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<front>
<journal-meta>
<journal-id>1027-2852</journal-id>
<journal-title><![CDATA[Biotecnología Aplicada]]></journal-title>
<abbrev-journal-title><![CDATA[Biotecnol Apl]]></abbrev-journal-title>
<issn>1027-2852</issn>
<publisher>
<publisher-name><![CDATA[Editorial Elfos Scientiae]]></publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S1027-28522016000100003</article-id>
<title-group>
<article-title xml:lang="en"><![CDATA[Evaluation of native microorganisms for biodegradation of oil and grease in palm oil refinery effluents]]></article-title>
<article-title xml:lang="es"><![CDATA[Evaluación de microorganismos nativos para la biodegradación de grasas y aceites en efluentes de la refinación de aceite palma]]></article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Agualimpia]]></surname>
<given-names><![CDATA[Bayron]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Otero]]></surname>
<given-names><![CDATA[José Vicente]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Zafra]]></surname>
<given-names><![CDATA[German]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution><![CDATA[,Universidad de Santander UDES Facultad de Ciencias Exactas, Físicas y Naturales Grupo de Investigación en Ciencias Básicas y Aplicadas para la Sostenibilidad, CIBAS]]></institution>
<addr-line><![CDATA[ ]]></addr-line>
<country>Colombia</country>
</aff>
<pub-date pub-type="pub">
<day>00</day>
<month>03</month>
<year>2016</year>
</pub-date>
<pub-date pub-type="epub">
<day>00</day>
<month>03</month>
<year>2016</year>
</pub-date>
<volume>33</volume>
<numero>1</numero>
<fpage>1221</fpage>
<lpage>1226</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http://scielo.sld.cu/scielo.php?script=sci_arttext&amp;pid=S1027-28522016000100003&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://scielo.sld.cu/scielo.php?script=sci_abstract&amp;pid=S1027-28522016000100003&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://scielo.sld.cu/scielo.php?script=sci_pdf&amp;pid=S1027-28522016000100003&amp;lng=en&amp;nrm=iso"></self-uri><kwd-group>
<kwd lng="en"><![CDATA[bioremediation]]></kwd>
<kwd lng="en"><![CDATA[microbial degradation]]></kwd>
<kwd lng="en"><![CDATA[wastewaters]]></kwd>
<kwd lng="en"><![CDATA[oil and grease]]></kwd>
<kwd lng="en"><![CDATA[palm oil mill effluent]]></kwd>
<kwd lng="en"><![CDATA[native microorganisms]]></kwd>
<kwd lng="es"><![CDATA[biorremediación]]></kwd>
<kwd lng="es"><![CDATA[degradación microbiana]]></kwd>
<kwd lng="es"><![CDATA[aguas residuales]]></kwd>
<kwd lng="es"><![CDATA[aceites y grasas]]></kwd>
<kwd lng="es"><![CDATA[efluente de molida de aceite de palma]]></kwd>
<kwd lng="es"><![CDATA[microorganismos nativos]]></kwd>
</kwd-group>
</article-meta>
</front><body><![CDATA[ <DIV class="Sect"   >        <P align="right"   ><font size="2" color="#000000" face="Verdana, Arial, Helvetica, sans-serif"><b>RESEARCH      </b></font></P >       <P align="right"   >&nbsp;</P >   <FONT size="+1" color="#000000">        <P   > </P >       <P   ><font size="4"><b><font face="Verdana, Arial, Helvetica, sans-serif">Evaluation      of native microorganisms for biodegradation of oil and grease in palm oil      refinery effluents </font></b></font></P >       <P   >&nbsp;</P >       <P   > </P >       <P   ><font size="3"><b><font face="Verdana, Arial, Helvetica, sans-serif">Evaluaci&oacute;n      de microorganismos nativos para la biodegradaci&oacute;n de grasas y aceites      en efluentes de la refinaci&oacute;n de aceite palma </font></b></font></P >       <P   >&nbsp;</P >       <P   >&nbsp;</P >       ]]></body>
<body><![CDATA[<P   > </P >       <P   ><b><font size="2" face="Verdana, Arial, Helvetica, sans-serif">Bayron Agualimpia,      Jos&eacute; Vicente Otero, German Zafra </font></b></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">Grupo de Investigaci&oacute;n      en Ciencias B&aacute;sicas y Aplicadas para la Sostenibilidad, CIBAS, Facultad      de Ciencias Exactas, F&iacute;sicas y Naturales, Universidad de Santander      UDES. Campus Lagos del Cacique, Calle 70 No. 55-210, Bucaramanga, Santander,      680003, Colombia. </font></P >       <P   >&nbsp;</P >       <P   >&nbsp;</P >   </font>   <hr>   <FONT size="+1" color="#000000">        <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>ABSTRACT </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">The use of novel      mixed microbial consortia composed of native yeast and bacteria was evaluated      for the treatment of palm oil mill effluents (POME) from an oil refining process.      For this purpose, 31 native yeast and bacteria isolates demonstrating the      ability to remove fats, oils and greases were evaluated, either as single      organisms or mixed inocula, for the treatment of POMEs. Molecular and biochemical      characterizations revealed that isolates corresponded to <i>Candida</i>, <i>Bacillus</i>      and <i>Pseudomonas genera</i>. Seven mixed inocula, containing the 6 most      degrading isolates, were established and tested for the removal of palm oil      in liquid culture, achieving 68 to 84 % removal after 48 h. The inoculum constituted      by all of the isolates produced the best results with an overall COD reduction      from 1840 to 260 mg/L (84 %), evidencing a synergic effect of the microorganisms.      The use of the same inoculum for the treatment of a palm oil mill effluent      led to a removal of 75 % organic matter and 72 % oil and grease after 48 h.      Our results demonstrated the ability of these isolates to use palm oil as      sole carbon source and effectively decrease the concentration of pollutants      in palm oil mill effluents in a short period of time. The use of these microorganisms      may provide adaptive advantages that could improve POME remediation processes,      especially with mixtures of native bacteria and yeast able to degrade palm      oil as sole carbon source. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><i><b>Keywords</b></i>:      bioremediation, microbial degradation, wastewaters, oil and grease, palm oil      mill effluent, native microorganisms. </font></P >   </font>   <hr>   <FONT size="+1" color="#000000">        <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>RESUMEN </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">En este trabajo se      evaluaron 31 aislados microbianos nativos con habilidad de remover grasas      y aceites para el tratamiento de efluentes de la refinaci&oacute;n de aceite      palma (POMEs), us&aacute;ndolos como organismos simples o consorcios. La caracterizaci&oacute;n      de los microorganismos mostr&oacute; que e</font><font size="2" face="Verdana, Arial, Helvetica, sans-serif">stos      correspond&iacute;an a los g&eacute;neros <i>Candida</i>, <i>Bacillus</i>      y <i>Pseudomonas</i>. El uso de siete in&oacute;culos mixtos, conformados      por diferentes combinaciones de los seis aislados con mayor actividad degradadora,      condujo a una remoci&oacute;n del 68 al 84 % de aceite de palma en medio l&iacute;quido      despu&eacute;s de 48 h de tratamiento. El in&oacute;culo constituido por todos      los aislados produjo los mejores resultados con una reducci&oacute;n de la      DBO de 1840 to 260 mg/L (84 %), evidenci&aacute;ndose un efecto sin&eacute;rgico      entre los microorganismos. El uso del mismo in&oacute;culo para el tratamiento      de POMEs llev&oacute; a una remoci&oacute;n del 75 % de la materia org&aacute;nica      y 72 % de grasas y aceites despu&eacute;s de 48 h. Nuestros resultados demuestran      la habilidad de estos aislados para utilizar aceite de palma como &uacute;nica      fuente de carbono y disminuir eficientemente la concentraci&oacute;n de contaminantes      en los POMEs en un periodo corto de tiempo. El uso de estos microorganismos      puede proveer ventajas adaptativas que podr&iacute;an mejorar el tratamiento      de los POMEs, especialmente cuando se usan mezclas de bacterias y levaduras      con capacidad degradadora. </font></P >       ]]></body>
<body><![CDATA[<P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b><i>Palabras clave</i></b>:      biorremediaci&oacute;n, degradaci&oacute;n microbiana, aguas residuales, aceites      y grasas, efluente de molida de aceite de palma, microorganismos nativos.      </font></P >   </font>   <hr>   <FONT size="+1" color="#000000">        <P   >&nbsp;</P >       <P   >&nbsp;</P >       <P   ><font size="3" face="Verdana, Arial, Helvetica, sans-serif"><b>INTRODUCTION </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">Palm oil has become      a major global agricultural product, which is used for food and non-food applications,      the manufacturing of value-added products, and more recently, a promising      feedstock for biofuel production [1]. Currently, there are about five million      hectares of palm planted in the world, representing 16 million tons of annual      production. Colombia is the largest producer of palm oil in the Americas and      the fourth largest in the world after Malaysia, Indonesia and Nigeria [2].      Much of this oil is obtained from the African oil palm (<i>Elaeis guineensis</i>      Jacq.) and hybrids with other species as well. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">Despite the economic      importance of the oil palm industry, it has also contributed to environmental      pollution as a consequence of the production of large amounts of by-products      from the oil extraction process. In particular, the palm oil mill effluent      (POME), is a thick brownish wastewater generated from palm oil milling activities,      which produces large amounts of methane gas from its anaerobic process, and      this gas is known to exert over 20 times the Global Warming Potential (GWP)      of other gasses [3]. Importantly, POME frequently has high amounts of oil      and grease (O&amp;G), total suspended solids (TSS), chemical oxygen (COD)      and biochemical oxygen demand (BOD) which counts for most of the contaminant      effects on watercourses due to their highly polluting properties and acidic      nature. The discharge of these effluents into water bodies may produce important      effects such as an alteration of pH, or an increase in the BOD and COD. In      addition, water contamination could prevent the passage of light and oxygen,      negatively affecting the photosynthetic processes and generating eutrophication      and potentially, toxic compounds [4-6]. Thus, treatment of POME is essential      to avoid environmental pollution in water bodies. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">An interesting option      for the management of POME and other liquid wastes relies on biological treatment,      which allows the degradation of the organic contaminants present in effluents,      while generating organic sludge that can be later exploited for the production      of compost [7]. Bioaugmentation, or the addition of exogenous bacteria, has      been demonstrated to be an efficient method for the reduction of organic pollutants      in POME, enhancing the overall degradative performance by adding microorganisms      with high degradation ability of specific environmental pollutants [8-10].      Previous studies have shown that bioaugmentation facilitates the degradation      of high amounts of grease and other organic contaminants present in effluents      via addition of POME-isolated microorganisms demonstrating lipolytic activity      isolated from the POME such as aerobic bacteria <i>Pseudomonas</i> spp. and      <i>Bacillus</i> spp. or yeasts such as <i>Candida</i> spp. and <i>Yarrowia</i>      spp. [11]. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">While several microbial      species with the ability to remediate POME have been identified, there are      few studies on the ability of environmental consortia to degrade these wastewaters,      whether through use of using native aerobic microbial enrichments, or constructed      consortia consisting of microorganisms isolated from highly polluted wastes.      In this study, we focused on the use of mixed microbial consortia composed      by yeast and bacteria. The use of this type of uncommon mixed cultures would      be beneficial, as POME is composed of heterogeneous matrices containing complex      combinations of organic compounds, which can be co-metabolically degraded      by a community of aerobic organisms belonging to different domain ranks and      taxa [12]. Moreover, the use of native microorganisms for the remediation      of POMEs would improve the ability of microorganisms to adapt, survive and      degrade effluents containing high amounts of organic suspended solids, O&amp;G,      COD and BOD. Thus, this study was aimed to isolate native microorganisms with      the ability to metabolize O&amp;G and evaluate their potential, either as      single organisms or mixed inocula, for the treatment of POME from palm oil      refining processes. </font></P >       <P   >&nbsp;</P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b><font size="3">MATERIALS      AND METHODS </font></b> </font></P >       ]]></body>
<body><![CDATA[<P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>Samples from O&amp;G-containing      wastes </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">Solid and liquid      wastes (POME) from a grease trap of a palm oil refining process, conducted      at C.I Saceites S.A.S. (Santander, Colombia), were used in this study. Waste      composite samples of either two liters or two kilograms were obtained using      250 mL Winkler amber flasks (Witeg, Germany) at different points and depths      across the oil trap. Samples were stored at 4 &deg;C until use. A physicochemical      characterization was conducted for all POME samples, consisting of the measurement      of pH, COD, TSS and O&amp;G content according to EPA methods 150.0, 410.4,      340.2, and ASTM Soxhlet method D5369, respectively. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>Isolation and      selection of native microorganisms </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">Microbial isolation      from liquid and solid oily wastes was carried out in several successive steps.      First, a non-selective pre-enrichment was performed by adding 10 g or 10 mL      (depending on the sample) to 70 mL of Basal Saline Medium (BSM; 3 g/L (NH<sub>4</sub>)<sub>2</sub>SO<sub>4</sub>;      0.9 g/L K<sub>2</sub>HPO<sub>4</sub>; 0.6 g/L KH<sub>2</sub>PO<sub>4</sub>;      0.2 g/L MgSO<sub>4</sub>; 0.5 g/L CaCO<sub>3</sub>; 0.1 g/L yeast extract).      Flasks were incubated with constant agitation at 150 rpm at 30 &deg;C until      turbidity in the medium was observed. Subsequently, a selective step was performed      by diluting 10 mL from the pre-enrichment culture in 90 mL of modified BSM      using 0.05 % palm oil as sole carbon source, using the same conditions described      above. For isolation, 1 mL of enrichment culture was streaked onto solid modified      BSM and incubated at 30 &deg;C for 96 h. Individual colonies were picked and      transferred to new plates of BSM containing palm oil as carbon source, and      the process repeated. Macroscopic and microscopic morphologic features of      colonies were verified, providing a basis </font><font size="2" face="Verdana, Arial, Helvetica, sans-serif">for      the establishment of pure cultures. Each pure culture (from a single colony)      was considered an individual microbial isolate. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>Screening of microbial      O&amp;G-degrading potential </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">The oil-degrading      potential of isolated microorganisms was assessed by observation of differences      in their growth using palm oil as sole carbon source in liquid culture. Each      isolate was used to inoculate 2 mL of liquid BSM containing 0.05 % (w/v) palm      oil, and incubated at 30 &deg;C and 150 rpm for 48 h. Changes in culture medium      such as turbidity increase, color variation and oil disappearance were evaluated      qualitatively. Isolates showing presumable lipolytic activity were identified      using API&reg; 20E, API&reg; 20NE and API&reg; 20C AUX systems (Biomerieux,      USA) and by PCR amplification and sequencing of the prokaryotic 16S rRNA and      eukaryotic ITS1, ITS2 and 5.8S rRNA regions, according to previously reported      primers and conditions [13]. BSM tubes without palm oil were inoculated with      each isolate, as well as non-inoculated BSM tubes containing 0.05 % oil, were      included as controls. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>Evaluation of      microbial antagonism </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">To determine if any      negative interspecies interaction occurred between isolates, the in vitro      evaluation of bacteria to bacteria, yeast to bacteria and yeast to yeast antagonism      of isolates showing the highest O&amp;G removal ability was carried out in      plate assays according to the disk method described by Bauer <i>et al</i>.      [14]. Isolates were grown in 50 mL of liquid BSM medium (containing 20 g/L      glucose), at 30 &deg;C with constant agitation at 200 rpm until cultures reached      an optical density of 0.14 at 600 nm (comparable to a MacFarland standard      No. 0.5). Subsequently, 100 &mu;L of each culture (approximately 1.5 &times;      10<sup>7</sup> c.f.u.) were spread over the surface of BSM2 plates with 1.5      % agar, and 5 mm diameter nitrocellulose discs (Millipore, USA) impregnated      with 50 &mu;L of 24-h culture supernatants of the other isolates were placed      onto the surface. Plates were incubated at 30 &deg;C and the inhibition halos      were measured every 24 h for 2 days. Discs without culture supernatants were      used as controls. Assays were performed in triplicate. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>Determination      of COD </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">The degradation of      O&amp;G was indirectly measured by means of the COD removal, as it allows      the quantitation of organic matter in liquid samples (including O&amp;G).      COD values were determined in triplicate according to method HACH 8000 [15].      Controls consisted of non-inoculated BSM flasks under the same conditions      described for the inoculated ones. The indirect measurement of the degradation      was calculated by the equation: </font></P >       ]]></body>
<body><![CDATA[<P align="center"   ><img src="/img/revistas/bta/v33n1/fr0103116.gif" width="467" height="87"></P >       
<P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">Where COD<sub>i</sub>      was the initial concentration of COD and COD<sub>f</sub> the final concentration      of COD in mg/L. This was corroborated through a standard curve, in which solutions      with different palm oil content gave a correction factor of 1.25 (1.25 mg/L      palm oil corresponded to 1 mg/L COD). </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>Evaluation of      isolates and constructed consortia for O&amp;G removal in liquid culture </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">The ability of selected      isolates to degrade palm oil was tested in BSM tubes containing 2000 mg/L      palm oil. For this, 20 mL of 10<sup>9</sup> c.f.u./mL lag-phase cultures from      each isolate were inoculated into glass flasks containing 200 mL BSM plus      palm oil and incubated at 27 &plusmn; 3 &deg;C with constant aeration. The      degrading ability of individual isolates was determined by the decrease in      O&amp;G content (measured as COD) during 48 and 72 h with respect to controls.      Subsequently, to test for possible synergistic effects between isolates, consortia      were constructed using combinations of yeasts and bacteria. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>O&amp;G removal      from POME by mixed inocula in a batch reactor </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">To determine the      capacity of constructed consortia to degrade O&amp;G in a batch reactor, a      mixed inocula demonstrating lipolytic activity was generated using palm oil-degrading      bacterial and yeast isolates that exhibited no negative interaction as outlined      above. O&amp;G degradation of this consortium was evaluated in a 4-L bioreactor      using 3 L of POME from the palm oil refining process. Microbial isolates were      grown separately on BSM with 0.05 % (v/v) palm oil, and used to inoculate      in the bioreactor at a final concentration of 10<sup>9</sup> c.f.u. each (1:1      ratio) and the volume adjusted to four liters with POME. The process was carried      out for 48 h at 27 &plusmn; 3 &ordm;C with constant aeration. O&amp;G removal      activity was determined by means of the O&amp;G and COD decrease at the end      of the process. O&amp;G determinations were performed according to the ASTM      Soxhlet method D5369. Assays were carried out in triplicate. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>Experimental design      and statistical analysis </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">The experimental      consisted of a random 2&times;2 factorial design. Data from COD measurements      were analyzed by analysis of variance (ANOVA) followed by a Bonferroni multiple      comparison test with the SPSS Statistics Software version 14 (IBM), considering      statistically significant differences those with a p &lt; 0.05. </font></P >       <P   >&nbsp;</P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b><font size="3">RESULTS      AND DISCUSSION </font> </b> </font></P >       ]]></body>
<body><![CDATA[<P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">The isolation of      native microorganisms with potential to degrade oily wastes is a key step      for providing safer and faster methods for the remediation of effluents from      the refinement of palm oil. In this study, we used liquid and solid wastes      from palm oil refinement as a reservoir of microorganisms with potential to      degrade O&amp;G and other pollutants at high loadings, while evaluating them      for the treatment of POME. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>Physicochemical      characteristics of oily wastes </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">As shown in <a href="/img/revistas/bta/v33n1/t0103116.gif">table      1</a>, POME samples used for microbial isolation showed slightly acidic pH      values (5.43 &plusmn; 0.51), whereas for solid samples were closer to neutrality      (6.20 &plusmn; 0.36). TSS, COD and O&amp;G levels were variable with mean      values of 2943 &plusmn; 0.76), 11 247 &plusmn; 1.85 and 4907 &plusmn; 0.67      mg/L, respectively. These findings are in agreement with previous studies      showing low pH values (3.8 to 4.7) and high values for solids (18 000 mg/L),      COD (50 000 mg/L) and greases (7000 mg/L) in wastewaters and POMEs from palm      oil refining processes [6, 15]. These high levels are thought to be a consequence      of the free fatty acids produced during oil treatment, which can vary according      to the type of fruit processed, its age and the method employed for oil extraction,      whiles gums, proteins and microbial biomass present during the process contribute      as well [17]. In practice, this also increases the chances of isolating microorganisms      </font><font size="2" face="Verdana, Arial, Helvetica, sans-serif">able to      degrade elevated concentrations of these compounds. That is, the complex nature      and high amounts of organic pollutants present in the wastes could favor the      adaptation and survival of microorganisms with the ability to tolerate and      use them as a substrate for its growth [13, 18]. </font></P >       
<P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">As reported previously,      a prior exposure to high concentrations of free fatty acids largely determined      the type and number of O&amp;G-degrading organisms found in POMEs, which in      turn strongly influenced the degradative ability of the native microorganisms      [19]. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>Isolation and      screening of O&amp;G-degrading microorganisms</b> </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">A total of 31 microbial      isolates, corresponding to 17 yeast and 14 bacteria, were obtained from liquid      and solid samples based on their ability to use palm oil as sole carbon source      in solid medium. Only 11 out of these 31 microbial isolates showed visible      lipolytic activity evidenced by changes in the turbidity, color and a reduction      in the palm oil layer present in MBS tubes. Initially, the API biochemical      characterization suggested that isolates corresponded to <i>Yarrowia</i>,      <i>Candida</i>, <i>Bacillus</i> and <i>Pseudomonas</i> genera. However, molecular      characterization of 16S rRNA and ITS1, ITS2 and 5.8S rRNA sequences confirmed      that isolates actually corresponded to <i>Candida palmioleophila</i>, <i>Bacillus</i>      sp. and <i>Pseudomonas</i> sp. (<a href="/img/revistas/bta/v33n1/t0203116.gif">Table 2</a>). </font></P >       
<P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">This group of microorganisms      have been previously described to transform and degrade vegetable, animal      and mineral O&amp;G, mainly due to the production of lipases and other enzymes      capable of completely or partially metabolize these compounds [20]. Fakharedine      <i>et al</i>. [21] described the isolation of lipolytic strains of <i>Candida      wickerhamii</i> and <i>Candida boidinii</i> from wastes derived from olive      oil production, and <i>Pseudomonas</i> sp. and <i>Pseudomonas aeruginosa</i>      have been also reported as producers of lipases in tributyrin agar [22, 23].      Since POME and other palm oil-derived wastewaters mainly contain fatty substances,      organic compounds and proteins, an inoculum composed by <i>Pseudomonas</i>,      <i>Bacillus</i> and <i>Candida</i> species could be a good option to enhance      the degradation of such wastewaters due to a complementary action of their      enzymatic mechanisms and long term survival [24]. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">In order to evaluate      the degradation potential of these microorganisms, we screened their ability      to metabolize O&amp;G in liquid medium containing palm oil as carbon source      and all of the 11 isolates showing lipolytic activity produced a substantial      decrease in O&amp;G concentrations in liquid MBS cultures. Five yeast (CL01,      CL05, CL08, CL09, CL11) and one bacterial (CB10) isolates promoted more than      50 % O&amp;G removal after 48 h, and the highest after 72 h with (CL11, 79      %; CL08, 78 %; CL05, 77%; CL09, 76 %; CB10, 67 %; CL01, 66 %) (<a href="/img/revistas/bta/v33n1/f0103116.gif">Figure      1</a>), with no significant differences between them. A different behavior      was observed in the case of isolates CL04 (<i>C. palmioleophila</i>) and CB02      (<i>Bacillus</i> sp.), which removed O&amp;G in a lower extent achieving only      37 and 49 % removal, respectively, being significantly lower than the other      six isolates (p = 0.04 and p = 0.049, respectively). </font></P >       
<P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">In general, individual      yeast isolates were more effective than individual bacterial isolates for      O&amp;G removal, even when the latter grew faster in culture tubes (data not      shown). This could indicate a higher activity or secretion of lipases by these      <i>Candida</i> isolates, even though some <i>Bacillus</i> lipases have been      reported to have advantages over yeast lipases, such as the ability to maintain      activity over broad temperature and pH ranges [25, 26]. There is also the      possibility </font><font size="2" face="Verdana, Arial, Helvetica, sans-serif">of      the secretion of other fungal and bacterial hydrolytic enzymes useful for      the degradation of O&amp;G, such as cellulases, proteases, laccases and catalases      [27]. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b>O&amp;G removal      in POMEs by mixed inocula</b> </font></P >       ]]></body>
<body><![CDATA[<P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">Our results indicated      that all of the evaluated isolates were suitable to construct mixed inocula,      since antagonism tests did not show any inhibitory effects between yeast and      bacteria. Additionally, comparison of the growth curves showed that bacterial      isolates, particularly <i>Bacillus</i> sp. CB02, presented the highest growth      rate in presence of 0.05 % palm oil whereas yeast isolates showed the lowest      (data not shown), and it may be possible that the combined activity of these      two groups of microorganisms could improve overall degradation. Thus, based      on the observed re-sults from the lipolytic screening, growth behavior and      the lack of major antagonistic effects, six isolates (CL01, CL05, CL08, CL09,      CB10 and CL11) showing the best O&amp;G removal results were selected to develop      seven different mixed inocula combining bacterial and yeast strains (<a href="/img/revistas/bta/v33n1/f0203116.gif">Figure      2</a>) and one of them included all the six individual isolates showing higher      O&amp;G removal rates. O&amp;G removal tests in liquid culture by the seven      established mixed inocula demonstrated similar degradation levels, ranging      from 68 to 84 % after 48 h (<a href="/img/revistas/bta/v33n1/f0203116.gif">Figure 2</a>). No significant      differences were observed between Mix5, Mix6 and Mix7 (p = 0.1), but interestingly,      the inoculum constituted by six yeast/bacterial isolates (Mix7) produced the      best results with an overall COD reduction from 1840 to 260 mg/L (84 %), evidencing      a synergistic effect between microorganisms. O&amp;G removal in non-inoculated      controls (12 %) was significantly lower (p = 0.001) than inoculated treatments.      </font></P >       
<P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">As Mix 7 showed the      highest degradative rates in flask experiments, and it also included the six      isolates producing the best degradation results, the evaluation of O&amp;G      removal in POME in a batch reactor was carried out using this mixed inoculum.      In addition, previous studies have suggested an additive effect of individual      degrading microorganisms in a mixed consortia, in which the microorganisms      better adapted to the new pollution conditions gradually displaces and replace      those organisms less well adapted. Toxic effects of POME are effective in      the selection of more adapted strains, and enrichment occurs when microorganisms      are able to use the pollutant as a source of carbon and energy, so having      more individual strains in a consortium would increase consortia stability      and survival when used in POMEs [28-30]. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">As observed in <a href="/img/revistas/bta/v33n1/t0303116.gif">table      3</a>, O&amp;G and COD removal was high, reaching a 75 % COD reduction (3588      mg/L removed) and 72 % O&amp;G degradation (809 mg/L) after 48 h. Comparatively,      a non-inoculated control showed a COD reduction of 51 % (1600 mg/L) and 50      % O&amp;G degradation (809 mg/L), and thus inoculation with the constructed      community described here represented respective increases for COD reduction      and O&amp;G removal of 225 and 144 %, respectively. These removal levels in      control could be attributed to native microorganisms already present in palm      oil-wastewaters, which in fact contains most of the isolated microorganisms      described in this study. In spite of the increased O&amp;G degradation, a      20 % increase in TSS was observed. This may have occurred as a consequence      of the increase in microbial biomass, produced in turn by the degradation      of organic matter. Notably, the results from O&amp;G quantitation using COD      during POME treatment corresponded with those obtained with the Soxhlet method      (51 vs. 50 % and 75 vs. 72 %), evidencing a good correlation between the two      methods. </font></P >       
<P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">Overall, O&amp;G      removal by the constructed consortia described here was shown to be higher      and faster than with other reported mixed inocula. For example, a mixed inoculum      composed by one strain of <i>Candida cylindracea</i> and three of <i>Yarrowia      lipolytica</i> decreased 30-70 % COD after 100 h of treatment [31]; Bala <i>et      al</i>. [32] also described the removal of 90 % COD in POME samples only after      5 days treatment using a consortium composed by two <i>Bacillus</i> strains.      Similar results were obtained by Prasad and Manjunath [33] and Bhumibhamon      <i>et al</i>. [4] using a mixture of <i>P. aeruginosa</i>, <i>Pseudomonas</i>      sp., <i>Bacillus</i> sp. and <i>Acinetobacter calcoaceticus</i> after 12 days      treatment of POME samples [4, 33]. Additionally, the results presented here      are consistent with previous reports showing an enhanced degradation in POME      by bacteria-yeast co-cultures, reaching up to 72 % O&amp;G and 80 % COD reduction      [4]. This highlights the advantage of using mixed cultures for the bioremediation      of POMEs, which could confer several improvements such as an increased co-metabolism      and better tolerance to pH and temperature variations [34]. </font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">Additionally, most      of the microbial lipases are inducible and secreted as extracellular enzymes      upon induction with fatty acids [35]. Therefore, the use of yeast-bacteria      mixed inocula would also improve the degradation of high molecular weight      greases by yeast after the induction of the bacterial enzymes able to degrade      low molecular weight molecules. Also, this type of metabolism could be effectively      used for the degradation of other related pollutants. In fact, an increased      co-metabolic degradation of total petroleum hydrocarbons in soil has been      achieved by the same microorganisms able to remediate POMEs [36, 37]. </font></P >       <P   >&nbsp;</P >       <P   ><font size="3" face="Verdana, Arial, Helvetica, sans-serif"><b>CONCLUSIONS </b></font></P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">The results of this      study showed that the bioaugmentation using native microorganisms isolated      from oily residues, either single or mixed, can be efficiently used to greatly      improve the removal of grease, oils and organic matter present in wastewaters      from palm oil extraction. Our results demonstrated the ability of these isolates      to use palm oil as sole carbon source and effectively decrease the concentration      of organic compounds in POME, including O&amp;G, in a short period (48 h).      The use of these microorganisms may provide adaptive advantages that could      improve POME remediation process, especially when lipolytic mixtures of native      bacteria and yeast are used. Further studies would be necessary in order to      clarify the role of each isolate in the mixed inoculum during the degradation      of O&amp;G in POMEs, as well as to test the potential to produce and secrete      lipolytic enzymes and other oxidoreductases. </font></P >       <P   >&nbsp;</P >       <P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif"><b><font size="3">ACKNOWLEDGEMENTS      </font> </b> </font></P >       ]]></body>
<body><![CDATA[<P   ><font size="2" face="Verdana, Arial, Helvetica, sans-serif">This work was supported      by the Universidad de Santander grant 017-11. The authors would like to thank      Dr. Eric Charles Peterson for critical reading of the manuscript. </font></P >       <P   >&nbsp;</P >       <P   ><font face="Verdana, Arial, Helvetica, sans-serif" size="3"><b>REFERENCES</b></font></P >       <!-- ref --><P   ><font size="2" color="#000000" face="Verdana, Arial, Helvetica, sans-serif">1.      Aluyor EO, Obahiagbon KO, Orijesu M. Biodegradation of vegetable oils: A review.      Sci Res Essays. 2009;4:543-8.     </font></P >   </font>        <!-- ref --><p   ><font size="2" color="#000000" face="Verdana, Arial, Helvetica, sans-serif">2.      USDA. Oilseeds: World markets and trade. 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<ref-list>
<ref id="B1">
<label>1</label><nlm-citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname><![CDATA[Aluyor]]></surname>
<given-names><![CDATA[EO]]></given-names>
</name>
<name>
<surname><![CDATA[Obahiagbon]]></surname>
<given-names><![CDATA[KO]]></given-names>
</name>
<name>
<surname><![CDATA[Orijesu]]></surname>
<given-names><![CDATA[M]]></given-names>
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<article-title xml:lang="en"><![CDATA[Biodegradation of vegetable oils: A review]]></article-title>
<source><![CDATA[Sci Res Essays]]></source>
<year>2009</year>
<volume>4</volume>
<page-range>543-8</page-range></nlm-citation>
</ref>
<ref id="B2">
<label>2</label><nlm-citation citation-type="book">
<collab>USDA</collab>
<source><![CDATA[Oilseeds: World markets and trade]]></source>
<year>2015</year>
<publisher-loc><![CDATA[Washington, DC ]]></publisher-loc>
<publisher-name><![CDATA[United States Department of Agriculture Foreign Agricultural Service]]></publisher-name>
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</ref>
<ref id="B3">
<label>3</label><nlm-citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname><![CDATA[Choi]]></surname>
<given-names><![CDATA[W-H]]></given-names>
</name>
<name>
<surname><![CDATA[Shin]]></surname>
<given-names><![CDATA[C-H]]></given-names>
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