<?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>0121-3709</journal-id>
<journal-title><![CDATA[ORINOQUIA]]></journal-title>
<abbrev-journal-title><![CDATA[Orinoquia]]></abbrev-journal-title>
<issn>0121-3709</issn>
<publisher>
<publisher-name><![CDATA[Instituto de Investigaciones de la Orinoquia Colombiana]]></publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0121-37092013000100009</article-id>
<title-group>
<article-title xml:lang="es"><![CDATA[Evaluación del cloruro de sodio, eugenol y zeolita en el confinamiento de Ancistrus triradiatus]]></article-title>
<article-title xml:lang="en"><![CDATA[Evaluation of the use of sodium chloride, eugenol, and zeolite in confinement of Ancistrus triradiatus]]></article-title>
<article-title xml:lang="pt"><![CDATA[Avaliação decloreto de sódio, o eugenol ezeolite em transporte Ancistrus triradiatus]]></article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Ramírez - Duarte]]></surname>
<given-names><![CDATA[Wilson F.]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Pineda - Quiroga]]></surname>
<given-names><![CDATA[Carolina]]></given-names>
</name>
<xref ref-type="aff" rid="A02"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Martínez - Rueda]]></surname>
<given-names><![CDATA[Nhora]]></given-names>
</name>
<xref ref-type="aff" rid="A03"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Eslava - Mocha]]></surname>
<given-names><![CDATA[Pedro R.]]></given-names>
</name>
<xref ref-type="aff" rid="A04"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution><![CDATA[,Universidad de los Llanos Instituto de Acuicultura de los Llanos Group on Health of Aquatic Organisms]]></institution>
<addr-line><![CDATA[ ]]></addr-line>
</aff>
<aff id="A02">
<institution><![CDATA[,Ejercicio particular  ]]></institution>
<addr-line><![CDATA[ ]]></addr-line>
</aff>
<aff id="A03">
<institution><![CDATA[,National University of Colombia School of Veterinary Medicine and Zootechny Departament of Science for Animal Production]]></institution>
<addr-line><![CDATA[Bogotá ]]></addr-line>
<country>Colombia</country>
</aff>
<aff id="A04">
<institution><![CDATA[,Universidad de los Llanos Instituto de Acuicultura de los Llanos Group on Health of Aquatic Organisms]]></institution>
<addr-line><![CDATA[ ]]></addr-line>
</aff>
<pub-date pub-type="pub">
<day>00</day>
<month>06</month>
<year>2013</year>
</pub-date>
<pub-date pub-type="epub">
<day>00</day>
<month>06</month>
<year>2013</year>
</pub-date>
<volume>17</volume>
<numero>1</numero>
<fpage>84</fpage>
<lpage>95</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http://www.scielo.org.co/scielo.php?script=sci_arttext&amp;pid=S0121-37092013000100009&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.co/scielo.php?script=sci_abstract&amp;pid=S0121-37092013000100009&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.co/scielo.php?script=sci_pdf&amp;pid=S0121-37092013000100009&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="es"><p><![CDATA[Se evaluó el uso de cloruro de sodio (1 y 2 g/L), eugenol (0.1 y 0.5 mg/L), y zeolita (7 g/L en confinamiento de 12 h y 10 g/L en el de 48 h), así como de las mezclas de cloruro de sodio más eugenol (1 g/L y0.5 mg/L, respectivamente) y eugenol más zeolita (0.5 mg/L y 7 o 10 g/L, respectivamente) en confinamiento de Ancistrus triradiatus durante periodos de 12 y 48 h. Se midieron los parámetros de calidad del agua, oxígeno disuelto, pH, temperatura, conductividad y concentraciones de amoniaco total, amonio no ionizado y nitrito. La concentración de glucosa en sangre fue medida antes de iniciar el confinamiento y a las 0, 24 y 48 horas después de terminado dicho confinamiento. También se realizó una prueba de resistencia al estrés al finalizar el periodo de confinamiento mediante la exposición de peces a una solución salina hiperosmótica durante 1 h, en la cual se registró el número de peces que mantenía el eje de nado a intervalos de 5 min; se registró la mortalidad al finalizar los periodos de confinamiento (12 y 48 horas) y la mortalidad acumulada durante los 7 días siguientes. El uso de 1 y 2 g/L de cloruro de sodio en el confinamiento de A. triradiatus durante periodos de 12 h y de 1 g/L durante periodos de 48 h incrementó la resistencia al estrés y redujo la mortalidad de los animales. El uso de eugenol o zeolita no mejoró la resistencia al estrés ni contribuyó a la reducción de la mortalidad de los animales, mientras que la exposición a las mezclas de sal más eugenol y de eugenol más zeolita incrementó la mortalidad, por lo que el uso de estas mezclas no es recomendado en operaciones de confinamiento de A. triradiatus.]]></p></abstract>
<abstract abstract-type="short" xml:lang="en"><p><![CDATA[The use of sodium chloride (1 and 2 g/L), eugenol (0.1 and 0.5 mg/L), and zeolite (clinoptilolite, 7 g/L for 12 h and 10 g/L for 48 h of confinement), and also mixtures of salt plus eugenol (1 g/L and 0.5 mg/L, respectively) and eugenol plus zeolite (0.5 mg/L and 7 or 10 g/L, respectively) were evaluated in the confinement of Ancistrus triradiatus for 12 and 48h. Water parameters as concentration of dissolved oxygen, pH, temperature, conductivity, and concentrations of total ammonia, non-ionized ammonia and nitrite were monitored. The blood glucose concentration was measured before the confinement started and at 0, 24, and 48 hours after the confinement period finished. A stress resistance test was conducted right after the confinement time was completed by exposing the fish to a hyperosmotic saline solution for one hour, recording the number of fish that maintained the swimming axis at intervals of 5 minutes. The mortality at the end of both confinement periods (12 and 48 hours), and its cumulative percentage rate during the following 7 days were also recorded. The use of sodium chloride 1 and 2 g/L in confinement times of 12 h, and 1 g/L in confinement time of 48 hours increased the resistance to confinement-induced stress, and reduced mortality of the animals. The use of eugenol and zeolite did not improve the response to the stress, nor contribute to the reduction of mortality of the animals, while exposure to the mixtures of salt plus eugenol and eugenol plus zeolite increased the mortality so they are not recommended in the confinement of A. triradiatus.]]></p></abstract>
<abstract abstract-type="short" xml:lang="pt"><p><![CDATA[Foi avaliada a utilização de cloreto de sódio (1 e 2 g/L), eugenol (0.1 e 0.5 mg/L) e zeolita (7 g/L para 12 h de confinamentoe 10 g/L em 48 h) e misturas de cloreto de sódio e eugenol (1 g/L e0.5 mg/L, respectivamente) e eugenol mais zeolita (0,5 mg/L, 7 ou 10 g/L, respectivamente) para confinamento de Ancistrus triradiatus por períodos de 12 e 48h. Parâmetros de qualidade de água foram medidos: concentração de oxigênio dissolvido, pH, temperatura, condutividade e concentração de amônia total e não ionizada e nitrito. A concentração de glicose no sangue foi medida antes e 0, 24 e 48 horas após a conclusão do período de confinamento. Um teste de estresse foi realizado no final do período de confinamento, expondo os peixes a uma salina hiperosmótica durante 1 h, sendo registrado o número de peixes que manteve o eixo de natação em intervalos de 5 min. Da mesma forma, a mortalidade foi registrada no final dos períodos de confinamento (12 e 48 horas), bem como o percentual acumulado nos 7 dias seguintes. A utilização de 1 e 2 g/L de cloreto de sódio no confinamento de A.triradiatusdurante 12 h, e 1 g/L a 48 h aumentou a resistência ao estresse e reduziu a mortalidade dos animais. O uso de zeolita ou eugenol não melhorou a resistência ao estressenem contribuiu para a redução da mortalidade dos animais, enquanto que a exposição a misturas de sal e eugenol e de eugenol e zeolita aumentou a mortalidade, de modo que o uso dessas misturas não é recomendado para o confinamento de A. triradiatus.]]></p></abstract>
<kwd-group>
<kwd lng="es"><![CDATA[Aceite de clavo]]></kwd>
<kwd lng="es"><![CDATA[clinoptilolita]]></kwd>
<kwd lng="es"><![CDATA[Loricariidae]]></kwd>
<kwd lng="es"><![CDATA[sal]]></kwd>
<kwd lng="es"><![CDATA[transporte de peces]]></kwd>
<kwd lng="en"><![CDATA[Clove oil]]></kwd>
<kwd lng="en"><![CDATA[clinoptilolite]]></kwd>
<kwd lng="en"><![CDATA[fish transport]]></kwd>
<kwd lng="en"><![CDATA[Loricariidae]]></kwd>
<kwd lng="en"><![CDATA[salt]]></kwd>
<kwd lng="pt"><![CDATA[Óleo de cravo]]></kwd>
<kwd lng="pt"><![CDATA[clinoptilolita]]></kwd>
<kwd lng="pt"><![CDATA[transporte de peixes]]></kwd>
<kwd lng="pt"><![CDATA[Loricariidae]]></kwd>
<kwd lng="pt"><![CDATA[sal]]></kwd>
</kwd-group>
</article-meta>
</front><body><![CDATA[  <font face="verdana" size="2">          <p align="center"><font size="4"><b>Evaluaci&oacute;n del cloruro de sodio, eugenol y zeolita en el confinamiento de <i>Ancistrus triradiatus</i></b></font></p>     <p align="center"><font size="3"><b>Evaluation of the use of sodium chloride, eugenol, and zeolite in confinement of <i>Ancistrus triradiatus</i></b></font></p>     <p align="center"><font size="3"><b>Avalia&ccedil;&atilde;o decloreto de s&oacute;dio, o eugenol ezeolite em transporte <i>Ancistrus triradiatus</i></b></font></p>     <p align="right"><b>Wilson F. Ram&iacute;rez - Duarte<sup><a href="#1" name="nr1">1</a></sup>    <br>   Carolina Pineda - Quiroga<a href="#2" name="nr2"><sup>2</sup></a>    <br>   Nhora Mart&iacute;nez - Rueda<sup><a href="#3" name="nr3">3</a></sup>    <br> Pedro R. Eslava - Mocha<sup><a href="#4" name="nr4">4</a></sup></b></p>     <p><a href="#nr1" name="1">1</a> MVZ, Research Group on Health of Aquatic Organisms - Instituto de Acuicultura de los Llanos, Universidad de los Llanos.    <br>   Email: <a href="mailto:wramirezduarte@gmail.com">wramirezduarte@gmail.com</a>.    ]]></body>
<body><![CDATA[<br>   <a href="#2" name="2">2</a> Zootecnista, Ejercicio particular.    <br>   <a href="#3" name="3">3</a> Estadistica, MSc, Departament of Science for Animal Production, School of Veterinary Medicine and Zootechny, National University of Colombia. Bogot&aacute;, Colombia.    <br>   <a href="#4" name="4">4</a> MV, MSc, Research Group on Health of Aquatic Organisms - Instituto de Acuicultura de los Llanos, Universidad de los Llanos.</p>     <p>Recibido: octubre 10 de 2012. Aprobado: mayo 07 de 2013</p> <hr size="1" />              <p><b>Resumen</b></p>     <p>Se evalu&oacute; el uso de cloruro de sodio (1 y 2 g/L), eugenol (0.1 y 0.5 mg/L), y zeolita (7 g/L en confinamiento de 12 h y 10   g/L en el de 48 h), as&iacute; como de las mezclas de cloruro de sodio m&aacute;s eugenol (1 g/L y0.5 mg/L, respectivamente) y eugenol   m&aacute;s zeolita (0.5 mg/L y 7 o 10 g/L, respectivamente) en confinamiento de <i>Ancistrus triradiatus</i> durante periodos de 12 y 48   h. Se midieron los par&aacute;metros de calidad del agua, ox&iacute;geno disuelto, pH, temperatura, conductividad y concentraciones de   amoniaco total, amonio no ionizado y nitrito. La concentraci&oacute;n de glucosa en sangre fue medida antes de iniciar el confinamiento   y a las 0, 24 y 48 horas despu&eacute;s de terminado dicho confinamiento. Tambi&eacute;n se realiz&oacute; una prueba de resistencia   al estr&eacute;s al finalizar el periodo de confinamiento mediante la exposici&oacute;n de peces a una soluci&oacute;n salina hiperosm&oacute;tica   durante 1 h, en la cual se registr&oacute; el n&uacute;mero de peces que manten&iacute;a el eje de nado a intervalos de 5 min; se registr&oacute; la mortalidad   al finalizar los periodos de confinamiento (12 y 48 horas) y la mortalidad acumulada durante los 7 d&iacute;as siguientes.   El uso de 1 y 2 g/L de cloruro de sodio en el confinamiento de <i>A. triradiatus</i> durante periodos de 12 h y de 1 g/L durante   periodos de 48 h increment&oacute; la resistencia al estr&eacute;s y redujo la mortalidad de los animales. El uso de eugenol o zeolita no   mejor&oacute; la resistencia al estr&eacute;s ni contribuy&oacute; a la reducci&oacute;n de la mortalidad de los animales, mientras que la exposici&oacute;n a   las mezclas de sal m&aacute;s eugenol y de eugenol m&aacute;s zeolita increment&oacute; la mortalidad, por lo que el uso de estas mezclas no es recomendado en operaciones de confinamiento de <i>A. triradiatus</i>.</p>          <p><b>Palabras clave</b>: Aceite de clavo, clinoptilolita, <i>Loricariidae</i>, sal, transporte de peces.</p>      <p><b>Abstract</b></p>     <p>The use of sodium chloride (1 and 2 g/L), eugenol (0.1 and 0.5 mg/L), and zeolite (clinoptilolite, 7 g/L for 12 h and 10 g/L for 48 h of confinement), and also mixtures of salt plus eugenol (1 g/L and 0.5 mg/L, respectively) and eugenol plus zeolite (0.5 mg/L and 7 or 10 g/L, respectively) were evaluated in the confinement of <i>Ancistrus triradiatus</i> for 12 and 48h. Water parameters as concentration of dissolved oxygen, pH, temperature, conductivity, and concentrations of total ammonia, non-ionized ammonia and nitrite were monitored. The blood glucose concentration was measured before the confinement started and at 0, 24, and 48 hours after the confinement period finished. A stress resistance test was conducted right after the confinement time was completed by exposing the fish to a hyperosmotic saline solution for one hour, recording the number of fish that maintained the swimming axis at intervals of 5 minutes. The mortality at the end of both confinement periods (12 and 48 hours), and its cumulative percentage rate during the following 7 days were also recorded. The use of sodium chloride 1 and 2 g/L in confinement times of 12 h, and 1 g/L in confinement time of 48 hours increased the resistance to confinement-induced stress, and reduced mortality of the animals. The use of eugenol and zeolite did not improve the response to the stress, nor contribute to the reduction of mortality of the animals, while exposure to the mixtures of salt plus eugenol and eugenol plus zeolite increased the mortality so they are not recommended in the confinement of <i>A. triradiatus</i>.</p>     <p><b>Key words</b>: Clove oil, clinoptilolite, fish transport, <i>Loricariidae</i>, salt.</p>     ]]></body>
<body><![CDATA[<p><b>Resumo</b></p>     <p>Foi avaliada a utiliza&ccedil;&atilde;o de cloreto de s&oacute;dio (1 e 2 g/L), eugenol (0.1 e 0.5 mg/L) e zeolita (7 g/L para 12 h de confinamentoe   10 g/L em 48 h) e misturas de cloreto de s&oacute;dio e eugenol (1 g/L e0.5 mg/L, respectivamente) e eugenol mais zeolita   (0,5 mg/L, 7 ou 10 g/L, respectivamente) para confinamento de <i>Ancistrus triradiatus</i> por per&iacute;odos de 12 e 48h. Par&acirc;metros   de qualidade de &aacute;gua foram medidos: concentra&ccedil;&atilde;o de oxig&ecirc;nio dissolvido, pH, temperatura, condutividade e concentra&ccedil;&atilde;o   de am&ocirc;nia total e n&atilde;o ionizada e nitrito. A concentra&ccedil;&atilde;o de glicose no sangue foi medida antes e 0, 24 e 48 horas   ap&oacute;s a conclus&atilde;o do per&iacute;odo de confinamento. Um teste de estresse foi realizado no final do per&iacute;odo de confinamento,   expondo os peixes a uma salina hiperosm&oacute;tica durante 1 h, sendo registrado o n&uacute;mero de peixes que manteve o eixo de   nata&ccedil;&atilde;o em intervalos de 5 min. Da mesma forma, a mortalidade foi registrada no final dos per&iacute;odos de confinamento (12   e 48 horas), bem como o percentual acumulado nos 7 dias seguintes. A utiliza&ccedil;&atilde;o de 1 e 2 g/L de cloreto de s&oacute;dio no   confinamento de A.triradiatusdurante 12 h, e 1 g/L a 48 h aumentou a resist&ecirc;ncia ao estresse e reduziu a mortalidade dos   animais. O uso de zeolita ou eugenol n&atilde;o melhorou a resist&ecirc;ncia ao estressenem contribuiu para a redu&ccedil;&atilde;o da mortalidade   dos animais, enquanto que a exposi&ccedil;&atilde;o a misturas de sal e eugenol e de eugenol e zeolita aumentou a mortalidade, de modo que o uso dessas misturas n&atilde;o &eacute; recomendado para o confinamento de <i>A. triradiatus</i>.</p>     <p><b>Palavras chave</b>: &Oacute;leo de cravo, clinoptilolita, transporte de peixes, <i>Loricariidae</i>, sal.</p>  <hr size="1" />           <p><b><font size="3">Introduction</font></b></p>     <p>In Colombia, the harvesting of ornamental fish for export   dates from the 1950's, and despite the commercial   and social importance of the activity, the actual   biological and handling knowledge is scarce (Mancera- Rodriguez and Alvarez-Le&oacute;n,2008).</p>     <p>Xenocara, <i>Ancistrus triradiatus</i> (Eigenmann, 1918), is   an ornamental armored catfish native to the Orinoco   basin that belongs to the Loricaridae family. This family   is the second in the number of ornamental species of   commercial interest, and consisted of 20% of the total   number of specimens exported from Colombia in   2009 (MADR and CCI, 2010). In spite of its importance,   few studies exist about culture and reproduction   of this species. Collazos-Lasso and Arias-Castellanos   (2009) showed that its reproduction is possible and   easy in captivity; currently, some fisheries in Colombia   started the culture of <i>A. triradiatus</i> and other species of Loricaridae.</p>     <p>Routine activities in aquaculture, such as seining,   handling and confinement, usual during shipment,   are common factors of stress that threaten fish health   and survival (Barton <i>et al</i>., 2000). A variety of techniques   have been developed to mitigate the negative   effects of these procedures. To improve the transport   conditions of live fish, and increase their survival rate,   various practices have been implemented, such as   feeding management (Pan <i>et al</i>., 2010), use of loading   densities appropriate to the species (Gomes <i>et al</i>., 2003a, 2003b;Urbinati<i>et al</i>., 2004), reduction of   water temperature (Golombieski <i>et al</i>., 2003; Lim <i>et al</i>., 2003), and addition of salt (Carneiro and Urbinati,   2001; Gomes <i>et al</i>., 2003a), anesthetics (Iversen<i>et al</i>.,   2009; Pramod<i>et al</i>., 2010), and ion exchange resins   to the water (Singh <i>et al</i>., 2004), and also the use of probiotics (Gomes <i>et al</i>., 2009).</p>     <p>Anesthetics are used in low concentrations to reduce   fish metabolic rate through transport, which results in   lower oxygen consumption, with consequent reduction   of ammonia and CO<sub>2</sub> production, all factors favoring   survival during and after transport (Hoskonen and   Pirhonen, 2004). The amount of anesthetic administered   in transport conditions should induce a state of   sedation, but not general anesthesia, since it is desirable   that the fish maintain their normal position through   the transport, and that an active opercular movement   be also maintained (Iversen <i>et al</i>., 2009). Eugenol, the main compound of clove oil, is considered promising in the aquaculture industry because it has low market cost, high efficiency in its use, adequate margin of safety for the fish, and lack of toxicity to humans (Roubach <i>et al</i>., 2005). This anesthetic, which is of recent use in aquaculture practices, has generated beneficial effects after confinement of channel catfish <i>Ictalurus punctatus</i> (Small, 2004), and in the transport of Atlantic salmon (smolt) <i>Salmo salar</i> (Iversen <i>et al</i>., 2009), which resulted in the increase of survival during each procedure, and in reduction of both cortisol and glucose blood levels.</p>     <p>Zeolite, an ion exchange resin, is used in aquaculture   in order to remove ammonia in fish production systems,   as well as during their storage in tanks or in transport   bags (Silapajarn <i>et al</i>., 2006), through sodium ion   exchange for ammonia (Kaiser <i>et al</i>., 2006; Singh <i>et al</i>.,   2004). The addition of zeolite in the transport of catla   <i>Catla catla</i>, roholabeo <i>Labeo rohita</i>, mrigal carp <i>Cirrhinus   mrigala</i> (Kaiser <i>et al</i>., 2006; Singh <i>et al</i>., 2004), the   Lake Victoria cichlid <i>Haplochromis obliquidens</i> (Kaiser <i>et al</i>., 2006), and guppy <i>Poecilia reticulata</i> (Teo <i>et al</i>.,   1989) have been evaluated, and all have reported favorable   effects on water quality.</p>     <p>The addition of sodium chloride in water during confinement   periods, such as during shipment, has been   implemented primarily to help with the electrolyte   balance of the fish, because it reduces the osmotic   gradient between the internal fluids and the water   (Carneiro <i>et al</i>., 2007). The benefits of the use this   substance have been demonstrated in tambaqui <i>Colossoma   macropomum</i> (Gomes <i>et al</i>., 2003a), matrinx&atilde;   <i>Brycon amazonicus</i> (Carneiro and Urbinati, 2001),   while in other species, such aspirarucu <i>Arapaima gigas</i>  (Gomes <i>et al</i>., 2006), and silver catfish <i>Rhamdia quelen</i>  (Gomes <i>et al</i>., 1999), the use of salt induced osmoregulatory   disturbances and may lead to high mortality   during shipment.</p>     ]]></body>
<body><![CDATA[<p>The aim of this study is to determine the effect of salt,   eugenol and zeolite, as well as mixtures thereof, in the   confinement of <i>A. triradiatus</i> for periods of 12 and 48   hours on survival, resistance to hyperosmolarity after   confinement, blood glucose, and water quality.</p>     <p><b><font size="3">Materials and methods</font></b></p>     <p><b><i>Experimental fish</i></b></p>     <p>Wild specimens of <i>Ancistrus triradiatus</i>, with marketable   size (9.0 &plusmn; 6.4 g and 7.0 &plusmn; 1.4 cm of standard length;   n=1576) were purchased from local distributors. The   fish were acclimated for at least 15 days to laboratory   conditions in 40 L aquaria. Acclimation mortality was   0.78%. The fish were fed once a day with commercial   feed with 30% crude protein. Feeding was suspended   3 days before the experiments were initiated, and was   resumed 1 day after the completion of them.</p>     <p>The effect of two confinement times (12 and 48 h) was   evaluated to simulate frequent transport times occurring   in Colombia, and in the processes of exportation. At the   beginning of the experiments, fish were weighed (balance   Traveler<sup>TM</sup> TA3001, OHAUS) and packed in double   polyethylene bags (38 x 35 cm to confine them 48   hours, and 29.5 x 17 cm to confine them 12 h), with 3 L   of water for confinement time of 48 h, and 2 L for 12 h,   utilizing in both cases, a 3:1 volume ratio of oxygen: water.   The number of fish and load density per bag were:   31 fish/bag and 137.5 g/L for 12 h and 27 fish/bag and   82.3 g/L for 48 h. The bags were packed in cardboard   boxes and kept under dark conditions.</p>     <p><b><i>Substances evaluated</i></b></p>     <p>The inclusion of sodium chloride (1 and 2 g/L, symbolized   as S1, and S2 respectively), eugenol (4-allyl-   2-methoxyphenol) (0.1 and 0.5 mg/L, symbolized as   E0.1, and E0.5 respectively), and zeolite (7 g/L for confinement   time of 12 h and 10 g/L for 48 h, symbolized   as Zeo) in the water was evaluated for both confinement   times. These concentrations were established   based on preliminary experiments. For zeolite, the inclusion   rate recommended by the manufacturer was   also taken into account, which was 1 g of zeolite per   1.5 mg total ammonia. Mixtures of salt and eugenol   (S1-E0.5) and eugenol and zeolite (E0.5-Z) were also   evaluated using concentrations of both salt and eugenol   that showed the best results when the fish were exposed   to these substances separately. The experiments   were run in triplicate.</p>     <p>Sodium chloride was purchased in the local market   and was a technical grade product. Eugenol was also   obtained in the local market and was a pharmaceutical   grade product for dental use, and was previously dissolved   in ethanol (1:9). Therefore, it was also included a   solvent control group exposed to the highest concentration   of ethanol that was used in the groups exposed to   eugenol, in order to evaluate a possible effect of ethanol.   The zeolite, clinoptilolite ProLine<sup>&reg;</sup>, was purchased   from Aquatic Eco-Systems, Inc. The control group did   not contain any substance added to the water.</p>     <p><b><i>Water quality parameters evaluated</i></b></p>     <p>Immediately prior to packing the fish in the polyethylene   bags, and also at the end of each experiment, water temperature, dissolved oxygen (oximeterOxi 330i,   WTW, Germany), pH, conductivity (multiparameter HI   98129, HANNA Instruments, USA), concentrations of   ammonia and nitrite (Spectroquant colorimetric kits,   Merck<sup>&reg;</sup> - Spectronic<sup>&reg;</sup> 20 GENESYS, Spectronic Instruments),   hardness (EDTA titrimetric method), and alkalinity   (by titration with bromocresol green) (APHA, 1992)   were measured. Additionally, non-ionized ammonia   concentrations were obtained applying the formulas of   Bower and Bidwell (1978), and of Johansson &#38; Wedborg   (1980). The temperature during the experiments   was recorded with maximum and minimum thermometers   (Sper Scientific), for which two of these thermometers   were placed in two bags packed in the same   conditions as the fish and kept in boxes with the bags   that included the experimental fish. To measure the concentrations   of total ammonia and nitrite, the water samples   were refrigerated and processed within 24h.</p>     ]]></body>
<body><![CDATA[<p>The water quality parameters at the beginning of the   experiments were: dissolved oxygen supersaturation;   pH 7.35 &plusmn; 0.09; total ammonia 0.05 &plusmn; 0.01 mg/L; nitrite   0.015 &plusmn; 0.012 mg/L; total hardness 9.13 &plusmn; 3.80 mg/L;   and total alkalinity 4.87 &plusmn; 0.50 mg/L. The initial conductivity   values of each group are recorded in <a href="#tab1">Table 1</a>.</p>       <p align="center"><img src="img/revistas/rori/v17n1/v17n1a09tab1.gif"><a name="tab1"></a></p>     <p><b><i>Blood Glucose Concentration</i></b></p>     <p>The blood glucose concentration was determined   from 6 fish in each treatment at 0, 24 and 48 h after   the end of confinement period with a glucose meter   Accu-Chek<sup>&reg;</sup> Active (Roche). The blood glucose of 10   fish was also determined during the acclimation period.   This measurement was taken as the basal blood   glucose concentration. In order to take the samples of   blood from the experimental fish, they were anesthetized   with eugenol (150 mg/L) for 5 minutes.</p>     <p><b><i>Test of resistance to conditions of hyperosmolarity</i></b></p>     <p>At the end of the experimental period, a resistance   test to hyperosmolarity was performed by the immersion   of 20 fish of each treatment in water with 2% salt   (NaCl, free of iodine and fluorine) and the number   of fish which retained the swimming axis for 1 hour   was recorded, with readings taken at 5 minute intervals.   Once the fish lost their swimming axis, they were   taken out in order to recover in an aquarium that was   salt-free.</p>     <p><b><i>Percentage of mortality</i></b></p>     <p>The mortality rate was recorded at the end of the confinement   and also during the following 7 days.</p>     <p><b><i>Statistical analysis</i></b></p>     <p>The homogeneity of variances was determined with   the Levene test (P&gt;0.01) for blood glucose and water   parameters data, and significant differences between   groups were established with the ANOVA test followed   by the <i>Tukey-Kramer test of multiple comparisons</i>. A logarithmic   transformation was done for blood glucose   data.</p>     ]]></body>
<body><![CDATA[<p>The results of the test of stress resistance were analyzed   using a multiple regression test with a linear model   with a qualitative predictor for the group, which has n   classes that correspond to the number of groups (Kutner <i>et al</i>., 2005).</p>     <p>Mortality results were analyzed by frequency distribution,   and the Chi square test of independence   was used to establish significant differences between   groups and also within each group, as well as between   mortality at the end of confinement period and in the   following 7 days.</p>     <p>In all the cases, significant differences were established   with P&lt;0.05. The software SAS version 8.05 was used.</p>     <p><b><font size="3">Results</font></b></p>     <p>There was no difference between the control and the   solvent control group for the different parameters at   12 and 48 hours confinement times (data not showed).</p>     <p><b><i>Confinement time of 12 hours</i></b></p>     <p><b>Water quality parameters</b></p>     <p>Dissolved oxygen was maintained at supersaturated   conditions in all groups at the end of the experimental   period of 12 hours, and the temperature ranged between   26 and 30 &deg;C.</p>     <p>The experiments of the mixtures of salt plus eugenol   as well as that of zeolite plus eugenol were performed   with concentrations of 1 g/L of salt and 0.5 mg/L of   eugenol, based on the results shown in <a href="#tab2">Table 2</a>.</p>       <p align="center"><a href="img/revistas/rori/v17n1/v17n1a09tab2.gif" target="_blank">Table 2</a><a name="tab2"></a></p>     ]]></body>
<body><![CDATA[<p>The pH in all groups declined at the end of the confinement   period relative to the initial pH, and it was   significantly lower (P&lt;0.05) in the group S1-E 0.5. All   other groups had the pH in the 6.0 to 6.4 range, and   it was significantly higher (P&lt;0.05) in the groups E0.5   and Zeo (<a href="#tab2">Table 2</a>). The variation of conductivity was   significantly lower (P&lt;0.05) in the groups S1 and S1-E   0.5 relative to the rest of the groups (<a href="#tab2">Table 2</a>).</p>     <p>Total ammonia concentrations at the end of this experimental   period were in the 4.9 to 6.8 mg/L range and   was significantly lower (P&lt;0.05) in the group Z-E0.5,   and significantly higher (P&lt;0.05) in the group S1-E 0.5.   However, no similar change was observed in the concentration   of non-ionized ammonia, which varied in the   range of 0.0012 to 0.0031 mg/L, and was significantly   higher (P&lt;0.05) in groups Zeo and E0.5 which showed   higher pH and the concentration of total ammonia was   significantly lower (P&lt;0.05). Additionally, in the group   S1-E0.5 the total ammonia concentration was significantly   higher in comparison with groups S1 and S0.5   (<a href="#tab2">Table 2</a>).</p>     <p>Nitrite was in the 0.17 to 0.59 mg/L range, and was   significantly lower (P&lt;0.05) in groups S2 and Z-E0.5.   The highest concentration (P&lt;0.05) was found in the   group E0.1 (<a href="#tab2">Table 2</a>).</p>     <p><b><i>Blood Glucose Concentration</i></b></p>     <p>Only the group containing 1g/Lof salt did not show a   significant increase of blood glucose concentration at   0h after 12h of confinement compared to basal blood   glucose concentration. After 24 h, all groups returned   to the basal concentration (<a href="#tab3">Table 3</a>).</p>       <p align="center"><a href="img/revistas/rori/v17n1/v17n1a09tab3.gif" target="_blank">Table 3</a><a name="tab3"></a></p>     <p>Resistance test to conditions of hyperosmolarity   The linear regression model between the number of   fish that kept their swimming axis(y) and the time of   exposure to the saline solution showed an inverse relationship   (P&lt;0.0001) for the two confinement times   (<a href="#fig1">Figure 1a</a>).</p>       <p align="center"><img src="img/revistas/rori/v17n1/v17n1a09fig1.gif"><a name="fig1"></a></p>     <p>The model developed was the following:</p>     <blockquote>y = &beta;0+(&beta;1*time)    ]]></body>
<body><![CDATA[<br>   &beta;0 and &beta;1 being significant (P&lt;0.0001).    <br>   Control, y = 15.74019 + (-1.41026*time)    <br>   S1, y = 19.61029 + (-1.41026*time)    <br>   S2, y = 20.11029 + (-1.41026*time)    <br>   E0.1, y = 14.74019 + (-1.41026*time)    <br>   E0.5, y = 19.36029 + (-1.41026*time)    <br>   Zeo, y = 18.86029 + (-1.41026*time)    <br>   Z-E0.5, y = 17.36029 + (-1.41026*time)    <br>   S1-E0.5, y = 17.61029 + (-1.41026*time)</blockquote>     <p>In the experiment of 12h, the S2 group showed the greatest   stress resistance, and was the only group that showed   significant differences with the control group, and also with   the group E0.1. The E0.5 group presented significantly higher   resistance than the group E0.1. No significant differences   were found between the other groups.</p>     ]]></body>
<body><![CDATA[<p><b><i>Mortality rate</i></b></p>     <p>The group S1-E 0.5 showed significantly higher mortality   than all the other groups, except the group E0.1, just   after finishing the12h of confinement (<a href="#tab4">Table 4</a>). After7   days post-confinement, the groups S1 and S2 did not   show any mortality, which was significantly lower than   for the other groups, except the group Zeo. The highest   mortality after 7 days post-confinement was found   in the groups exposed to mixtures Z-E0.5 and S1-E 0.5.   Furthermore, there was a significant increase in mortality   during the7 days post-confinement in the group   exposed to the mixture Z-E0.5.</p>       <p align="center"><a href="img/revistas/rori/v17n1/v17n1a09tab4.gif" target="_blank">Table 4</a><a name="tab4"></a></p>     <p><font size="3"><b>Confinement time of 48 hours</b></font></p>     <p><b><i>Water Quality Parameters</i></b></p>     <p>The temperature ranged between 25 and 28 &deg;C.</p>     <p>The pH ranged between 6.13 and 6.87, showing a reduction   in each of the groups from the initial values,   being significantly lower (P&lt;0.05) in the groups Zeo   and S1-E0.5. The highest pH (P&lt;0.05) was found in the   control, S2 and E0.5 groups (Table 2). The highest increase   of conductivity (P&lt;0.05) was seen in the control   group, while the lowest increase (P&lt;0.05) was found in   groups S1, Zeo and S1-E0.5 (<a href="#tab2">Table 2</a>).</p>     <p>Total ammonia was in the 4 to 12.3 mg/L range, and   was significantly lower (P&lt;0.05) in group Zeo. The highest   concentrations (P&lt;0.05) were found in the control,   S2 and S1-E0.5 groups (<a href="#tab2">Table 2</a>). Furthermore, the   group S1-E0.5 showed significantly higher total ammonia   in comparison with groups S1 and S0.5. Unionized   ammonia was in the 0.0015 to 0.0175 mg/L range, and   the significantly highest concentrations (P&lt;0.05) were   found in the control and S2 groups. The nitrite concentration   was in the 0.05 to 0.26 mg/L range, with the   significantly highest concentration (P&lt;0.05) in the control   group. Significantly lowest concentrations (P&lt;0.05)   were found in the groups Zeo and S1-E0.5 (<a href="#tab2">Table 2</a>).</p>     <p><b><i>Blood Glucose Concentration</i></b></p>     <p>The groups E0.1, E0.5 and Z-E0.5 showed a significant   increase (P&lt;0.05) on blood glucose at time 0h after   confinement, relative to the basal concentration. The   lowest blood glucose concentration sat time 0h were   found in the groups S2 and Zeo. After 24h post-confinement,   all groups returned to the basal blood glucose   concentration (<a href="#tab3">Table 3</a>).</p>     ]]></body>
<body><![CDATA[<p><b><i>Test of resistance to conditions of hyperosmolarity</i></b></p>     <p>The linear regression model between the number of   fish that kept their swimming axis (y) and time of exposure   to the saline solution shows an inverse relationship   (P&lt;0.0001) (<a href="#fig2">Figure 1b</a>).</p>       <p align="center"><img src="img/revistas/rori/v17n1/v17n1a09fig2.gif"><a name="fig2"></a></p>     <p>The model developed was as follows:</p>     <blockquote>y = &beta;0 + (&beta;1*time)    <br>   &beta;0 and &beta;1 being significant (P&lt;0.0001).    <br>   Control, y = 19.32645 + (-0.86612*time)    <br>   S1, y = 22.27745 + (-0.86612*time)    <br>   S2, y = 18.86116 + (-0.86612*time)    <br>   E0.1, y = 19.82645 + (-0.86612*time)    ]]></body>
<body><![CDATA[<br>   E0.5, y = 18.46116 + (-0.86612*time)    <br>   Zeo, y = 15.74587 + (-0.86612*time)    <br>   Z-E0.5, y = 15.49587 + (-0.86612*time)    <br>   S1-E0.5, y = 21.56317 + (-0.86612*time)</blockquote>     <p>Groups S1 and S1-E0.5 had the highest resistance to   stress, while the lowest resistance was shown in the   groups Zeo and Z-E0.5 (<a href="#fig2">Figure 1b</a>).</p>     <p><b><i>Mortality rate</i></b></p>     <p>There were no significant differences in mortality right   after finishing the confinement period. However, there   was a significant increase on mortality in the S2 group   for the following 7 days which resulted insignificantly   higher mortality rate compared to the other groups.</p>     <p><b><font size="3">Discussion</font></b></p>     <p><b><i>Water quality parameters</i></b></p>     <p>The reduction in pH values obtained at the end of confinement   period compared to the initial value is due   to the production of CO<sub>2</sub>, a product of respiration.   In general, pH values recorded in all groups are below   the range recorded in habitats of this species, this   being approximately 6.5 to 7.5 (Ram&iacute;rez-Duarte <i>et al</i>.,   2009). Although this reduction in pH values lowers the   concentration of non-ionized ammonia in the water, it   also has deleterious effects, such as, decreased oxygen   carrying capacity of the blood (Berka, 1986). So it is   recommended that buffer substances be used in the   water as it has been suggested by other authors (Lim <i>et al</i>., 2003).</p>     ]]></body>
<body><![CDATA[<p>The increase in the water conductivity of the water at   the end of the experiments is explained by the net loss   of electrolytes from the blood, a process favored by   the increase in gill permeability, caused by the increased   secretion of catecholamines and cortisol as part of   the primary stress response in fish (Wendelaar-Bonga,   1997). In both experiments (12 and 48h), the lowest   increases of conductivity in groups S1 and S1-E 0.5   can be explained by the reduced osmotic gradient between   the plasma and the water that reduces the loss of   plasma electrolytes (Carneiro <i>et al</i>., 2007).</p>     <p>In the experiment of 48 h, the significantly lower change   of conductivity and blood glucose concentration   in group Zeo may indicate that the adsorptive action   of the zeolite on ammonia mitigates or prevents the   ammonia-induced ionoregulatory disturbances (Silapajarn <i>et al</i>., 2006). Similar to the results obtained for Nile   tilapia <i>Oreochromis niloticus</i> (Oliveira <i>et al</i>., 2009), the   addition of increasing amounts of salt and eugenol did   not reduce total ammonia at the end of 12 hour experiment.   The addition of eugenol to transport water   of <i>Haplochromis obliquidens</i> (Kaiser <i>et al</i>., 2006) and   matrinx&atilde; (Inoue <i>et al</i>., 2005) also did not reduce total   ammonia concentration.</p>     <p>Even though significant differences were found in   the concentration of non-ionized ammonia between   groups in both experiments (12 and 48 h), in all cases   (<a href="#tab2">Table 2</a>) they were well below the range of values of   LC50 at 96 h reported for teleosts (&ge;0.34 mg/L) for pH   values between 6 and 8.2 (Abbas, 2006; Miron <i>et al</i>.,   2008; Rodrigues <i>et al</i>., 2007).</p>     <p>The concentrations of nitrite in the experiment of 12 h   were found near and above concentrations reported   as lethal to other fish species (0.25 mg/L at 96 h in   <i>Oncorhynchus mykiss</i>) (Russo <i>et al</i>., 1981). A similar   situation was found in the experiment of 48 h, except   for groups exposed to zeolite (Zeo) and S1-E0.5. In   the case of the zeolite group, it may be lower due to   significantly lower concentrations of total ammonia.   However, the mechanism is unknown by which in the   group salt plus eugenol the concentration of nitrite   was significantly lower, even when the same group   presented the highest concentration of total ammonia.   Nitrite is produced by bacterial oxidation of ammonia,   and from the aerobic decomposition of organic matter,   and it accumulates as nitrite generation exceeds   the rate of oxidation of nitrite to nitrate (Wedemeyer,   1996). However, no relationship was found between   nitrite concentration and mortality.</p>     <p><b><i>Concentration of blood glucose</i></b></p>     <p>The rise of concentration of catecholamines and cortisol   in blood induces an increase in blood glucose, so   this parameter is used as an indicator of stress when   the fish are exposed to stressful events (Carneiro and   Urbinati, 2001; Gomes <i>et al</i>., 2003b; Wendelaar-Bonga,   1997).</p>     <p>In this study the beneficial effect of adding salt to water   in both experiments (12 and 48 h) is also reflected in   the results of the glucose concentration 12h experiment   (<a href="#tab3">Table 3</a>), where the group S1 was the only group   that did not increase significantly the blood glucose   right after the confinement period finished (time 0h)   compared to the basal blood glucose concentration,   indicating less energy expenditure imposed by the reduced   loss of electrolytes into the blood.</p>     <p>The addition of salt has been linked to decreased secretion   of cortisol and lower levels of glucose during   and after transport in tambaqui <i>Colossoma macropomum</i>  exposed to 8 g/L (Gomes <i>et al</i>., 2003a), matrinx&atilde;   to 6 g/L (Carneiro and Urbinati, 2001) and pejerrey   (<i>Odontesthes bonariensis</i>) exposed to 3-5 g/L (Tsuzuki   <i>et al</i>., 2001). Therefore, reduction of stress may be   reflected in low gill permeability, leading to lower ion   loss through gill epithelium.</p>     <p>Eugenol at 0.1 and 0.5 mg/L (E0.1 and E0.5 respectively)   did not reduce fish stress during the two confinement   times. In contrast to these results, 2 to 5 mg/L   eugenol in Nile tilapia (Oliveira <i>et al</i>., 2009) and 5   mg/L in matrinx&atilde; (Inoue <i>et al</i>., 2005) were reported   as useful for mitigating the stress response as reflected   in low blood glucose levels at the end of transport.   In preliminary trials with <i>A. triradiatus</i>, 5 and 10 mg/L   eugenol caused loss of the swimming axis and severe   reduction of opercular movements within one hour of   exposure, and at 10 mg/L the fish did not recover after   one hour of exposure and died (unpublished data). It   is recommended that fish maintain their normal position   within the transport containers, or bags, and also   maintain an active opercular movement (Iversen <i>et al</i>.,   2009).</p>     <p><b><i>Test of resistance to conditions of hyperosmolarity</i></b></p>     ]]></body>
<body><![CDATA[<p>Exposure to high concentrations of salt has been suggested   as a resistance test to stress, where a high   resistance indicates increased survival of fish when   subjected to stressful conditions (Lim <i>et al</i>., 2003).   Stress increases gill permeability and leads to changes   in plasma electrolyte concentrations in hyposmotic or   hyperosmotic environments (Carneiro <i>et al</i>., 2007). In   this experiment, it was found that the groups exposed   to salt 2 g/L in the experiment of 12 h, and 1 g/L of   salt in the experiment of 48h, were the only groups   that showed a significant increase in resistance compared   with the control group, indicating less impairment   of gill permeability, which gives it greater capacity to   conserve hydro-electrolytic balance to stressors, and,   therefore, greater chance of survival (Carneiro <i>et al</i>.,   2007).</p>     <p>Eugenol at 0.1 and 0.5 mg/L (E0.1 and E0.5 respectively)   and the mixtures S1-E0.5 and Z-E0.5 did not improve   (P&lt;0.05) resistance to stress compared with the   control group.</p>     <p><b><i>Percentage of mortality</i></b></p>     <p>The absence of mortality in groups exposed to 1 and   2 g/L NaCl in the 12 h experiment and S1 group in   the experiment of 48h shows the beneficial effects of   sodium chloride by reducing the osmotic gradient between   the water and blood, alleviating the stress, and   increasing resistance to conditions of hyperosmolarity.   The absence of mortality in these groups is notable   because it avoids deterioration of water quality caused   by dead fish.   The 16% mortality registered for the S2 group in the   experiment of 48h the following 7 days after finishing   the confinement period indicates that the concentration   of 2 g/L of salt is not suitable for prolonged exposure   in the confinement of <i>A. triradiatus</i>. Gomes <i>et al</i>. (1999, 2006) reported that exposure of jundi&aacute; to   6 g/L of salt, and tambaqui to 1, 2, and 3 g/L, caused   mortality after 12h and 24h, respectively. Gomes <i>et al</i>.   (2006) also reported that exposure of piraruc&uacute; to concentrations   between 1 and 5 g/L induced osmoregulatory   disturbances and did not alleviate the stress during   transport. Similarly, Pavlidis <i>et al</i>. (2003) did not report   beneficial effects from the addition of salt on the survival   of red porgy, Pagrus pagrus. The significant increase   in mortality after 7 days in the group exposed to 2 g/L   of salt agrees with the recommendation of Lim <i>et al</i>.   (2003) to monitor mortality up to 7 days after transport   due to the effects of stress in the medium term.   There was not a beneficial effect of eugenol and the   mixtures S1-E0.5 and Z-E0.5 on fish survival.</p>     <p><b><font size="3">Conclusions</font></b></p>     <p>The use of 1 to 2 g/L sodium chloridein12h confinement,   and of 1g/L in 48h confinement, increases   resistance to stress, and reduces the mortality of <i>A. triradiatus</i>.   The use of eugenol or zeolite did nor reduce   the stress response nor reduce mortality. The combinations   of salt plus eugenol and zeolite plus eugenol   are not recommended because they can increase mortality.</p>     <p><b><font size="3">Acknowledgements</font></b></p>     <p>This study was developed under the project "<i>Construction   of the first epidemiological map of ornamental fish   diseases in Colombia</i>",contract No. 057-2007U4448-387-07, funded by the Ministry of Agriculture and Rural   Development of Colombia, as a result of a national   contest co-finance research programs, technological   development, and innovation for the agricultural sector   by means of productive chains.</p>     <p>The authors express their gratitude to the young   members of Research Group on Health of Aquatic   Organisms of the Universidad de los Llanos that collaborated   in the development of the experiments.</p>     <p><b><font size="3">References</font></b></p>     ]]></body>
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