di Architettura, Design e Urbanistica of the University of Sassari. They were collected from the water surface layer (–30 cm), from 3 to 5 stations (<xref ref-type="table" rid="T1">Fig. 1</xref>) during <italic>Chattonella</italic> blooms in the summers of 1994, 1998, 1999, 2010 and 2013, the first four coinciding with extensive fish mortalities. All samples were immediately fixed with Lugol’s iodine solution and analysed within ten days from sampling to assess <italic>Chattonella</italic> cell densities, following the Utermöhl method (<xref ref-type="bibr" rid="CIT33">Utermöhl 1958</xref>) and using an inverted Axiovert Zeiss 25 microscope. Further, within a few hours from the collection, live samples were always observed under the microscope for species identification.</p>
		  	<table-wrap id="T1">
			<label>Table 1</label>
		<caption>
			<title>List of analysed samples, <italic>Chattonella</italic> densities and PCR amplification assay results. +, positive amplification; –, negative amplification. * BLD, below the detection limit of &lt;10 cells L<sup>–1</sup>.</title>
		</caption>
		<table frame="hsides" rules="groups">
  <thead>

		        <tr>
		          <th rowspan="3">Sampling date</th>
		          <th rowspan="3">Station</th>
		          <th rowspan="3"> <italic>Chattonella</italic> density
		            (cells 10<sup>3</sup> L<sup>–1</sup>) </th>
		          <th colspan="4"> PCR amplifications </th>
	            </tr>
		        <tr>
		          <th colspan="2"> <italic>Chattonella subsalsa</italic> </th>
		          <th colspan="2"> <italic>Chattonella marina</italic> </th>
	            </tr>
		        <tr>
		          <th>Undiluted DNA</th>
		          <th>Diluted DNA</th>
		          <th>Undiluted DNA</th>
		          <th>Diluted DNA </th>
	            </tr>
	          </thead>
		      <tbody>
		        <tr>
		          <td> 03/08/1994 </td>
		          <td>1</td>
		          <td>12,927</td>
		          <td>- - -</td>
		          <td>+ + +</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>3</td>
		          <td>30,243</td>
		          <td>- - -</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 25/08/1994 </td>
		          <td>5</td>
		          <td>187</td>
		          <td>+ + -</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 06/09/1994 </td>
		          <td>3</td>
		          <td>831</td>
		          <td>+ + -</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>5</td>
		          <td>256</td>
		          <td>+ + -</td>
		          <td>+ - -</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 03/09/1998 </td>
		          <td>1</td>
		          <td>179</td>
		          <td>+ + +</td>
		          <td>+ - -</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>5</td>
		          <td>3,249</td>
		          <td>+ + +</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 26/08/1999 </td>
		          <td>2</td>
		          <td>3,692</td>
		          <td>+ + -</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>3</td>
		          <td>11,931</td>
		          <td>+ + -</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 07/09/1999 </td>
		          <td>1</td>
		          <td>1,278</td>
		          <td>- - -</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>2</td>
		          <td>1,315</td>
		          <td>+ - -</td>
		          <td>+ - -</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 19/07/2010 </td>
		          <td>3</td>
		          <td>399</td>
		          <td>+ + -</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>5</td>
		          <td>390</td>
		          <td>+ + -</td>
		          <td>+ - -</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 17/07/2010 </td>
		          <td>6</td>
		          <td>BLD*</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>3</td>
		          <td>BLD*</td>
		          <td>- - -</td>
		          <td>- - -</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>4</td>
		          <td>BLD*</td>
		          <td>- - -</td>
		          <td>- - -</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 22/07/2010 </td>
		          <td>2</td>
		          <td>474</td>
		          <td>+ + +</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>3</td>
		          <td>2,191</td>
		          <td>+ + -</td>
		          <td>+ + +</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>4</td>
		          <td>584</td>
		          <td>+ + -</td>
		          <td>+ - -</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 24/07/2010 </td>
		          <td>1</td>
		          <td>1,600</td>
		          <td>+ + +</td>
		          <td>+ + +</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>3</td>
		          <td>1,827</td>
		          <td>+ + -</td>
		          <td>+ + +</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 04/08/2010 </td>
		          <td>2</td>
		          <td>898</td>
		          <td>+ - -</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>3</td>
		          <td>2,511</td>
		          <td>+ + -</td>
		          <td>- - -</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 05/04/2012 </td>
		          <td>3</td>
		          <td>BLD*</td>
		          <td>- - -</td>
		          <td>- - -</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 30/07/2013 </td>
		          <td>3</td>
		          <td>15</td>
		          <td>+ + +</td>
		          <td>+ + +</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
		        <tr>
		          <td></td>
		          <td>5</td>
		          <td>34</td>
		          <td>+ + +</td>
		          <td>+ + +</td>
		          <td>- - -</td>
		          <td>- - -</td>
	            </tr>
		        <tr>
		          <td> 07/08/2013 </td>
		          <td>3</td>
		          <td>65</td>
		          <td>+ + +</td>
		          <td>+ + +</td>
		          <td>- - -</td>
		          <td> - - - </td>
	            </tr>
	          </tbody>
	        </table>
	      </table-wrap>
</sec>
<sec id="S2.3">
<title>Cellular cultures</title>
			
		  <p>Five clonal cultures of <italic>C</italic>. cf. <italic>subsalsa</italic> (Adriatic genotype) were established from samples collected from Santa Giusta Lagoon in July 2013 (UNISS7, UNISS8, UNISS9, UNISS10, UNISS11). Vegetative cells were isolated with glass micropipettes and transferred into IWAKI tissue culture multiplates. Plates were filled with L1 medium (<xref ref-type="bibr" rid="CIT11">Guillard and Hargraves 1993</xref>) prepared with filtered seawater adjusted to a salinity of 35, and maintained at 20±1°C with a 12:12 light:dark cycle. Illumination was provided by a photon irradiance of 100 µmol m<sup>–2</sup> s<sup>–1</sup>.</p>
			<p>Reference cultures of <italic>C. subsalsa</italic> (CCMP217; Global genotype) from the Scandinavian Culture Collection of Algae &amp; Protozoa (SCCAP) and <italic>C. antiqua</italic> (<italic>C. marina</italic> var. <italic>antiqua</italic>, NIES 1) (fixed with Lugol’s iodine solution) from the Provasoli-Guillard National Centre for Marine Algae and Micobiota (NCMA, formerly CCMP) were also acquired.</p>
			
		</sec>
<sec id="S2.4">
<title>Artificial samples and DNA tests</title>
			
		  <p>Three artificial phytoplankton samples (Lugol-fixed, hereinafter named artificial samples) were used to create controlled conditions of presence of Global and Adriatic <italic>C. subsalsa</italic> genotypes and other algae, as could happen in natural conditions. The first sample contained CCMP217 and UNISS8 strains (sample A; i.e. both Global and Adriatic genotypes), the others only one of the two genotypes, respectively sample B the Global genotype (CCMP217) and sample C the Adriatic genotype (UNISS8; <xref ref-type="table" rid="T2">Table 2</xref>). </p>
		  	<table-wrap id="T2">
			<label>Table 2</label>
		<caption>
			<title>Species composition and cell abundances (cells 10<sup>3</sup> L<sup>–1</sup>) of the analysed artificial samples.</title>
		</caption>
		<table frame="hsides" rules="groups">
  <thead>
		        <tr>
		          <th></th>
		          <th>Sample A</th>
		          <th>Sample B</th>
		          <th> Sample C </th>
	            </tr>
	          </thead>
		      <tbody>
		        <tr>
		          <td><italic>C. subsalsa</italic> CCMP217 </td>
		          <td>816</td>
		          <td>816</td>
		          <td> 0 </td>
	            </tr>
		        <tr>
		          <td><italic>C</italic>. cf. <italic>subsalsa</italic> Adriatic Genotype </td>
		          <td>764</td>
		          <td>0</td>
		          <td> 764 </td>
	            </tr>
		        <tr>
		          <td><italic>Alexandrium minutum</italic> Halim </td>
		          <td>304</td>
		          <td>304</td>
		          <td> 304 </td>
	            </tr>
		        <tr>
		          <td><italic>Amphidinium carterae</italic> Hulburt </td>
		          <td>550</td>
		          <td>550</td>
		          <td> 550 </td>
	            </tr>
		        <tr>
		          <td><italic>Scrippsiella</italic> sp. </td>
		          <td>694</td>
		          <td>694</td>
		          <td> 694 </td>
	            </tr>
		        <tr>
		          <td><italic>Cylindrotheca</italic> sp. </td>
		          <td>490</td>
		          <td>490</td>
		          <td> 490 </td>
	            </tr>
	          </tbody>
	        </table>
	      </table-wrap>
<p>Further, we mixed in different proportions the DNA extracted from two different cultures of <italic>C. subsalsa</italic> genotypes (CCMP217 and UNISS8, respectively) by performing six tests (hereinafter named DNA tests, <xref ref-type="table" rid="T3">Table 3</xref>) to verify whether different DNA concentrations might affect the ITS-5.8S rDNA amplification region.</p>
	<table-wrap id="T3">
			<label>Table 3</label>
		<caption>
			<title>List of tests carried out using the two <italic>C. subsalsa</italic> genotypes with different DNA concentrations (ng µL<sup>–1</sup>).</title>
		</caption>
		<table frame="hsides" rules="groups">
  <thead>
      <tr>
        <th></th>
        <th> <italic>C. subsalsa</italic> CCMP217 </th>
        <th> <italic>C</italic>. cf. <italic>subsalsa</italic> UNISS8 </th>
        <th>Concentration ratio</th>
      </tr>
    </thead>
    <tbody>
      <tr>
        <td> TEST 1 </td>
        <td>5.65</td>
        <td>11.29</td>
        <td>1:2</td>
      </tr>
      <tr>
        <td> TEST 2 </td>
        <td>2.26</td>
        <td>11.29</td>
        <td>1:5</td>
      </tr>
      <tr>
        <td>TEST 3</td>
        <td>1.13</td>
        <td>11.29</td>
        <td>1:10</td>
      </tr>
      <tr>
        <td> TEST 4 </td>
        <td>0.45</td>
        <td>11.29</td>
        <td>1:25</td>
      </tr>
      <tr>
        <td> TEST 5 </td>
        <td>0.26</td>
        <td>11.29</td>
        <td>1:50</td>
      </tr>
      <tr>
        <td> TEST 6 </td>
        <td>0.11</td>
        <td>11.29</td>
        <td> 1:100 </td>
      </tr>
    </tbody>
  </table>
</table-wrap>
</sec>
<sec id="S2.5">
<title>Molecular analyses</title>
			
		  <p>DNA was extracted with the DNeasy Plant Kit (Qiagen, Valencia, CA, USA) according to the manufacturer’s instructions from 50 mL of archived samples, artificial samples and from 15 mL of fixed cultures (<xref ref-type="fig" rid="F2">Fig. 2</xref>). </p>
		  			<fig id="F2">
				<label>Fig. 2</label>
				<caption>
				<title>Scheme of the protocol used; in the first passage, 50 mL of archived samples, 15 mL of artificial samples or 15 mL of cultures were used.</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm80n1-4292-web-resources/image/sm4292fig2_fmt.jpeg"/>
			</fig>


<p>PCR analyses were performed on archived samples from at least two of the sampled stations for each sampling date (<xref ref-type="table" rid="T1">Table 1</xref>). An archived sample with <italic>C. subsalsa</italic> abundance below the detection limit (&lt;10 cells L<sup>–1</sup>) and from a season not favourable to <italic>C. subsalsa</italic> growth (Station 3 of 5/4/2012) was used as a negative control. A first PCR was performed with 1 µL of extracted DNA (<xref ref-type="fig" rid="F2">Fig. 2</xref>) in a total of 40.5 µL reaction mixture containing the following: 0.25 mM of each dNTP; 0.1µM of each primer; 2.5 mM MgCl<sub>2</sub>; 1x HotMaster Taq Buffer (PRIME, Hamburg, Germany); and 2.5 U Taq DNA polymerase (PRIME). ITSA and ITSB primers (<xref ref-type="bibr" rid="CIT01">Adachi et al. 1994</xref>) were used to amplify the internal transcribed spacer (ITS) regions and 5.8S rDNA. PCR conditions were as follows: an initial denaturation step at 94°C for 5 min, followed by 35 cycles at 94°C for 20 s, 57°C for 10 s, and 70°C for 30 s; and a final elongation step at 70°C for 5 min. Six PCR replicates for each sample were performed, three with undiluted DNA and three with 1:10 diluted DNA (<xref ref-type="fig" rid="F2">Fig. 2</xref>). Subsequently, 1 µL of each PCR product was used in two distinct nested PCR amplifications (<xref ref-type="fig" rid="F2">Fig. 2</xref>), with the same mixture condition as above. These two different nested PCRs were carried out with specific primers: oBTG-005-F (CTGGGGAAGGATCATTACC) and oBTG-027-R (GCCGATTGCTTCCAGAGA) for <italic>C. marina</italic>, and oBTG-005-F and oBTG-028-R(CGCCACTCGTTGCCCAGT) for <italic>C. subsalsa</italic> (<xref ref-type="bibr" rid="CIT09">Connell 2002</xref>). Nested PCR conditions were as follows: an initial denaturation step at 95°C for 5 min; then 35 cycles at 95°C for 30 s, 55°C for 10 s (using species-specific primers for <italic>C. marina</italic>) or 45°C for 10 s (using species-specific primers for <italic>C. subsalsa</italic>), and 72°C for 30 s; and a final elongation step at 72°C for 10 min. The DNA extracted from the cultures <italic>C. subsalsa</italic> CCMP217 and <italic>C. antiqua </italic>(<italic>C. marina</italic> var. <italic>antiqua</italic>) NIES 1 were used as a positive control in each PCR on the analysed archived samples.</p>
			<p>Genetic analyses were also conducted to confirm species and genotype identification of the five <italic>C</italic>. cf. <italic>subsalsa</italic> UNISS7, UNISS8, UNISS9, UNISS10, UNISS11 cultures. For the ITS-5.8S rDNA sequences, the first PCR was performed using ITSA and ITSB primers (<xref ref-type="bibr" rid="CIT01">Adachi et al. 1994</xref>) and the nested PCR with primers oBTG-005-F and oBTG-028-R (<xref ref-type="bibr" rid="CIT09">Connell 2002</xref>), with the same PCR protocol as that described above. PCR primers D1R and D2C (<xref ref-type="bibr" rid="CIT27">Scholin et al. 1994</xref>) were used to amplify the LSU rDNA. PCR was carried out in 50-μL reactions containing 1 μL of DNA extract, 0.8 µM of each primer, 200 µM of dNTPs (Qiagen mix), PCR Buffer 1X (Qiagen) containing 1.5 mM of MgCl<sub>2</sub>, and 1.25 U of Taq DNA polymerase. Thermocycling included one initial step at 95°C for 5 min followed by 40 cycles at 95°C for 20 s, 55°C and at 72°C for 1 min, followed by a final extension at 72°C for 10 min. </p>
			<p>The whole protocol applied on archived samples was also tested on the three artificial samples (<xref ref-type="fig" rid="F2">Fig. 2</xref>,<xref ref-type="table" rid="T2"> Table 2</xref>). The same PCR-based assay was also applied on the six DNA tests (<xref ref-type="table" rid="T3">Table 3</xref>). The DNA concentration was evaluated with the SmartSpec<sup>TM</sup> Plus Spectrophotometer (Bio-rad) following the manufacturer’s instruction.</p>
			<p>All PCR amplifications were performed in a DNA Engine<sup>®</sup> Thermal Cycler.</p>
			<p>All PCR products were resolved on a 1.8% (80v) agarose gel. All nested PCR products were purified and sequenced by an external service (Macrogen Inc., Europe) using both primers, and a 3730XL DNA sequencer.</p>
			
	</sec>
<sec id="S2.6">
<title>	Phylogenetic analyses</title>
			
			<p>Sequences obtained in this study were compared with sequences in the NCBI Nucleotide Collection (BLAST Algorithm; <ext-link ext-link-type="uri" xlink:href="http://www.ncbi.nlm.-nih.gov">http://www.ncbi.nlm.-nih.gov</ext-link>) to determine the closest known sequences. Sequences were also aligned with those obtained from GenBank (<xref ref-type="table" rid="T4">Table 4</xref> and <xref ref-type="table" rid="T5">5</xref>) using the MAFFT v.6 program (<xref ref-type="bibr" rid="CIT18">Katoh et al. 2002</xref>) under FFT-NS-i (slow; iterative refinement method). Alignments were manually checked with BioEdit v. 7.0.5 (<xref ref-type="bibr" rid="CIT12">Hall 1999</xref>). Phylogenetic relationships, based on the LSU rDNA data (<xref ref-type="table" rid="T5">Table 5</xref>), were inferred using maximum likelihood (ML) method and the GTRGAMMA evolution model on Randomized Axelerated Maximum Likelihood v. 7.0.4 (RA×ML) (<xref ref-type="bibr" rid="CIT29">Stamatakis 2006</xref>). All model parameters were estimated by RA×ML, using <italic>Pseudochattonella verruculosa</italic> strains from public databases as an outgroup. The tree with the best topology (the one with the greatest likelihood of 1000 alternative trees) was selected by repeated runs on distinct starting trees. Bootstrap ML analysis was done with 1000 pseudo-replicates and the consensus tree was computed with the RA×ML software.</p>
				<table-wrap id="T4">
			<label>Table 4</label>
		<caption>
			<title>ITS-5.8S rDNA sequences obtained in this study and the sequences deposited at GenBank which showed a strong similarity with ours in the BLAST analysis. </title>
		</caption>
		<table frame="hsides" rules="groups">
  <thead>
			      <tr>
			        <th>Accession number</th>
			        <th>Geographical origin</th>
			        <th> Strain code or source </th>
			        <th>References</th>
		          </tr>
		        </thead>
			    <tbody>
			      <tr>
			        <td> AB334367 </td>
			        <td>Gulf of Mexico, USA</td>
			        <td> CCMP 217 </td>
			        <td><xref ref-type="bibr" rid="CIT10">Demura et al. 2009</xref></td>
		          </tr>
			      <tr>
			        <td> AB334368 </td>
			        <td>Indian River Bay, USA</td>
			        <td>CCMP 2191</td>
			        <td><xref ref-type="bibr" rid="CIT10">Demura et al. 2009</xref></td>
		          </tr>
			      <tr>
			        <td> AF153196 </td>
			        <td>Gulf of Mexico, USA</td>
			        <td>CCMP 217</td>
			        <td><xref ref-type="bibr" rid="CIT08">Connell 2000</xref></td>
		          </tr>
			      <tr>
			        <td> AF409126 </td>
			        <td>/</td>
			        <td>/</td>
			        <td><xref ref-type="bibr" rid="CIT05">Ben Ali et al. 2002</xref></td>
		          </tr>
			      <tr>
			        <td> AY858864 </td>
			        <td>Seto Island Sea, Japan</td>
			        <td>CMSTAC J04 C. Tomas Japan</td>
			        <td><xref ref-type="bibr" rid="CIT07">Bowers et al. 2006</xref></td>
		          </tr>
			      <tr>
			        <td> AY858866 </td>
			        <td>Salton Sea, California, USA</td>
			        <td>CMSTAC SS 4 C. Tomas California</td>
			        <td><xref ref-type="bibr" rid="CIT07">Bowers et al. 2006</xref></td>
		          </tr>
			      <tr>
			        <td> AY858868 </td>
			        <td>New River, North Carolina, USA</td>
			        <td>CMSTAC NR 22 C. Tomas North Carolina</td>
			        <td><xref ref-type="bibr" rid="CIT07">Bowers et al. 2006</xref></td>
		          </tr>
			      <tr>
			        <td> AY858869 </td>
			        <td>Santa Giusta Lagoon, Sardinia, Italy</td>
			        <td>CMSTAC OL 4 C. Tomas Sardinia</td>
			        <td><xref ref-type="bibr" rid="CIT07">Bowers et al. 2006</xref></td>
		          </tr>
			      <tr>
			        <td> DQ191680 </td>
			        <td>Delaware Inland Bays, USA</td>
			        <td>CCMP 2191</td>
			        <td><xref ref-type="bibr" rid="CIT34">Zhang et al. 2006</xref></td>
		          </tr>
			      <tr>
			        <td> JF896101 </td>
			        <td>Iran</td>
			        <td>CHPI36</td>
			        <td><xref ref-type="bibr" rid="CIT02">Attaran-Fariman and Bolch 2014 </xref></td>
		          </tr>
			      <tr>
			        <td> JF907041 </td>
			        <td>Bahia de Navachiste, Sinaloa, Mexico</td>
			        <td>CSNAV-1</td>
			        <td><xref ref-type="bibr" rid="CIT04">Band-Schmidt et al. 2012 </xref></td>
		          </tr>
			      <tr>
			        <td>JX067584 </td>
			        <td>Adriatic Sea, Rimini, Italy</td>
			        <td>CRIM_F</td>
			        <td><xref ref-type="bibr" rid="CIT20">Klöpper et al. 2013</xref></td>
		          </tr>
			      <tr>
			        <td> JX067585 </td>
			        <td>Adriatic Sea, Rimini, Italy</td>
			        <td>CRIM_E</td>
			        <td><xref ref-type="bibr" rid="CIT20">Klöpper et al. 2013</xref></td>
		          </tr>
			      <tr>
			        <td> KR709213 </td>
			        <td>Santa Giusta Lagoon, Italy</td>
			        <td>UNISS7</td>
			        <td>This study</td>
		          </tr>
			      <tr>
			        <td> KR709214 </td>
			        <td>Santa Giusta Lagoon, Italy</td>
			        <td>UNISS8</td>
			        <td>This study</td>
		          </tr>
			      <tr>
			        <td>KR709215</td>
			        <td>Santa Giusta Lagoon, Italy</td>
			        <td>UNISS9</td>
			        <td>This study</td>
		          </tr>
			      <tr>
			        <td> KR709216 </td>
			        <td>Santa Giusta Lagoon, Italy</td>
			        <td>UNISS10</td>
			        <td>This study</td>
		          </tr>
			      <tr>
			        <td> KR709217 </td>
			        <td>Santa Giusta Lagoon, Italy</td>
			        <td>UNISS11</td>
			        <td>This study</td>
		          </tr>
			      <tr>
			        <td> KR709218 </td>
			        <td>Gulf of Mexico, USA</td>
			        <td>CCMP217</td>
			        <td> This study </td>
		          </tr>
		        </tbody>
		      </table>
		  </table-wrap>
		  	<table-wrap id="T5">
			<label>Table 5</label>
		<caption>
			<title>List of the species, strains, geographical origin and GenBank accession numbers of species used in the LSU rDNA phylogenetic tree. * obtained in this study.</title>
		</caption>
		<table frame="hsides" rules="groups">
  <thead>
                  <tr>
                    <th>Species</th>
                    <th>Strain code or source</th>
                    <th>Geographical origin</th>
                    <th> Accession Number </th>
                  </tr>
                </thead>
                <tbody>
                  <tr>
                    <td rowspan="5"><italic>Fibrocapsa</italic> cf. <italic>japonica</italic>
                      
                      </td>
                    <td>FRIM_A</td>
                    <td>Adriatic Sea, Rimini, Italy</td>
                    <td> JX067577
                      </td>
                  </tr>
                  <tr>
                    <td>FRIM_B</td>
                    <td>Adriatic Sea, Rimini, Italy</td>
                    <td> JX067578
                      </td>
                  </tr>
                  <tr>
                    <td>FRIM_C</td>
                    <td>Adriatic Sea, Rimini, Italy</td>
                    <td> JX067574
                      </td>
                  </tr>
                  <tr>
                    <td>FRIM_D</td>
                    <td>Adriatic Sea, Rimini, Italy</td>
                    <td> JX067575
                      </td>
                  </tr>
                  <tr>
                    <td>FRIM_E</td>
                    <td>Adriatic Sea, Rimini, Italy</td>
                    <td> JX067576
                      </td>
                  </tr>
                  <tr>
                    <td rowspan="3"><italic>F. japonica</italic>
                      
                      Toriumi et Takano&#160;
                      
                      </td>
                    <td>CCMP1661</td>
                    <td>Port Phillip Bay, Australia</td>
                    <td> JX067580
                      </td>
                  </tr>
                  <tr>
                    <td>Fibjap_JG</td>
                    <td>North Sea, Germany:</td>
                    <td> JX067579
                      </td>
                  </tr>
                  <tr>
                    <td>LB2162</td>
                    <td>/</td>
                    <td> AF086949
                      </td>
                  </tr>
                  <tr>
                    <td><italic>Haramonas dimorpha</italic> Horiguchi 1996
                      </td>
                    <td>CCMP2053</td>
                    <td>Queensland, Australia</td>
                    <td> JX067581
                      </td>
                  </tr>
                  <tr>
                    <td rowspan="5"><italic>Heterosigma akashiwo</italic> (Hada)
                      
                      Hada ex Hara et Chihara&#160;
                      </td>
                    <td>NIES-145</td>
                    <td>Kagoshima, Japan</td>
                    <td> AB217645
                      </td>
                  </tr>
                  <tr>
                    <td>893</td>
                    <td>/</td>
                    <td> AB217646
                      </td>
                  </tr>
                  <tr>
                    <td>OS-11</td>
                    <td>/</td>
                    <td> AB217647
                      </td>
                  </tr>
                  <tr>
                    <td>/</td>
                    <td>Korea</td>
                    <td> JX067554
                      </td>
                  </tr>
                  <tr>
                    <td>CCMP2274</td>
                    <td>California, USA</td>
                    <td> JX067555
                      </td>
                  </tr>
                  <tr>
                    <td rowspan="4"><italic>C. subsalsa</italic> Biecheler
                      </td>
                    <td>/</td>
                    <td>/</td>
                    <td> AF409126
                      </td>
                  </tr>
                  <tr>
                    <td>CCMP217</td>
                    <td>Gulf of Mexico, USA</td>
                    <td> JX067559
                      </td>
                  </tr>
                  <tr>
                    <td>CCMP217</td>
                    <td>Gulf of Mexico, USA</td>
                    <td> AF210736
                      </td>
                  </tr>
                  <tr>
                    <td>CCMP217</td>
                    <td>Gulf of Mexico, USA</td>
                    <td> KR709212*
                      </td>
                  </tr>
                  <tr>
                    <td><italic>C.</italic> cf. <italic>subsalsa</italic>
                      </td>
                    <td>CHPI36</td>
                    <td>Iran</td>
                    <td> JF896100
                      </td>
                  </tr>
                  <tr>
                    <td rowspan="20"><italic>C.</italic> cf. <italic>subsalsa</italic> Adriatic
                      </td>
                    <td>R281</td>
                    <td>Gulf of Naples, Italy</td>
                    <td> JN390438
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_A</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067560
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_B</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067562
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_C</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067568
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_D</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td>JX067564</td>
                  </tr>
                  <tr>
                    <td>CRIM_E</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067567
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_F</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067563
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_G</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067572
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_H</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067561
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_I</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067571
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_J</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067570
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_K</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067565
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_L</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067566
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_M</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067569
                      </td>
                  </tr>
                  <tr>
                    <td>CRIM_N</td>
                    <td>Rimini, Adriatic, Italy</td>
                    <td> JX067573
                      </td>
                  </tr>
                  <tr>
                    <td>UNISS7</td>
                    <td>Santa Giusta Lagoon, Italy</td>
                    <td> KR709207*
                      </td>
                  </tr>
                  <tr>
                    <td>UNISS8</td>
                    <td>Santa Giusta Lagoon, Italy</td>
                    <td> KR709208*
                      </td>
                  </tr>
                  <tr>
                    <td>UNISS9</td>
                    <td>Santa Giusta Lagoon, Italy</td>
                    <td> KR709209*
                      </td>
                  </tr>
                  <tr>
                    <td>UNISS10</td>
                    <td>Santa Giusta Lagoon, Italy</td>
                    <td> KR709210*
                      </td>
                  </tr>
                  <tr>
                    <td>UNISS11</td>
                    <td>Santa Giusta Lagoon, Italy</td>
                    <td> KR709211*
                      </td>
                  </tr>
                  <tr>
                    <td rowspan="7"><italic>Chattonella marina</italic> var. <italic>antiqua</italic>
                      
                      (Hada) Demura &amp; Kawachi, comb et stat. nov.
                      </td>
                    <td>CCMP2052</td>
                    <td>Aichi, Japan</td>
                    <td>JX067556</td>
                  </tr>
                  <tr>
                    <td>G8</td>
                    <td>/</td>
                    <td>AB217634</td>
                  </tr>
                  <tr>
                    <td>NIES-1</td>
                    <td>Harima-Nada, Japan</td>
                    <td> AB217631
                      </td>
                  </tr>
                  <tr>
                    <td>NIES-1</td>
                    <td>Harima-Nada, Japan</td>
                    <td> AF210737
                      </td>
                  </tr>
                  <tr>
                    <td>NIES-558</td>
                    <td>Mikawa Bay, Japan</td>
                    <td> AB217632
                      </td>
                  </tr>
                  <tr>
                    <td>NIES-86</td>
                    <td>Uranouchi Bay, Japan</td>
                    <td>AB217868</td>
                  </tr>
                  <tr>
                    <td>OA-3</td>
                    <td>/</td>
                    <td> AB217633
                      </td>
                  </tr>
                  <tr>
                    <td rowspan="8"><italic>C. marina</italic> var. <italic>marina</italic>
                      
                      (Subrahmanyan) Hara et
                      
                      Chihara&#160;
                      </td>
                    <td>S-11</td>
                    <td>/</td>
                    <td> AB217637
                      </td>
                  </tr>
                  <tr>
                    <td>NIES-559</td>
                    <td>Maizuru Bay, Japan</td>
                    <td> AB217636
                      </td>
                  </tr>
                  <tr>
                    <td>G-12</td>
                    <td>/</td>
                    <td>AB217638</td>
                  </tr>
                  <tr>
                    <td>MS-3-P</td>
                    <td>/</td>
                    <td> AB217639
                      </td>
                  </tr>
                  <tr>
                    <td>NIES-121</td>
                    <td>Kagoshima Bay, Japan</td>
                    <td> AB217635
                      </td>
                  </tr>
                  <tr>
                    <td>/</td>
                    <td>Hong Kong</td>
                    <td> AY704162
                   </td>
                  </tr>
                  <tr>
                    <td>CCMP-217</td>
                    <td>/</td>
                    <td> AF210739
                      </td>
                  </tr>
                  <tr>
                    <td>CCMP2049</td>
                    <td>Kagoshima, Japan</td>
                    <td>JX067557</td>
                  </tr>
                  <tr>
                    <td rowspan="4"><italic>Chattonella marina</italic> var. <italic>ovata</italic> (Y. Hara &amp; Chihara) Demura &amp; Kawachi, comb. et stat. nov.
                     </td>
                    <td>NIES-603</td>
                    <td>Harima-Nada, Japan</td>
                    <td>AB217640</td>
                  </tr>
                  <tr>
                    <td>ovata-P</td>
                    <td>/</td>
                    <td>AB217641</td>
                  </tr>
                  <tr>
                    <td>/</td>
                    <td>Hong Kong</td>
                    <td> AY704163
                      </td>
                  </tr>
                  <tr>
                    <td>NIES-603</td>
                    <td>Harima-Nada, Japan</td>
                    <td> AF210738
                      </td>
                  </tr>
                  <tr>
                    <td rowspan="3"><italic>Pseudochattonella verruculosa</italic>
             
                      Hosoi-Tanabe 2007
                      </td>
                    <td>NIES 670 </td>
                    <td>Harima-Nada, Japan</td>
                    <td> AM040504
                      </td>
                  </tr>
                  <tr>
                    <td>NIES-670</td>
                    <td>Harima-Nada, Japan</td>
                    <td> AB217642
                      </td>
                  </tr>
                  <tr>
                    <td>ver-P</td>
                    <td>/</td>
                    <td> AB217643
                      </td>
                  </tr>
                </tbody>
              </table>
          </table-wrap>
		  </sec>
	   </sec>
<sec id="S3">
<title>RESULTS</title>
			
<sec id="S3.1">
<title>Archived samples</title>
			
		  <p>Through the sequencing and BLAST analysis of the nested PCR products, <italic>C. subsalsa</italic> was detected in all archived samples, which resulted positive also for microscope analysis (<xref ref-type="table" rid="T1">Table 1</xref>). The only exception was a sample taken before the beginning of the bloom in 2010 (17/7/2010), for which PCR results were positive and microscope analysis negative, and the sample was assumed as negative (Station 3 of 5/4/2012).</p>
			<p>All PCR products unequivocally belonged to <italic>C. subsalsa</italic>, with control DNA of 380 bp length for <italic>C. subsalsa</italic> CCMP217 (<xref ref-type="fig" rid="F3">Fig 3a</xref>, GenBank accession number KR709218) and 181 bp for <italic>C. antiqua</italic> (<italic>C. marina </italic>var. <italic>antiqua</italic>) NIES 1 (<xref ref-type="fig" rid="F3">Fig 3b</xref>).</p>
						<fig id="F3">
				<label>Fig. 3</label>
				<caption>
				<title>Nested PCR amplification products using an EasyLadder I - Bioline (L) for <italic>C. subsalsa</italic> and <italic>C. antiqua</italic> (<italic>C. marina</italic> var. <italic>antiqua</italic>) NIES 1: a) <italic>C. subsalsa</italic>, six replicates of 22-7-2010 (station 2) sample with five positive PCR amplifications (2-6), the positive control using CCMP217 culture (+), and the negative control (–); b) <italic>C. marina</italic>, six replicates of 22-7-2010 (station 3) sample with six negative PCR amplifications (1-6), three replicates of <italic>C. antiqua</italic> (<italic>C. marina</italic> var. <italic>antiqua</italic>) NIES 1 culture as positive controls (+), and the negative control (–). </title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm80n1-4292-web-resources/image/sm4292fig3_fmt.jpeg"/>
			</fig>

<p>ITS-5.8S rDNA sequences comparison among sequences from the 24 archived samples and those of <italic>C. subsalsa</italic> deposited in GenBank (<xref ref-type="table" rid="T4">Table 4</xref>) yielded a BLAST analysis with a 99%-100% similarity with the Global genotype sequences, 96%-97% sequence identity with the <italic>C</italic>. cf. <italic>subsalsa</italic> strains CRIM E and CRIM F (i.e. Adriatic genotype) and 98%-99% sequence identity with the <italic>C</italic>. cf. <italic>subsalsa</italic> strain CHPI36. </p>
			
		</sec>
<sec id="S3.2">
<title>	Cellular cultures</title>
			
		  <p>The nested PCR on cellular cultures produced six ITS-5.8S rDNA sequences (<xref ref-type="table" rid="T4">Table 4</xref>), four of which were of 573 bp (UNISS7, UNISS8, UNISS9, UNISS10 strains) and one of 576 pb (UNISS11 strain). These five sequences were longer than the nested PCR product of CCMP217 strain (380 pb) (<xref ref-type="fig" rid="F4">Fig. 4</xref>). </p>
		  			<fig id="F4">
				<label>Fig. 4</label>
				<caption>
				<title>Nested PCR amplification products using an EasyLadder I - Bioline (L) for <italic>C</italic>. cf. <italic>subsalsa</italic> Adriatic genotype (where C1AS, C1DS are the UNISS7 strain and C7AS, C7DS are the UNISS11 strain), <italic>C. subsalsa</italic> CCMP217 culture (+S), and two negative controls (=, –).</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm80n1-4292-web-resources/image/sm4292fig4_fmt.jpeg"/>
			</fig>

<p>The MAFT alignment among the oBTG-028-R primer and the ITS-5.8S rDNA sequences of <italic>C. subsalsa</italic> strains (UNISS7, UNISS9, CCMP217, CRIM E and C. Tomas Sardinia) indicated seven differences for UNISS7, UNISS9, CRIM E strains (i.e. Adriatic genotype) with respect to the CCMP217 and C. Tomas Sardinia strains (i.e. Global genotype). The BLAST analysis of 5.8S-ITS rDNA sequences showed a 99%-100% similarity of UNISS7, UNISS8, UNISS9, UNISS10 and UNISS11 strains with <italic>C</italic>. cf. <italic>subsalsa</italic> CRIM E and CRIM F strains and 94%-96% sequence identity with all <italic>C. subsalsa</italic> Global sequences (<xref ref-type="table" rid="T4">Table 4</xref>). </p>
			<p>The six LSU rDNA partial sequences were long 652 pb for UNISS7, 650 pb for UNISS8, UNISS10 and UNISS11, 651 pb for UNISS9 and 643 pb for CCMP217. The ML phylogenetic tree obtained for LSU rDNA sequences showed that <italic>C. subsalsa</italic> strains divided into two distinct groups (<xref ref-type="fig" rid="F5">Fig. 5</xref>). The first group showed a branch with the only <italic>C</italic>. cf. <italic>subsalsa</italic> CHPI36 and another with <italic>C. subsalsa</italic> CCMP217 and <italic>C. subsalsa</italic> AF409126. The second group included all <italic>C</italic>. cf. <italic>subsalsa</italic> Adriatic genotype (<xref ref-type="bibr" rid="CIT20">Klöpper et al. 2013</xref>) and UNISS7, UNISS8, UNISS9, UNISS10, UNISS11 strains, with a bootstrap value of 100%. All strains of <italic>C. marina</italic> var. <italic>marina</italic>, <italic>C. marina</italic> var. <italic>ovata</italic>, and <italic>C. marina</italic> var. <italic>antiqua</italic> grouped together with a 100% bootstrap support. </p>
						<fig id="F5">
				<label>Fig. 5</label>
				<caption>
				<title>Maximum likelihood (ML) phylogenetic tree of LSU rDNA sequences among <italic>Chattonella</italic>-like species. <italic>C. subsalsa</italic> CCMP217_UNISS12 is the sequence obtained in this study for the <italic>C. subsalsa</italic> Global genotype (KR709212), <italic>Pseudochattonella verruculosa</italic> strains from public databases were used as an outgroup. Bootstrap values (&gt;70%) are shown respectively at each node.</title>
				</caption>
				<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="../sm80n1-4292-web-resources/image/sm4292fig5_fmt.jpeg"/>
			</fig>

		
</sec>
<sec id="S3.3">
<title>Artificial samples and DNA tests</title>
			
		  <p>The nested PCR of the samples A and B produced sequences with a length of 380 pb belonging to <italic>C. subsalsa</italic> CCMP217. The nested PCR of sample C produced a sequence with a length of 573 pb belonging to <italic>C</italic>. cf. <italic>subsalsa</italic> UNISS8. </p>
			<p>The nested PCR of DNA tests produced sequences with a length of 380 pb belonging to the CCMP217 strain even when <italic>C</italic>. cf. <italic>subsalsa</italic> UNISS8 had a concentration one hundred times higher. </p>
	</sec>		
	</sec>
<sec id="S4">
<title>DISCUSSION</title>
			
		  <p><italic>Chattonella</italic> is one of the raphidophyte genera which includes species associated with fish kills (<xref ref-type="bibr" rid="CIT13">Hallegraeff and Hara 2003</xref>). The searching out of these taxa in recent investigations and in time series data has been very difficult due to the loss of necessary morphological characteristics in fixed samples (<xref ref-type="bibr" rid="CIT20">Klöpper et al. 2013</xref>), and presumably due to low cell abundance in coastal areas (<xref ref-type="bibr" rid="CIT15">Imai et al. 2006</xref>). Consequently, <italic>Chattonella</italic> species often become evident only when harmful events occur. Further, whereas harmful <italic>Chattonella</italic> blooms have been well documented on East Asian coasts, i.e. those of Japan, Korea (<xref ref-type="bibr" rid="CIT19">Kim et al. 2007</xref>), China (<xref ref-type="bibr" rid="CIT32">Tseng et al. 1993</xref>), India (<xref ref-type="bibr" rid="CIT30">Subrahmanyan 1954</xref>, <xref ref-type="bibr" rid="CIT17">Jugnu and Kripa 2009</xref>), South Australia (<xref ref-type="bibr" rid="CIT14">Hallegraeff et al. 1998</xref>), and southeast USA (California, <xref ref-type="bibr" rid="CIT31">Tomas 1998</xref>, <xref ref-type="bibr" rid="CIT21">Lewitus et al. 2008</xref>), in the last few decades (<xref ref-type="bibr" rid="CIT16">Imai and Yamaguchi 2012</xref>) they have been less frequently reported from Mediterranean coastal areas, including lagoons and other transitional ecosystems (<xref ref-type="bibr" rid="CIT24">Mikhail 2007</xref>). The use of molecular methods to detect the presence of <italic>Chattonella</italic> species is a viable alternative approach to expedite and facilitate identification in fixed natural samples (<xref ref-type="bibr" rid="CIT09">Connell 2002</xref>, <xref ref-type="bibr" rid="CIT07">Bowers et al. 2006</xref>; <xref ref-type="bibr" rid="CIT23">Marin and Scholin 2010</xref>), as has been experienced for other harmful species (<xref ref-type="bibr" rid="CIT25">Penna et al. 2007</xref>).</p>
			<p>Between <italic>C. marina</italic> and <italic>C. subsalsa</italic>, the former is the most notorious fish-killing species and has caused severe damage to fish farming and wild fish populations, with great economic losses (<xref ref-type="bibr" rid="CIT16">Imai and Yamaguchi 2012</xref>). <italic>C. subsalsa</italic> has exhibited relatively more recent history as a deleterious species, and data on this species is scarce (<xref ref-type="bibr" rid="CIT016">Imai and Yamaguchi 2012</xref>). Cell morphology shows overlapping characters between <italic>C. subsalsa</italic> and <italic>C. marina</italic>, as emphasized by <xref ref-type="bibr" rid="CIT13">Hallegraeff and Hara (2003)</xref>. Consequently, species identification with microscopic methods is uncertain, especially on fixed samples, whereas molecular techniques appear useful for obtaining valuable results.</p>
			<p><xref ref-type="bibr" rid="CIT07">Bowers et al. (2006)</xref> have already reported <italic>C. subsalsa</italic> in Santa Giusta Lagoon, analysing a strain obtained from a non-bloom sample (Lugliè A., personal communication). Our study considered a longer and more detailed temporal scale in the same Mediterranean lagoon and documented the presence of <italic>C. subsalsa</italic> also during four past harmful events coinciding with fish kills (1994, 1998, 1999, 2010), and a bloom in 2013 (cells density up to 65 10<sup>3</sup> L<sup>–1</sup>). The use of molecular investigative techniques on archived samples collected over time up to 20 years old allowed us to identify unequivocally the species and helped increase knowledge of <italic>C. subsalsa</italic> in the Mediterranean Sea. Indeed, this geographical area is not yet well documented for this species, though its type locality is a Mediterranean lagoon (Thau Lagoon, Salins de Villeroy, Sète; <xref ref-type="bibr" rid="CIT06">Biecheler 1936</xref>). Although we cannot support a cause-effect relationship between <italic>C. subsalsa</italic> blooms and fish kills, which have been observed concurrently over the years, our results can confirm that when harmful events occurred, <italic>C. subsalsa</italic> was present. On-going studies integrating our long-term ecological data will offer further detailed scenarios on the environmental conditions accompanying these events. </p>
			<p>A further new knowledge that emerged from our results was the presence of the <italic>C</italic>. cf. <italic>subsalsa</italic> Adriatic genotype in the Santa Giusta Lagoon, thanks to the analyses on the cultures obtained in 2013. This is the first unequivocal evidence of this genotype in a Mediterranean lagoon and in a different place to those of its first ascertainment (<xref ref-type="bibr" rid="CIT20">Klöpper et al. 2013</xref>). The analyses performed to assess whether both genotypes had been present in the archived samples could not resolve the question. In fact, the positive results of the PCR only for <italic>C. subsalsa</italic> Global genotype in the archived samples, artificial samples A and B and DNA tests could be explained because of the differences in the DNA bases of the two <italic>C. subsalsa</italic> genotypes where the oBTG-028-R primer binds. This is a specific primer constructed by <xref ref-type="bibr" rid="CIT09">Connell (2002)</xref> for <italic>C. subsalsa</italic> CCMP217 Global genotype. The length of <italic>C. subsals</italic>a Global genotype sequences obtained in this study was in accordance with <xref ref-type="bibr" rid="CIT09">Connell (2002)</xref>, whereas <italic>C</italic>. cf. <italic>subsalsa</italic> Adriatic genotype sequences were longer, indicating a different primer response. Therefore, this primer cannot discriminate the two <italic>C. subsalsa</italic> genotypes when they are present at the same time. On this basis, because of the positivity of <italic>C. subsalsa</italic> Global genotype in all archived samples, we cannot state whether the blooms were due to the contemporaneous presence of both the genotypes. However, for the same reason, we can state that none of them was due only to the <italic>C</italic>. cf. <italic>subsalsa</italic> Adriatic genotype. </p>
			<p>In conclusion, our results support the recent studies of <xref ref-type="bibr" rid="CIT20">Klöpper et al. (2013)</xref> and <xref ref-type="bibr" rid="CIT02">Attaran-Fariman and Bolch (2014)</xref>, highlighting the existence of clearly distinct strains of <italic>C. subsalsa</italic>. We also support the “overlapping hypothesis” of the two genotypes, Adriatic and Global, in the same geographical area (<xref ref-type="bibr" rid="CIT20">Klöpper et al. 2013</xref>). In fact, in addition to our assessment of the <italic>C</italic>. cf. <italic>subsalsa</italic> Adriatic genotype in Santa Giusta Lagoon and the previous record of the <italic>C. subsalsa </italic>Global genotype at the same site (<xref ref-type="bibr" rid="CIT07">Bowers et al. 2006</xref>), we also confirm the presence of the Global genotype along the western Sardinian coasts (Bosa beach; data not published). </p>
			<p>The need for further studies is evident, using a plurality of markers on strains from additional Mediterranean and world sites, in order to ascertain the possibility of different new species.</p>
			
		</sec>
		</body>
		<back>
<ack>
<title>ACKNOWLEDGEMENTS</title>
			
		  <p>This study was produced as part of the PhD dissertation in Environmental Biology from the University of Sassari, Academic year 2010-2011 – 26th cycle, with the support of a grant funded with resources from the POR SARDINIA F.S.E. 2007-2013 – Objective Regional Competitiveness and Employment, Human Capital Priority IV, Line Operation l.3.1. The authors thank Adriana Zingone of the Laboratory of Marine Botany, Stazione Zoologica “A. Dohrn”, Napoli, Italy for her support and advice on the analyses.</p>
		  </ack>
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