<?xml version="1.0" encoding="ISO-8859-1"?><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance">
<front>
<journal-meta>
<journal-id>0034-7744</journal-id>
<journal-title><![CDATA[Revista de Biología Tropical]]></journal-title>
<abbrev-journal-title><![CDATA[Rev. biol. trop]]></abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name><![CDATA[Universidad de Costa Rica]]></publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0034-77442013000100015</article-id>
<title-group>
<article-title xml:lang="en"><![CDATA[Evaluation of marking efficiency of different alizarin red S concentrations on body fish structures in Oreochromis niloticus (Perciformes: Cichlidae) juveniles]]></article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Ibáñez]]></surname>
<given-names><![CDATA[Ana L.]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Rodríguez-Canto]]></surname>
<given-names><![CDATA[Antonio]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Cortés-Martínez]]></surname>
<given-names><![CDATA[Jasmín]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[García-Calderón]]></surname>
<given-names><![CDATA[José L.]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution><![CDATA[,Universidad Autónoma Metropolitana-Iztapalapa  ]]></institution>
<addr-line><![CDATA[ D.F]]></addr-line>
<country>México</country>
</aff>
<pub-date pub-type="pub">
<day>00</day>
<month>03</month>
<year>2013</year>
</pub-date>
<pub-date pub-type="epub">
<day>00</day>
<month>03</month>
<year>2013</year>
</pub-date>
<volume>61</volume>
<numero>1</numero>
<fpage>193</fpage>
<lpage>201</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442013000100015&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442013000100015&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442013000100015&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p><![CDATA[The use of alizarin red S (ARS) marked tilapias could provide valuable fisheries management information to evaluate fish stocking events and may facilitate aquaculture management practices. As a new technique in fishes, the aim of this study was to compare and evaluate the chemical marks produced in tilapia juveniles by ARS through two treatments: 1) 12 hours of immersion and 2) immersion after osmotic induction. This was analyzed at three concentrations: 50, 75 and 100mg/l, and in three structures: otoliths, fish scales and caudal fin rays of Oreochromis niloticus juveniles. After three culture months 80% of specimens were analyzed and significant differences (p<0.05) in mark intensity were detected between treatments for otoliths and fin rays, but not for fish scales. Significant differences between concentrations were found for the 12h immersion treatment, while no significant differences were detected with osmotic induction. Our results showed that marks appeared at all concentrations, and none of the concentrations produced weak marks. Osmotic induction had a greater mortality than the 12h immersion procedure. After eight culture months the rest of the specimens were analyzed and the mark permanence was observed in all cases. According to the present results we recommend the marking process of 12h immersion treatment at 100mg/L concentration.]]></p></abstract>
<abstract abstract-type="short" xml:lang="es"><p><![CDATA[El uso de alizarina roja S (ARS) para marcar tilapias podría proporcionar información valiosa para el manejo de su pesquería. Para evaluar pesquerías acuaculturales manejadas con siembras o repoblamientos de peces se comparó y evaluó la marca producida por la alizarina roja S, empleando dos tratamientos: 1) Inmersión en ARS durante 12h; e 2) Inmersión en ARS después de un choque osmótico. El análisis se realizó a tres concentraciones: 50, 75 y 100mg/l y en tres estructuras: otolitos, escamas y radios de la aleta caudal de Oreochromis niloticus. Ochenta por ciento de los ejemplares fueron cultivados durante tres meses y analizados posteriormente. Los resultados mostraron diferencias entre las concentraciones de la marca para el tratamiento de 12h de inmersión mientras que no hubo diferencias entre las concentraciones para el tratamiento con inducción osmótica. Se encontraron diferencias en la intensidad de la marca entre los tratamientos para otolitos y radios de las aletas pero para las escamas no hubo diferencias significativas. Todas las concentraciones produjeron marcas (desde débiles a intensas), sin embargo la concentración de 100mg/l no produjo marcas débiles. El tratamiento por inducción osmótica presentó mayores niveles de mortalidad. Después de ocho meses de cultivo el resto de los ejemplares fueron analizados y se observó la permanencia de las marcas en todos los casos. En vista de lo anterior, para los propósitos de marcaje se recomienda el uso del tratamiento de inmersión por 12h y una concentración de 100mg/l.]]></p></abstract>
<kwd-group>
<kwd lng="en"><![CDATA[dye]]></kwd>
<kwd lng="en"><![CDATA[tilapia]]></kwd>
<kwd lng="en"><![CDATA[fish stocking]]></kwd>
<kwd lng="en"><![CDATA[chemical mark]]></kwd>
<kwd lng="en"><![CDATA[stock enhancement]]></kwd>
<kwd lng="en"><![CDATA[alizarin red]]></kwd>
<kwd lng="es"><![CDATA[pigmento]]></kwd>
<kwd lng="es"><![CDATA[tilapia]]></kwd>
<kwd lng="es"><![CDATA[siembra de peces]]></kwd>
<kwd lng="es"><![CDATA[marcaje químico]]></kwd>
<kwd lng="es"><![CDATA[mejoramiento pesquero]]></kwd>
</kwd-group>
</article-meta>
</front><body><![CDATA[ <div style="text-align: justify;">     <div style="text-align: center;"><font style="font-weight: bold;"  size="4"><span style="font-family: verdana;">Evaluation of marking efficiency of different alizarin red S concentrations on body fish structures in </span></font><font size="4"><span style="font-family: verdana;"><span  style="font-style: italic;">Oreochromis niloticus</span></span></font><font  style="font-weight: bold;" size="4"><span style="font-family: verdana;"> (Perciformes: Cichlidae) juveniles</span></font><br  style="font-family: verdana;"> </div> <br style="font-family: verdana;">     <div style="text-align: center;"><font size="2"><span  style="font-family: verdana;">Ana L. Ib&aacute;&ntilde;ez<sup><a href="#1">1</a><a name="2"></a>*</sup>, Antonio Rodr&iacute;guez-Canto<a href="#1"><sup>1</sup></a>, Jasm&iacute;n Cort&eacute;s-Mart&iacute;nez<a href="#1"><sup>1</sup></a> &amp; Jos&eacute; L. Garc&iacute;a-Calder&oacute;n<a href="#1"><sup>1</sup></a></span></font><br  style="font-family: verdana;"> </div> <font size="2"><span style="font-family: verdana;">    <br> <a name="Correspondencia2"></a>*<a href="#Correspondencia1">Direcci&oacute;n para correspondencia:</a><br style="font-family: verdana;"> </span></font><font style="font-weight: bold;" size="3"><span  style="font-family: verdana;"></span></font> <hr style="width: 100%; height: 2px;"><font style="font-weight: bold;"  size="3"><span style="font-family: verdana;">Abstract</span></font><br  style="font-family: verdana;"> <br style="font-family: verdana;"> <font size="2"><span style="font-family: verdana;">The use of alizarin red S (ARS) marked tilapias could provide valuable&nbsp; fisheries management information to evaluate fish stocking events and may facilitate aquaculture management practices. As a new technique in fishes, the aim of this study was to compare and evaluate the chemical marks produced in tilapia juveniles by ARS through two treatments: 1) 12 hours of immersion and 2) immersion after osmotic induction. This was analyzed at three concentrations: 50, 75 and 100mg/l, and in three structures: otoliths, fish scales and caudal fin rays of <span  style="font-style: italic;">Oreochromis niloticus</span> juveniles. After three culture months 80% of specimens were analyzed and significant differences&nbsp; (p&lt;0.05) in mark intensity were detected between treatments for otoliths and fin rays, but not for fish scales. Significant differences between concentrations were found for the 12h immersion treatment, while no significant differences were detected with osmotic induction. Our results showed that marks appeared at all concentrations, and none of the concentrations produced weak marks. Osmotic induction had a greater mortality than the 12h immersion procedure. After eight culture months the rest of the specimens were analyzed and the mark permanence was observed in all cases. According to the present results we recommend the marking process of 12h immersion treatment at 100mg/L concentration. </span></font><br  style="font-family: verdana;"> <br style="font-family: verdana;"> <font size="2"><span style="font-family: verdana;"><span  style="font-weight: bold;">Key words:</span> dye, tilapia, fish stocking, chemical mark, stock enhancement, alizarin red.</span></font><br  style="font-family: verdana;"> <br style="font-family: verdana;"> <font style="font-weight: bold;" size="3"><span  style="font-family: verdana;">Resumen</span></font><br  style="font-family: verdana;"> <br style="font-family: verdana;"> <font size="2"><span style="font-family: verdana;">El uso de alizarina roja S (ARS) para marcar tilapias podr&iacute;a proporcionar informaci&oacute;n valiosa para el manejo de su pesquer&iacute;a. Para evaluar pesquer&iacute;as acuaculturales manejadas con siembras o repoblamientos de peces se compar&oacute; y evalu&oacute; la marca producida por la alizarina roja S, empleando dos tratamientos: 1) Inmersi&oacute;n en ARS durante 12h; e 2) Inmersi&oacute;n en ARS despu&eacute;s de un choque osm&oacute;tico. El an&aacute;lisis se realiz&oacute; a tres concentraciones: 50, 75 y 100mg/l y en tres estructuras: otolitos, escamas y radios de la aleta caudal de <span style="font-style: italic;">Oreochromis niloticus.</span> Ochenta por ciento de los ejemplares fueron cultivados durante tres meses y analizados&nbsp; posteriormente. Los resultados mostraron&nbsp; diferencias entre las concentraciones de la&nbsp; marca para el tratamiento de 12h de inmersi&oacute;n mientras que no hubo diferencias entre las concentraciones para el tratamiento con inducci&oacute;n osm&oacute;tica. Se encontraron&nbsp; diferencias en la intensidad de la marca&nbsp; entre&nbsp; los tratamientos para otolitos y radios&nbsp; de las aletas pero para las escamas no hubo&nbsp; diferencias significativas. Todas las&nbsp; concentraciones produjeron marcas (desde&nbsp; d&eacute;biles a intensas), sin embargo la concentraci&oacute;n de 100mg/l no produjo marcas d&eacute;biles. El tratamiento por inducci&oacute;n osm&oacute;tica present&oacute; mayores niveles de mortalidad. Despu&eacute;s de ocho meses de cultivo el resto de los ejemplares fueron analizados y se observ&oacute; la permanencia de las marcas en todos los casos. En vista de lo anterior, para los prop&oacute;sitos de marcaje se recomienda el uso del tratamiento de inmersi&oacute;n por 12h y una concentraci&oacute;n de 100mg/l.</span></font><br style="font-family: verdana;"> <br style="font-family: verdana;"> <font size="2"><span style="font-family: verdana;"><span  style="font-weight: bold;">Palabras clave:</span> pigmento, tilapia, siembra de peces, marcaje qu&iacute;mico, mejoramiento pesquero.</span></font><font  size="2"><span style="font-family: verdana;"></span></font>    <br>     <hr style="width: 100%; height: 2px;"><font size="2"><span      style="font-family: verdana;"></span></font><font size="2"><span      style="font-family: verdana;">According to FAO     (2009), worldwide     percapita aquaculture fish consumption has rapidly increased between     ]]></body>
<body><![CDATA[1970 and 2006, from 0.7 to 7.8kg (with an annual increase rate of     6.9%); tilapia culture has been gradually expanding since 1970     and&nbsp; occupies&nbsp; the&nbsp; second&nbsp; place in worldwide     aquaculture just after shrimp. Hatchery-bred fish (fingerling     production) has been developed to supplement and support the rapidly     depleting stocks of freshwater environments (Brown &amp; Day 2002). The     ability to discriminate between wild and hatchery-produced fish     fingerlings is vital to evaluate the efficiency and sustainability of     stock enhancement. A variety of methods for identification of     hatchery-produced fish have been developed including tagging, chemical     ]]></body>
<body><![CDATA[marking,     and genetic analysis (Nielsen 1992). For age determination purposes,     the chemical (e.g. ARS) marking of otoliths has provided a good     validation method (Bell 2001). The most reliable validation comes from     comparing the increment in otolith size in fish of known ages. Chemical     tagging by bath immersion is an efficient method in fish, since     individual handling is not required and it is possible to mark numerous     specimens in the same batch at low costs (Mauk 2008). These methods are     used to produce marks in otoliths or other calcified structures by     immersion in fluorescent colorants, such as oxytetracycline (OTC),     ]]></body>
<body><![CDATA[calceine or ARS during a predetermined exposure period (6-12h). </span></font><br      style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">&nbsp;</span></font><br      style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">Different chemicals     have been     successfully used for fish and specifically, several for cichlids.     Klesius <span style="font-style: italic;">et al.</span> (2006), used     calceine to discriminate between a     vaccinated population of tilapia (<span style="font-style: italic;">Oreochromis     ]]></body>
<body><![CDATA[niloticus L.</span>) and other     not treated populations. They found a detectable fluorescent band     following a four- hour-bath in 500mg/l. Egger (2004) used tetracycline     to validate the pattern of increment in the otoliths of <span      style="font-style: italic;">Tropheus moorii</span>     Boulenger (1898), a native cichlid of Lake Tanganyika, where marking     involved individually injecting each fish with 10mm (4.4mg/l) of     tetracycline solution. Likewise, Barker &amp; McKaye (2004), marked     juveniles of the cichlid <span style="font-style: italic;">Amphilophus</span>,     with OTC     ]]></body>
<body><![CDATA[concentrations&nbsp; of&nbsp; 200,&nbsp; 400&nbsp; and 600mg/l in four,     eight or 16h treatments; as a result they defined     an optimal concentration of 600mg/l after an eight hours     bath. Besides, Mauk (2008), worked with OTC to assess the effectiveness     of marking techniques in otoliths of Palmetto Bass (striped bass     hybrid) that live in hard waters, using concentrations of 500 and     700mg/l during a six hour fixed period. Marks were detectable in 63 and     74% of individuals, respectively.</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     ]]></body>
<body><![CDATA[<font size="2"><span style="font-family: verdana;">Immersion in a dye,     combined with     osmotic induction, is a technique consisting of a brief salt bath prior     to immersion in a fluorescent dye. This procedure dramatically reduces     color absorption time, in comparison to conventional methods of     marking. Simplicity and speed of osmotic induction make this method     especially suitable for marking fish on a large scale where cost and     logistics largely determine the utility of marking methods (Mohler     2003). Crook <span style="font-style: italic;">et al.</span> (2007     &amp; 2009) also evaluated osmotic methods     ]]></body>
<body><![CDATA[for golden perch <span style="font-style: italic;">Macquaria ambigua </span>using     ARS. They found that the     osmotic induction-marked fish possessed more intense marks and that     these marks remained visible nine months after treatment. Mark     production using ARS it is consider as nontoxic for several species     (Lucas <span style="font-style: italic;">et al.</span> 2008, Simon <span      style="font-style: italic;">et al.</span> 2009) and human consumption;     also is     acceptable to the public for commercial use (Rothlisberg &amp; Preston     1992). </span></font><br style="font-family: verdana;">     ]]></body>
<body><![CDATA[<br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">In Mexico, the     federal government     supports 40 fish farms that produce, on average, 111 million fry per     year, 48% of which are tilapia. Although culture-based fisheries in     Mexico are almost one century old, there is very little information     available as to their influence on fish production&nbsp;     (Ib&aacute;&ntilde;ez&nbsp; 2004,&nbsp; Ib&aacute;&ntilde;ez&nbsp;     <span style="font-style: italic;">et&nbsp; al.</span> 2011). The     release of ARS-marked tilapias could provide     ]]></body>
<body><![CDATA[valuable fisheries management information and assist in evaluating     release strategies which optimize survival, and migration patterns that     affect productivity and inter-breeding with wild fish. </span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">The aim of this     study was to     compare and evaluate the chemical mark produced by ARS through two     treatments: 1) 12h of immersion and 2) immersion after osmotic     induction. This was analyzed using three different concentrations: 50,     ]]></body>
<body><![CDATA[75 and 100mg/l; and evaluating their effect in three body fish     structures: otoliths, fish scales and rays from the caudal fin.</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font style="font-weight: bold;" size="3"><span      style="font-family: verdana;">Material and Methods</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;"><span      style="font-weight: bold;">Fish transportation     ]]></body>
<body><![CDATA[and     acclimation:</span> Juveniles of the Stirling strain <span      style="font-style: italic;">of Oreochromis niloticus     L.</span> were obtained from a fish farm at Zacatepec, in the     State&nbsp; of     Morelos,&nbsp; Central South Mexico. They were transported to the     Fisheries laboratory at the Metropolitan University in Mexico City, in     plastic bags filled with fresh water and oxygen. Fish were acclimated     for seven weeks in an aerated 200-l tank with a Fluval filter model 305     (volume of 710 l/h) and fed to satiation twice a day each day with     ]]></body>
<body><![CDATA[tilapia pellets (32% of protein). They were then transferred to a     recirculating system with a matured biofilter and 14 plastic aquariums,     each of a 12-l capacity. Temperature was controlled with a thermostat     of 1 000W located in the biofilter container. Air was provided by a     blower net system. Seven individuals were housed in each aquarium for     one week prior to treatment. A total of 112 fish were analyzed; 56 per     treatment: two replicates of seven fish (14 specimens by each of three     chemical concentrations), and 14 specimens were used for control     analysis. The total mean length of these juveniles was     6.7&plusmn;0.63cm (range, 5.0-7.8cm) while total mean weight was     ]]></body>
<body><![CDATA[3.8&plusmn;1.62g (range, 1.7-6.9g) at the beginning of the experiment     when fish was two months old. To avoid infections, methyl blue and salt     were occasionally added to the reservoir of the recirculation system.     Water temperature (&ordm;C), salinity (PSU), total dissolved solids     (g/l), oxygen (mg/l) and pH, were daily measured using an YSI     multimeter model MSP 556. </span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;"><span      style="font-weight: bold;">Experimental design:</span>     ]]></body>
<body><![CDATA[Two     experimental treatments were evaluated. In treatment 1, fish were     removed&nbsp; from&nbsp; aquaria&nbsp; and&nbsp; immersed in 10-l     solutions of 50, 75 and 100mg/l ARS (Baker Analyzed&reg;Reagent) for a     period of 12h. Treatment 2 consisted of a previous osmotic induction,     following Crook <span style="font-style: italic;">et al.</span> (2007)     protocol; for this, fish were immersed in     a 5% sea-salt solution for five minutes, followed by a five seconds     rinse in aquarium water, and then, a 10 minute immersion in the ARS     solution of 10-l with the respective 50, 75 and 100mg/l concentration.     ]]></body>
<body><![CDATA[The salt was from &#8220;Salinas del M&aacute;rquez&#8221; brand obtained from     evaporation of the Pacific coast water of Salina Cruz, Oaxaca,     M&eacute;xico. The salt solution was prepared by dissolving 500g of     commercial sea salt in a 10-l of fresh water. As unmarked controls, an     additional group of seven fish was immersed in a 5% salt solution for     5min without immersion in ARS solution. Aerated 10-l buckets were used     in all treatments; each replicate was manipulated in a different bucket.</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">After the marking     ]]></body>
<body><![CDATA[process, all fish     from different treatments and replicates were maintained and fed to     satiation for three months in different aquaria in a recirculation     system. Afterwards, from October 2009, five fish (from the seven) from     each treatment were sacrificed and examined; all the results analysis     showed here correspond to these five specimens. Additionally, to assess     the permanence of the mark the two remaining fish were examined five     months later to assess the longevity     of the mark. This accounted for a commercial size that is     normally reached after approximately eight months following     ]]></body>
<body><![CDATA[stocking. Fish were euthanized by adding cold water to produce a     gentle death. Afterwards, total length and total weight were measured,     and scales, otoliths and caudal fins were obtained.</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;"><span      style="font-weight: bold;">Structure     preparation and     examination:</span> Scales were cleaned and placed between two glass     slides     ]]></body>
<body><![CDATA[for observation. Caudal fin rays were placed on an excavated slide     glass. Otoliths were sanded in&nbsp; the sagittal plane and fixed on an     excavated glass. Structures were examined using an epifluorescence     microscope (Zeiss&nbsp; Axio&nbsp; Start)&nbsp; fitted&nbsp; with&nbsp;     a&nbsp; TXR&nbsp; filter set. The TXR filter set has an excitation     filter BP560/40, beamsplitter FT585 and with emission BP630/75.     Structures were examined in a darkened room to reduce external light     effect, and digital photographs were taken with four-x magnification     using a Canon camera.</span></font><br style="font-family: verdana;">     <br style="font-family: verdana;">     ]]></body>
<body><![CDATA[<font size="2"><span style="font-family: verdana;">To&nbsp;     assign&nbsp; a&nbsp;     mark&nbsp; intensity&nbsp; value&nbsp; based on&nbsp; an&nbsp;     ordinal&nbsp; scoring&nbsp; system,&nbsp; the&nbsp; following five     classifications were established: no mark, weak mark, moderate mark,     intense mark and very bright mark (modified from Crook <span      style="font-style: italic;">et al.</span> 2007). In     order to determine significant differences between the ARS     concentrations used, Kruskal-Wallis tests were     used; furthermore, a Mann-Whitney U-test was used to determine     ]]></body>
<body><![CDATA[significant     differences&nbsp; in&nbsp; mark intensity between the     ARS treatment groups and between concentration     replicates. Differences were considered significant at p&lt;0.05.</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">Fish were treated in     compliance     with the regulations and protocols of our University (Lineamientos para     la conducci&oacute;n &eacute;tica de la investigaci&oacute;n, la     ]]></body>
<body><![CDATA[docencia y la difusi&oacute;n en la Divisi&oacute;n de Ciencias     Biol&oacute;gicas y de la Salud de la Universidad Aut&oacute;noma     Metropolitana (http://cbs.izt.uam.mx/informacion/consejo_     divisional/index.htm). </span></font><br style="font-family: verdana;">     <br style="font-family: verdana;">     <font style="font-weight: bold;" size="3"><span      style="font-family: verdana;">Results</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">The results shown     ]]></body>
<body><![CDATA[here are from the     specimens maintained for three months, while in the mark permanence     subtitle are the results from fish eight months old. </span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;"><span      style="font-weight: bold;">Mortality:</span>&nbsp;     Mortalities     reached 12.24% in the 12h ARS immersion treatment (Treatment 1), and     22.4% in the osmotic induction- ARS immersion treatment (Treatment 2).     ]]></body>
<body><![CDATA[In treatment 1,&nbsp; fish&nbsp; remained&nbsp; at&nbsp; the&nbsp;     bottom&nbsp; of the buckets during chemical exposure and no excessive     movements were observed. Mortalities for this treatment group occurred     during the subsequent growth period, but no mortality was observed     during chemical exposure itself. For treatment 2, the fins of fish     immersed in the&nbsp; 5% salt solution turned to a noticeable white     color and many individuals lost     equilibrium and floated to the&nbsp;     surface; most of these were stressed. Highest mortalities     in this treatment occurred during the first week after this osmotic     ]]></body>
<body><![CDATA[treatment. The stress behavior occurred only in the osmotic treatment,     suggesting that the cause was the salt rather than the ARS.</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;"><span      style="font-weight: bold;">General mark results     for both     treatments:</span> Moderate and intense marks were the most frequent     results     in both treatments (38.8 and 36.1%, respectively) for the whole period.     ]]></body>
<body><![CDATA[Caudal fins depicted the highest mark intensity followed by those in     the otoliths. The control treatment for the 12-hour immersion showed no     marks, whilst the osmotic induction control exhibited autofluorescence     in all three structures (<a href="/img/revistas/rbt/v61n1/a15i1.jpg">Figs.     1</a>, <a href="/img/revistas/rbt/v61n1/a15i2.jpg">2</a>). Mark     intensity was not     significantly different between duplicates for the two treatments     (Treatment 1: p=0.509; Treatment 2: p=0.964). There were significant     differences between treatments for caudal fin&nbsp; (p=0.001) and     otoliths (p=0.019), but not for scales (p=0.302). Significant     ]]></body>
<body><![CDATA[differences were found for ARS concentrations in scales (p=0.001). </span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;"><span      style="font-weight: bold;">Treatment 1:</span> Mark     intensity in the     12h immersion treatment of otoliths showed wide variability, while most     scales had moderate intensity marks (74.1%). Likewise, most caudal fin     marks were intense (63.0%). It is important to mention that the 20%     frequency in the no mark results showed in <a     ]]></body>
<body><![CDATA[ href="/img/revistas/rbt/v61n1/a15i1.jpg">figure 1a</a>, applies to     control specimens. In the 50mg/L batch, 62.5% of the marks were     moderate while very bright marks were not observed. Most of the 75mg/l     concentration batch showed either intense (57.7%) or moderate marks     (30.8%); while intense (42.1%) and very bright marks (31.6%) increased     in the 100mg/l group. At this higher concentration,     no weak marks were formed (<a href="/img/revistas/rbt/v61n1/a15i1.jpg">Fig.     1b</a>). This treatment showed differences     between 50 and 75mg/l and also between 50 and 100mg/l for otoliths     (p=0.003 and p=0.001, respectively). Also, differences in ARS     ]]></body>
<body><![CDATA[concentrations, for caudal rays in the 12-hour treatment, were notable     between 75 and 100mg/l, and 50 and 100mg/l (p&lt;0.000 and p=0.001,     respectively). </span></font><br style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;"><span      style="font-weight: bold;">Treatment 2:</span> The     osmotic induction     treatment did not produce very bright marks in any case (<a      href="/img/revistas/rbt/v61n1/a15i2.jpg">Figs. 2</a>, <a      href="/img/revistas/rbt/v61n1/a15i1.jpg">3</a>);     ]]></body>
<body><![CDATA[most of the marks were moderate or intense. This treatment did not     produce differences among concentrations in otoliths and caudal fin     rays (p=0.09). Approximately, 50% of otoliths and scales from osmotic     immersion showed moderate marks (28.6%), followed by     intense marks (23.8%), while 52.3% of caudal fin depicted intense and     28.6% moderate     marks (<a href="/img/revistas/rbt/v61n1/a15i2.jpg">Fig. 2a</a>). At 50     and 75mg/l most marks were moderate with 83.3%     and 73.3%, respectively. On the other hand, at 100mg/l, 83.3% of the     marks were intense.</span></font><br style="font-family: verdana;">     ]]></body>
<body><![CDATA[<br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;"><span      style="font-weight: bold;">Environmental     parameters:</span> During     the eight-month culture period, water temperature ranged from 15.9 to     27.0&deg;C (21.0&plusmn;2.3), pH from&nbsp; 8.9-9.3&nbsp;     (9.3&plusmn;0.3),&nbsp; oxygen&nbsp; ranged&nbsp; from 4.7 to 6.4mg/l     (5.2&plusmn;1.0), salinity from 5.0 to 8.2 PSU (6.5&plusmn;1.0) and     total dissolved solids from 3.4 to 8.6g/l (7.4&plusmn;1.3). Temperature     and oxygen, in particular, fluctuated widely during the day. Most of     ]]></body>
<body><![CDATA[these variations were due to the time of day that samples were taken.     Additionally, temperature variation was&nbsp;     also&nbsp; due to a harsh winter, which demanded artificial heating to     better represent conditions the fish would have experienced in the     wild, for the eight months period. After three months, fish total     length range was between 5.3-9.2cm, with a mean of 7.3&plusmn;0.85.</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;"><span      style="font-weight: bold;">Mark permanence: </span>As     ]]></body>
<body><![CDATA[it was     mentioned, two remaining fish from different treatments and dye     concentrations were examined at eight months age. The three structures     (otoliths, fins and scales) of the two treatments were checked for     marks under a UV light microscope. In all cases (100%), marks were     visible, nevertheless it was not evaluated the mark intensity value.     Although the small number of specimens investigated does not permit     statistical analysis by treatment and concentrations. The visibility of     the marks after eight months clearly indicates that the chosen methods     allow for recognition of released individuals.</span></font><br     ]]></body>
<body><![CDATA[ style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">In summary, mark     intensity did not     differ between replicates. There were differences between treatments in     the results obtained for caudal fins and otoliths, but not for scales.     ARS concentrations only produced different intensities in treatment 1.     Osmotic induction treatment did not result in very bright marks.     Different ARS concentrations produced marks going from weak to intense     with the exception of the 100mg/l, which did not produce weak marks.</span></font><br     ]]></body>
<body><![CDATA[ style="font-family: verdana;">     <br style="font-family: verdana;">     <font style="font-weight: bold;" size="3"><span      style="font-family: verdana;">Discussion</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">In this study,     mortality resulted     greater than in other similar studies (Leips <span      style="font-style: italic;">et al.</span> 2001, Bashey 2004,     ]]></body>
<body><![CDATA[Crook <span style="font-style: italic;">et al.</span> 2007, Crook <span      style="font-style: italic;">et al.</span> 2009).&nbsp; Size&nbsp;     of&nbsp;     fish&nbsp; could&nbsp; be&nbsp; an&nbsp; explanation of&nbsp;     these&nbsp; results&nbsp; since, in those studies,&nbsp; fish were     smaller and we observed that small fish were less vulnerable to the     osmotic immersion shock. As a consequence of exposing the tilapia to     high salinity water, the fish cells loose a certain amount of water.     When the tilapias return to the ARS solution, the consequential osmotic     differences resulted in the rapid uptake of dye, as water was replaced     ]]></body>
<body><![CDATA[via osmosis through the skin and gills (Mohler 2003); this generated an     efficient utilization of dye independently of the ARS concentrations,     and the reduction in immersion time (Mohler 2003, Negus &amp; Tureson     2004) and high-quality marks (Crook <span style="font-style: italic;">et     al.</span> 2007). Nevertheless, osmotic     induction marking with ARS produced more mortality than the 12-hour     immersion treatment; we do not discard that lower salt immersion times     might produce less mortality. According to Crook <span      style="font-style: italic;">et al.</span> (2007)     increasing the immersion time beyond 3.5min may not necessarily improve     ]]></body>
<body><![CDATA[the mark quality in golden perch fingerlings. Although osmotic     induction marking with ARS requires supplementary testing, we believe     that has significant potential since is less time consuming, however,     the exploration of longer or shorter periods of immersion in both the     salt and ARS solutions that could enhance the intensity of the mark     should be experimented. </span></font><br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">&nbsp;</span></font><br      style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">This experiment has     demonstrated     ]]></body>
<body><![CDATA[the promising use of ARS to mark tilapia by immersion and by osmotic     induction techniques; nevertheless, several issues must be addressed,     e.i. according to Simon <span style="font-style: italic;">et al.</span>     (2009) the growth and mortality of     European glass eel <span style="font-style: italic;">Anguilla anguilla</span>     192 days after marking with     oxytetracycline and alizarin red S were not significantly different     between the two treatments and not different to the unmarked <span      style="font-style: italic;">A.     anguilla.</span> The study provided evidence that both marking methods     ]]></body>
<body><![CDATA[(OTC     and ARS) fulfill the capture&#8211; recapture assumption of no effect on     growth and survival within the glass-eel <span      style="font-style: italic;">A. anguilla</span> stage. Therefore,     it must be studied the species specific effects of the marking     techniques on growth and mortality rates.</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">The affinity of the     ARS to calcium     ]]></body>
<body><![CDATA[could explain that the caudal fin ray was the structure that showed the     best mark intensities, followed by otoliths and fish scales, since fin     rays and otoliths are constructed by calcareous elements (Estrada&nbsp;     1977),&nbsp; while&nbsp; fish&nbsp; scales&nbsp; consist&nbsp; of an     outer, initially non-calcified matrix (Wallin 1957). The present     results shows that fin rays of tilapia is a good structure for tagging     revision, since fish mark could be evaluated without fish sacrifice.</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">Bashey     ]]></body>
<body><![CDATA[(2004) and Crook <span style="font-style: italic;">et al.</span>     (2009) also reported the presence of     weak marks in non-exposed controls using osmotic immersion     treatments.&nbsp; Even so, auto-fluorescence does not present a problem     because it is easily distinguished from chemical marks. Natural     fluorescence is due in large part to substances like flavins,     porphyrins, lipofuscin and (in plants) chlorophyll. Lipofuscin is the     breakdown product of old red blood cells with fluorescent red under     green excitation. Elastin and collagen also could produce     autofluorescence. Elastin contains several fluorophores, one of which     ]]></body>
<body><![CDATA[is a crosslinking&nbsp; tricarboxylic amino     acid with a pyridinium ring (Deyl <span style="font-style: italic;">et     al.</span> 1980). This is a similar     fluorophore to the one found in collagen. The elastine in presence of a     saline solution, even for 10min followed by a 5min wash, shifts the     usual green autofluorescence emission of elastin into a red emission     (Neumann &amp; Detlef 2002). The mentioned substances could have     produced the autofluorescence in the control specimens of shock osmotic     treatment; nevertheless, to be certain it will be necessary to design a     particular study to explore this aim.</span></font><br     ]]></body>
<body><![CDATA[ style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">Mark permanence is     decisive in dye     election. In this study ARS showed eight months permanence. According     to Simon <span style="font-style: italic;">et al.</span> (2009) fish     marks with ARS and oxytetracycline were     clearly visible after a period of two years in specimens of <span      style="font-style: italic;">Anguilla     anguilla.</span> The visibility of the marks eight months after marking     ]]></body>
<body><![CDATA[definitely indicates that the chosen methods allocate for recognition     of released individuals. ARS-marked larvae and juveniles of other fish     species as <span style="font-style: italic;">Macquaria ambigua</span>     and <span style="font-style: italic;">Thymallus thymallus</span> has     been retained     from months to years (Beckman &amp; Schulz 1996, Crook <span      style="font-style: italic;">et al.</span> 2007).</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">The concentrations     ]]></body>
<body><![CDATA[of ARS solutions     had an effect in the mark intensity, higher concentrations produce     better marks than lower concentrations. The selection of diverse     pigment concentrations must be made taking into consideration the     importance of mark quality in opposition to the expenses and logistics     of the marking method. These decisions will be related to the     particular aims and restrictions of the study or marking agenda.</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">The present results     ]]></body>
<body><![CDATA[indicate     that&nbsp; ARS facilitate easy and rapid mass-marking of big number of     tilapia and as well, could be used for fisheries assessment. The     chemical marks offer suitable modes of induction, long-term marks over     time. Fishes fit in ARS into calcifying tissues while growing within     some hours and as a result, the mark can be recognized under UV light     as a fluorescent mark which can facilitate the growth rate and relative     age at recapture of the fish.</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     ]]></body>
<body><![CDATA[<font size="2"><span style="font-family: verdana;">In conclusion, both     treatments and     all concentrations produced useful marks, but the 100mg/treatment did     not produce weak marks. Control in the 12-hour immersion did not mark     while auto-fluorescence appeared in the osmotic treatment control. The     osmotic treatment resulted in greater mortality rates than the 12h     immersion; thus, a concentration of 100mg/l combined with a 12h     immersion in ARS can be recommended for hatchery produced <span      style="font-style: italic;">O. niloticus</span>     in this size range. </span></font><br style="font-family: verdana;">     ]]></body>
<body><![CDATA[<br style="font-family: verdana;">     <font style="font-weight: bold;" size="3"><span      style="font-family: verdana;">Acknowledgments</span></font><br      style="font-family: verdana;">     <br style="font-family: verdana;">     <font size="2"><span style="font-family: verdana;">We thank the     valuable help in the     English adaptation to Anselmo Galindo Molina and to three anonymous     referees who really improved the first version of the manuscript.     Financial support was obtained from the Universidad Aut&oacute;noma     ]]></body>
<body><![CDATA[Metropolitana Iztapalapa. </span></font><br      style="font-family: verdana;">     <br> <hr style="width: 100%; height: 2px;">    <!-- ref --><br> <font style="font-weight: bold;" size="3"><span  style="font-family: verdana;">References</span></font><br  style="font-family: verdana;"> <br style="font-family: verdana;"> <font size="2"><span style="font-family: verdana;">Barker, M.J. &amp; R.K. McKaye. 2004. Immersion marking of juvenile midas Cichlids with Oxytetracycline. N. Am. J. Fish. Manage. 24: 262-269.    &nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;[&#160;<a href="javascript:void(0);" onclick="javascript: window.open('/scielo.php?script=sci_nlinks&ref=1822794&pid=S0034-7744201300010001500001&lng=','','width=640,height=500,resizable=yes,scrollbars=1,menubar=yes,');">Links</a>&#160;]<!-- end-ref --><!-- ref --></span></font><br  style="font-family: verdana;"> <br style="font-family: verdana;"> <font size="2"><span style="font-family: verdana;">Bashey, F. 2004. 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M&eacute;xico, D.F. 09340, M&eacute;xico; ana@xanum.uam.mx</span></font>    <br> <font size="2"><span style="font-family: verdana;">Antonio Rodr&iacute;guez-Canto: </span></font><font size="2"><span  style="font-family: verdana;">Universidad Aut&oacute;noma Metropolitana-Iztapalapa, Departamento de Hidrobiolog&iacute;a, Av. San Rafael Atlixco 186, Col. Vicentina. M&eacute;xico, D.F. 09340, M&eacute;xico; roca@xanum.uam.mx</span></font>    ]]></body>
<body><![CDATA[<br> <font size="2"><span style="font-family: verdana;">Jasm&iacute;n Cort&eacute;s-Mart&iacute;nez: </span></font><font size="2"><span  style="font-family: verdana;">Universidad Aut&oacute;noma Metropolitana-Iztapalapa, Departamento de Hidrobiolog&iacute;a, Av. San Rafael Atlixco 186, Col. Vicentina. M&eacute;xico, D.F. 09340, M&eacute;xico; hada_30@hotmail.com</span></font>    <br> <font size="2"><span style="font-family: verdana;">Jos&eacute; L. Garc&iacute;a-Calder&oacute;n:</span></font><font size="2"><span  style="font-family: verdana;"> Universidad Aut&oacute;noma Metropolitana-Iztapalapa, Departamento de Hidrobiolog&iacute;a, Av. San Rafael Atlixco 186, Col. Vicentina. M&eacute;xico, D.F. 09340, M&eacute;xico; jlgc@xanum.uam.mx    <br> </span></font><font size="2"><span style="font-family: verdana;"><a  name="1"></a><a href="#2">1</a>. Universidad Aut&oacute;noma Metropolitana-Iztapalapa, Departamento de Hidrobiolog&iacute;a, Av. San Rafael Atlixco 186, Col. Vicentina. M&eacute;xico, D.F. 09340, M&eacute;xico; ana@xanum.uam.mx, roca@xanum.uam.mx, hada_30@hotmail.com, jlgc@xanum.uam.mx</span></font>    <br> <font size="2"><span style="font-family: verdana;"></span></font> <hr style="width: 100%; height: 2px;">     <div style="text-align: center;"><font size="2"><span  style="font-family: verdana;"></span></font><font  style="font-weight: bold;" size="2"><span style="font-family: verdana;">Received 13-II-2012.&nbsp;&nbsp; &nbsp;Corrected 09-VIII-2012.&nbsp;&nbsp; &nbsp;Accepted 13-IX-2012. </span></font>    <br> </div> </div>      ]]></body><back>
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