<?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>1665-2738</journal-id>
<journal-title><![CDATA[Revista mexicana de ingeniería química]]></journal-title>
<abbrev-journal-title><![CDATA[Rev. Mex. Ing. Quím]]></abbrev-journal-title>
<issn>1665-2738</issn>
<publisher>
<publisher-name><![CDATA[Universidad Autónoma Metropolitana, División de Ciencias Básicas e Ingeniería]]></publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S1665-27382008000300006</article-id>
<title-group>
<article-title xml:lang="en"><![CDATA[Dispersion model to describe the carbon removal from wastewater in a fixed bed up flow pilot bioreactor with a hexagonal feldspar packing]]></article-title>
<article-title xml:lang="es"><![CDATA[Modelo de dispersión para describir la remoción de carbono de aguas residuales en un reactor de flujo ascendente de lecho fijo con un empaque hexagonal de feldespato]]></article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Martínez-Delgadillo]]></surname>
<given-names><![CDATA[S. A.]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Rodríguez-Cruz]]></surname>
<given-names><![CDATA[M.]]></given-names>
</name>
<xref ref-type="aff" rid="A02"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Rodríguez-Rosales]]></surname>
<given-names><![CDATA[M. G.]]></given-names>
</name>
<xref ref-type="aff" rid="A03"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution><![CDATA[,Universidad Autónoma Metropolitana -Azcapotzalco. Departamento de Energía ]]></institution>
<addr-line><![CDATA[México D.F.]]></addr-line>
</aff>
<aff id="A02">
<institution><![CDATA[,Universidad Autónoma Chapingo Área de Física ]]></institution>
<addr-line><![CDATA[ ]]></addr-line>
<country>México</country>
</aff>
<aff id="A03">
<institution><![CDATA[,Instituto Politécnico Nacional (IPN) Escuela Nacional de Ciencias Biológicas (ENCB) Depto. Ingeniería en Sistemas Ambientales]]></institution>
<addr-line><![CDATA[México D.F.]]></addr-line>
</aff>
<pub-date pub-type="pub">
<day>00</day>
<month>12</month>
<year>2008</year>
</pub-date>
<pub-date pub-type="epub">
<day>00</day>
<month>12</month>
<year>2008</year>
</pub-date>
<volume>7</volume>
<numero>3</numero>
<fpage>223</fpage>
<lpage>228</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_arttext&amp;pid=S1665-27382008000300006&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_abstract&amp;pid=S1665-27382008000300006&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.mx/scielo.php?script=sci_pdf&amp;pid=S1665-27382008000300006&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p><![CDATA[In this work the modeling of carbon removal from wastewater in a fixed bed up flow pilot bioreactor with a hexagonal feldspar packing was carried out. The performance of a hexagonal feldspar packing was evaluated in an aerated biological pilot reactor. The feldspar packing was obtained by direct extrusion followed by sintering at 1100°C, during 4 hours, conditions at which the highest porosity and specific surface area were obtained. In addition to its easy preparation and low cost, the packing presented chemical resistance to different acids. The biological fixed bed up flow reactor with a total volume of 30.7 L was randomly packed with the hexagonal pieces of feldspar. Dispersion test were performed with a tracer (KCl), to estimate the dispersion number (Nd) in the reactor, with and without aeration. It was found that the dispersion increased due to the aeration and exerts a strong influence on reactor performance. A plug flow reactor model with axial dispersion and Monod kinetic was used to describe the carbon removal (COD) in the reactor at different hydraulic loading rates. The wastewater used during the tests was sampled at the exit of the primary settler of a Mexican wastewater treatment plant, being a mixture of industrial and urban effluents, with a COD = 650 mg/L. Four ascendant flow hydraulic loadings (L) from 1.08 x 10-4 (m³/s m²) to 4.32 x 10-4 (m³/s m²) were tested. The COD removal was about 95%, higher than the 85% reported in other studies.]]></p></abstract>
<abstract abstract-type="short" xml:lang="es"><p><![CDATA[En el presente trabajo se modeló la remoción de carbono de aguas residuales en un bioreactor piloto de lecho fijo de flujo ascendente con un empaque hexagonal de feldespato. El desempeño del empaque hexagonal de feldespato fue evaluado en el reactor piloto aireado. El empaque fue obtenido mediante extrusión seguida de un proceso de sinterizado a 1100°C durante 4 horas, en la cual se obtuvo la mayor porosidad y área superficial especifica. Además de su fácil preparación y bajo costo, el empaque de feldespato resultó ser resistente a diferentes ácidos. El reactor piloto, con volumen total de operación 30.7 L, fue empacado al azar con el soporte hexagonal de feldespato. Se realizaron pruebas con y sin aireación, para estimar el número de dispersión (Nd), utilizando como trazador KCl. Se encontró que la dispersión se incrementa con la aireación y ejerce una fuerte influencia en el desempeño del reactor. Para describir la remoción de carbono (DQO) se utilizo un modelo que considera la dispersión axial en el reactor, así como una reacción de remoción de tipo Monod que fue validado a diferentes cargas hidráulicas. Durante los experimentos se utilizó agua residual muestreada a la salida del sedimentador primario de una planta mexicana de tratamiento de aguas residuales. El agua residual es una mezcla de agua residual industrial y de agua residual domestica con una demanda química de oxigeno (DQO) de 650 mg/L. Las pruebas se realizaron con flujo ascendente y se probaron 4 cargas hidráulicas (L); desde 1.08 x 10-4 (m³/s m²) hasta 4.32 x 10-4 (m³/s m²). La remoción DQO alcanzó un 95 % lo cual es mayor a lo reportado (85%) en otros estudios.]]></p></abstract>
<kwd-group>
<kwd lng="en"><![CDATA[dispersion]]></kwd>
<kwd lng="en"><![CDATA[modeling]]></kwd>
<kwd lng="en"><![CDATA[feldspar packing]]></kwd>
<kwd lng="en"><![CDATA[wastewater secondary]]></kwd>
<kwd lng="en"><![CDATA[treatment]]></kwd>
<kwd lng="es"><![CDATA[dispersión]]></kwd>
<kwd lng="es"><![CDATA[modelo]]></kwd>
<kwd lng="es"><![CDATA[lecho fijo]]></kwd>
<kwd lng="es"><![CDATA[feldespato]]></kwd>
<kwd lng="es"><![CDATA[empaque]]></kwd>
<kwd lng="es"><![CDATA[reactor]]></kwd>
<kwd lng="es"><![CDATA[flujo ascendente]]></kwd>
<kwd lng="es"><![CDATA[agua residual]]></kwd>
</kwd-group>
</article-meta>
</front><body><![CDATA[ <p align="justify"><font face="verdana" size="4">Ingenier&iacute;a ambiental</font></p>     <p align="center"><font face="verdana" size="4">&nbsp;</font></p>     <p align="center"><font face="verdana" size="4"><b>Dispersion model to describe the carbon removal from wastewater in a fixed bed up flow pilot bioreactor with a hexagonal feldspar packing</b></font></p>     <p align="center"><font face="verdana" size="2">&nbsp;</font></p>     <p align="center"><font face="verdana" size="3"><b>Modelo de dispersi&oacute;n para describir la remoci&oacute;n de carbono de aguas residuales en un reactor de flujo ascendente de lecho fijo con un empaque hexagonal de feldespato</b></font></p>     <p align="center"><font face="verdana" size="2">&nbsp;</font></p>     <p align="center"><font face="verdana" size="2"><b>S. A. Mart&iacute;nez&#150;Delgadillo<sup>1</sup>*, M. Rodr&iacute;guez&#150;Cruz<sup>2</sup> and M. G. Rodr&iacute;guez&#150;Rosales<sup>1,3</sup></b></font></p>     <p align="justify"><font face="verdana" size="2">&nbsp;</font></p>     <p align="justify"><font face="verdana" size="2"><i><sup>1</sup> Departamento de Energ&iacute;a, Universidad Aut&oacute;noma Metropolitana &#151;Azcapotzalco. Av. San Pablo 180. Azcapotzalco. CP.02200. M&eacute;xico D.F. * <i>Corresponding author. E&#150;mail: </i></i><a href="mailto:samd@correo.azc.uam.mx">samd@correo.azc.uam.mx</a></font></p>     <p align="justify"><font face="verdana" size="2"><i><i><sup>2</sup></i> &Aacute;rea de F&iacute;sica, Universidad Aut&oacute;noma Chapingo. Km 38.5 Carretera M&eacute;xico&#150;Texcoco. M&eacute;xico </i></font></p>     ]]></body>
<body><![CDATA[<p align="justify"><font face="verdana" size="2"><i><sup>3</sup> Depto. Ingenier&iacute;a en Sistemas Ambientales, ENCB, IPN, Av. Wilfrido Massieu s/n Unidad Profesional Adolfo L&oacute;pez Mateos, M&eacute;xico D.F.</i></font></p>     <p align="justify"><font face="verdana" size="2">&nbsp;</font></p>     <p align="justify"><font face="verdana" size="2">Received 3<sup>rd</sup> of December 2007    <br> Accepted 10<sup>th</sup> of October 2008</font></p>     <p align="justify"><font face="verdana" size="2">&nbsp;</font></p>     <p align="justify"><font face="verdana" size="2"><b>Abstract</b></font></p>     <p align="justify"><font face="verdana" size="2">In this work the modeling of carbon removal from wastewater in a fixed bed up flow pilot bioreactor with a hexagonal feldspar packing was carried out. The performance of a hexagonal feldspar packing was evaluated in an aerated biological pilot reactor. The feldspar packing was obtained by direct extrusion followed by sintering at 1100&deg;C, during 4 hours, conditions at which the highest porosity and specific surface area were obtained. In addition to its easy preparation and low cost, the packing presented chemical resistance to different acids. The biological fixed bed up flow reactor with a total volume of 30.7 L was randomly packed with the hexagonal pieces of feldspar. Dispersion test were performed with a tracer (KCl), to estimate the dispersion number <i>(Nd) </i>in the reactor, with and without aeration. It was found that the dispersion increased due to the aeration and exerts a strong influence on reactor performance. A plug flow reactor model with axial dispersion and Monod kinetic was used to describe the carbon removal (COD) in the reactor at different hydraulic loading rates. The wastewater used during the tests was sampled at the exit of the primary settler of a Mexican wastewater treatment plant, being a mixture of industrial and urban effluents, with a COD = 650 mg/L. Four ascendant flow hydraulic loadings (L) from 1.08 x 10<sup>&#150;4</sup> (m<sup>3</sup>/s m<sup>2</sup>) to 4.32 x 10<sup>&#150;4</sup> (m<sup>3</sup>/s m<sup>2</sup>) were tested. The COD removal was about 95%, higher than the 85% reported in other studies.</font></p>     <p align="justify"><font face="verdana" size="2"><b>Keywords: </b>dispersion, modeling, feldspar packing, wastewater secondary treatment.</font></p>     <p align="justify"><font face="verdana" size="2">&nbsp;</font></p>     <p align="justify"><font face="verdana" size="2"><b>Resumen</b></font></p>     ]]></body>
<body><![CDATA[<p align="justify"><font face="verdana" size="2">En el presente trabajo se model&oacute; la remoci&oacute;n de carbono de aguas residuales en un bioreactor piloto de lecho fijo de flujo ascendente con un empaque hexagonal de feldespato. El desempe&ntilde;o del empaque hexagonal de feldespato fue evaluado en el reactor piloto aireado. El empaque fue obtenido mediante extrusi&oacute;n seguida de un proceso de sinterizado a 1100&deg;C durante 4 horas, en la cual se obtuvo la mayor porosidad y &aacute;rea superficial especifica. Adem&aacute;s de su f&aacute;cil preparaci&oacute;n y bajo costo, el empaque de feldespato result&oacute; ser resistente a diferentes &aacute;cidos. El reactor piloto, con volumen total de operaci&oacute;n 30.7 L, fue empacado al azar con el soporte hexagonal de feldespato. Se realizaron pruebas con y sin aireaci&oacute;n, para estimar el n&uacute;mero de dispersi&oacute;n <i>(Nd), </i>utilizando como trazador KCl. Se encontr&oacute; que la dispersi&oacute;n se incrementa con la aireaci&oacute;n y ejerce una fuerte influencia en el desempe&ntilde;o del reactor. Para describir la remoci&oacute;n de carbono (DQO) se utilizo un modelo que considera la dispersi&oacute;n axial en el reactor, as&iacute; como una reacci&oacute;n de remoci&oacute;n de tipo Monod que fue validado a diferentes cargas hidr&aacute;ulicas. Durante los experimentos se utiliz&oacute; agua residual muestreada a la salida del sedimentador primario de una planta mexicana de tratamiento de aguas residuales. El agua residual es una mezcla de agua residual industrial y de agua residual domestica con una demanda qu&iacute;mica de oxigeno (DQO) de 650 mg/L. Las pruebas se realizaron con flujo ascendente y se probaron 4 cargas hidr&aacute;ulicas (L); desde 1.08 x 10<sup>&#150;4</sup>  (m<sup>3</sup>/s m<sup>2</sup>) hasta 4.32 x 10<sup>&#150;4</sup> (m<sup>3</sup>/s m<sup>2</sup>). La remoci&oacute;n DQO alcanz&oacute; un 95 % lo cual es mayor a lo reportado (85%) en otros estudios.</font></p>     <p align="justify"><font face="verdana" size="2"><b>Palabras clave: </b>dispersi&oacute;n, modelo, lecho fijo, feldespato, empaque, reactor, flujo ascendente, agua residual.</font></p>     <p align="justify"><font face="verdana" size="2">&nbsp;</font></p>     <p align="justify"><font face="verdana" size="2"><a href="/pdf/rmiq/v7n3/v7n3a6.pdf" target="_blank">DESCARGAR ART&Iacute;CULO EN FORMATO PDF</a></font></p>     <p align="justify"><font face="verdana" size="2">&nbsp;</font></p>     <p align="justify"><font face="verdana" size="2"><b>References</b></font></p>     <!-- ref --><p align="justify"><font face="verdana" size="2">APHA, AWWA, WPCF. (1995). <i>Standard Methods for the Examination of Water and Wastewater. </i>19<sup>th</sup> ed. American Public health Association, Washington, D.C., U.S.A.    &nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;[&#160;<a href="javascript:void(0);" onclick="javascript: window.open('/scielo.php?script=sci_nlinks&ref=8534777&pid=S1665-2738200800030000600001&lng=','','width=640,height=500,resizable=yes,scrollbars=1,menubar=yes,');">Links</a>&#160;]<!-- end-ref --></font></p>     <!-- ref --><p align="justify"><font face="verdana" size="2">Bruckschen B., Seitz H., Buzug T. M, Tille C., Leukers B., Irsen S. (2005). Comparing Different Porosity Measurement Methods for Characterisation of 3D Printed Bone Replacement Scaffolds. <i>Biomedizinische Technik 50, </i>1609&#150;1610.    &nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;[&#160;<a href="javascript:void(0);" onclick="javascript: window.open('/scielo.php?script=sci_nlinks&ref=8534779&pid=S1665-2738200800030000600002&lng=','','width=640,height=500,resizable=yes,scrollbars=1,menubar=yes,');">Links</a>&#160;]<!-- end-ref --></font></p>     ]]></body>
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