<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">AiM</journal-id><journal-title-group><journal-title>Advances in Microbiology</journal-title></journal-title-group><issn pub-type="epub">2165-3402</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/aim.2016.69063</article-id><article-id pub-id-type="publisher-id">AiM-69433</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Biomedical&amp;Life Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Proliferation of Microorganisms in Acidic Fermentation of &lt;i&gt;Elaeis guineensis&lt;/i&gt; L. Waste
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>M.</surname><given-names>Adedolapo Orimoloye</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>A.</surname><given-names>Isaac Sanusi</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>Department of Microbiology, Federal University of Technology, Akure, Nigeria</addr-line></aff><pub-date pub-type="epub"><day>02</day><month>08</month><year>2016</year></pub-date><volume>06</volume><issue>09</issue><fpage>644</fpage><lpage>649</lpage><history><date date-type="received"><day>13</day>	<month>June</month>	<year>2016</year></date><date date-type="rev-recd"><day>accepted</day>	<month>31</month>	<year>July</year>	</date><date date-type="accepted"><day>3</day>	<month>August</month>	<year>2016</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  An investigation into the type of fermentation oil palm fruit waste undergoes and the probable microorganisms involved within a short period was carried out using simple fermenter. The temperature was determined using mercury thermometer, the pH of the medium was monitored with calibrated pH meter and the titratable acidic was determined using standard technique. The microbial profile of the medium was also evaluated using standard procedures. The highest temperature value was observed at day 0 (32.65&amp;deg;C) and the lowest at day 1 (29.50&amp;deg;C). The pH values of the fermentation oil palm fruit waste ranged between 4.15 - 4.60. The highest pH value was obtained at day 3 of the fermentation which was 4.60. The titratable acidity showed variation from day 0 - 2 and then with a continuous decrease till day 5. The least titratable acidity was obtained at day 5 (0.03) and the highest at day 2 (0.77). Bacteria load decreases from 1.0 
  &#215; 10
  <sup>8</sup>
   - 1.6 &#215; 10
  <sup>7 </sup>
  cfu/ml, while the fungi population increases from day 0 to day 5 of the fermentation period (1 &#215; 10
  <sup>3</sup>
   - 2 &#215; 10
  <sup>4 </sup>
  sfu/ml). Bacterial isolates obtained were
   Micrococcus leteus
  ,
   Proteus vulgaris
  ,
   Bacillus cereus
  ,
   Baccillus subtilis
  ,
   
  and
   Staphylococcus aureus 
  while the fungal isolates obtained were 
  Aspergillus niger
  ,
   Neurospora crassa
  ,
   Brachysporium 
  spp,
   
  and 
  Saccharomyces cerevisiae. 
  It can be concluded that oil palm waste fermentation is an acidic fermentation that involved mesophiles microbes. And with these, several tons of oil palm epicarp waste can be optimally fermented (though with further research) and used for other purposes thereby reducing environmental pollution that would have resulted leaving this oil palm fruit waste in the environment.
 
</p></abstract><kwd-group><kwd>&lt;i&gt;Elaeis guineensis&lt;/i&gt; L.</kwd><kwd> Fermentation</kwd><kwd> Microorganism</kwd><kwd> Proliferation</kwd><kwd> Waste</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Solid substrate fermentation has been exploited for the production of value added products namely antibiotics, alkaloids, plant growth factors, bio-fuels, enzymes, organic acid and biological detoxification of agro-industrial residues, nutritional enrichment, pulping, bio-pharmaceuticals product [<xref ref-type="bibr" rid="scirp.69433-ref1">1</xref>] . Fermentation is one of the oldest applied biotechnological methods having been employed in food processing for many years [<xref ref-type="bibr" rid="scirp.69433-ref2">2</xref>] . Fermentation either naturally or with selected microbial inoculums has also been extensively used to enhance the nutrient potential of oil palm and its by-products for human use, and contribute significantly to food security. It also enhances micro content bioavalability and aids degrading anti-nutritional factors [<xref ref-type="bibr" rid="scirp.69433-ref3">3</xref>] . Microbial growth in agricultural and food processing wastes offers the potential for additional food and feed of a wide variety for domestic and farm animals. The microbes can produce many times as much protein per area than slow growing plants and animals. Thus high fat content and low protein crops like oil palm waste can be enhanced nutritionally through microbial conversion.</p><p>The oil palms comprise two species of the Arecaceae or palm family. They are used in commercial agriculture in the production of palm oil. The African oil palm Elaeis guineensis is native to West Africa occurring between Angola and Gambia, while the American Oil Palm Elaeis oleifera is native to tropical Central America and South America. Each palm fruit is made up of an oily, fleshy outer layer, with a single seed (the palm kernel), also rich in oil. Oil is extracted from both the pulp of the fruit (palm oil, edible oil) and the kernel (palm kernel oil, used in foods and for soap manufacture). After oil extraction, the remaining shaft is thrown away as waste. This can become nuisance to the environment, if not properly disposed. Palm oil increasing use in the commercial food industry though buoyed by its cheaper pricing, high oxidative stability of the refined product and high levels of natural antioxidants [<xref ref-type="bibr" rid="scirp.69433-ref4">4</xref>] , has also lead to increase in the amount of oil palm waste generated.<sup> </sup></p><p>The oil palm by-product is acceptable to ruminant at low level inclusion in the diet. Crude protein and crude fiber digestibility decrease when the level of inclusion exceeds 25% - 30%. The fiber can be dried and pelletized to overcome the problem of poor keeping quality and bulkiness. Fermentation can be employed to improve the protein content and generally the digestibility of this waste. This research is sought to investigate the type of fermentation oil palm fruit waste undergoes and the probable microorganisms involved within a short period. Thereby, encouraging its removal from the environment, to be use as inclusion in animal diets.</p></sec><sec id="s2"><title>2. Materials and Methods</title><sec id="s2_1"><title>2.1. Collection of Sample</title><p>Fresh palm oil waste was obtained from Nigerian Institute For Oil Palm Research (NIFOR) near Benin City, Edo state (6˚30'N 6˚00'E). The types of fruit processed are mixture of Dura and Tenera varieties.</p></sec><sec id="s2_2"><title>2.2. Solid State Fermentation</title><p>Dried sample of oil palm waste was weighed (about 500 g) and rapped with foil paper and was sterilized in the autoclave for 15 minutes at 121˚C, after which the oil palm waste was aseptically transferred into a sterile bowl (fermenter), 500 mls of sterile water was aseptically added and then allowed to ferment for 5 days. Sample was taken for titratable acidic daily while the pH and the temperature were also determined daily in the fermenter using pH meter and mercury thermometer respectively. The microbial loads were monitored daily. Isolation of bacteria and fungi from the fermenting palm waste was carried out on the fifth day.</p></sec><sec id="s2_3"><title>2.3. Physiochemical Parameters</title><p>The physiochemical parameters measured were: pH, temperature, and titrable acidity determination [<xref ref-type="bibr" rid="scirp.69433-ref5">5</xref>] .</p></sec><sec id="s2_4"><title>2.4. Enumeration of Fungi and Bacteria Counts</title><p>Spore/colony counting was carried out by counting the number of visible spores/colonies that appeared on the agar plates. Nutrient agar was used for bacteria culture while potatoes dextrose agar was used for fungi culturing. Calculation of spore/colony forming unit (sfu/cfu) per ml for fungi and bacteria were based on the volume of the sample used.</p></sec><sec id="s2_5"><title>2.5. Cultural and Microscopic Characteristics of Fungi</title><p>The fungi were isolated on potatoes dextrose agar and each colony was identified using visible observation and microscope at low power magnification (&#215;40), the parameters such as colony colour, characteristics of the submerged hyphae rhizoid, spiral or regular and characteristic shape of mature fruiting bodies were all observed. Microscopic characterization involved transferring a small piece of mycelium free of medium using a sterile inoculating loop unto a clean glass slide containing a drop of cotton blue-in-lactophenol and the mycelium was spread properly. The preparation was covered with a clean grease free cover slip and observed under medium power (&#215;100). The observations made were used in identifying the fungi organism [<xref ref-type="bibr" rid="scirp.69433-ref6">6</xref>] .</p></sec><sec id="s2_6"><title>2.6. Biochemical and Morphological Identification of Bacteria Isolates</title><p>Bacteria were isolated using nutrient agar and the individual colonies were identified by morphological and biochemical techniques using methods described by [<xref ref-type="bibr" rid="scirp.69433-ref7">7</xref>] [<xref ref-type="bibr" rid="scirp.69433-ref8">8</xref>] .</p></sec></sec><sec id="s3"><title>3. Results</title><p>A total of 5 bacterial isolates were obtained based on their morphological and biochemical properties for the bacteria and a total of 4 fungal isolates were obtained. The bacteria were: Micrococcus leteus, Proteus vulgaris, Bacillus cereus, Baccillus subtilis, Staphylococcus aureus. And fungi were: Aspergillus niger, Neurospora crassa, Brachysporium spp, and Saccharomyces cerevisiae. <xref ref-type="table" rid="table1">Table 1</xref> shows the microbial population of oil palm waste during fermentation. Oil palm wastes microbial load decreases from 1.0 &#215; 10<sup>8</sup> - 1.6 &#215; 10<sup>7</sup> cfu/ml. While the fungi growth increases from day 0 to day 5 of the fermentation period (1 &#215; 10<sup>3</sup> - 2 &#215; 10<sup>4</sup> sfu/ml).</p><sec id="s3_1"><title>3.1. pH Values Observed during Fermentation</title><p>The pH values of the fermentation process were below the neutral pH of 7.00. It ranged between 4.15 - 4.60 (<xref ref-type="fig" rid="fig1">Figure 1</xref>). The highest pH value was obtained at day 3 of the fermentation which was 4.60.</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Microbial population of oil palm wastes during liquid state fermentation</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Days</th><th align="center" valign="middle" >Fungi sfu/ml</th><th align="center" valign="middle" >Bacteria cfu/ml</th></tr></thead><tr><td align="center" valign="middle" >Day 0</td><td align="center" valign="middle" >1 &#215; 10<sup>3 </sup></td><td align="center" valign="middle" >1.0 &#215; 10<sup>8 </sup></td></tr><tr><td align="center" valign="middle" >Day 1</td><td align="center" valign="middle" >-</td><td align="center" valign="middle" >2.1 &#215; 10<sup>7 </sup></td></tr><tr><td align="center" valign="middle" >Day 2</td><td align="center" valign="middle" >2 &#215; 10<sup>3 </sup></td><td align="center" valign="middle" >2.8 &#215; 10<sup>7 </sup></td></tr><tr><td align="center" valign="middle" >Day 3</td><td align="center" valign="middle" >2 &#215; 10<sup>4 </sup></td><td align="center" valign="middle" >1.6 &#215; 10<sup>7 </sup></td></tr><tr><td align="center" valign="middle" >Day 4</td><td align="center" valign="middle" >-</td><td align="center" valign="middle" >1.6 &#215; 10<sup>7 </sup></td></tr><tr><td align="center" valign="middle" >Day 5</td><td align="center" valign="middle" >2 &#215; 10<sup>4 </sup></td><td align="center" valign="middle" >2.3 &#215; 10<sup>8 </sup></td></tr></tbody></table></table-wrap><fig id="fig1"  position="float"><label><xref ref-type="fig" rid="fig1">Figure 1</xref></label><caption><title> pH of fermented oil palm waste</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/6-2270781x6.png"/></fig></sec><sec id="s3_2"><title>3.2. Acidity of Oil Palm Waste Observed during Fermentation<sup> </sup></title><p>The titratable acidity showed variation from day 0 - 2 and then with a continuous decrease till day 5. The least titratable acidity was obtained at day 5 with 0.03 and the highest at day 2 with 0.77 (<xref ref-type="fig" rid="fig2">Figure 2</xref>).<sup> </sup></p></sec><sec id="s3_3"><title>3.3. Temperature Observed during Fermentation</title><p><xref ref-type="fig" rid="fig3">Figure 3</xref> show the daily temperature of oil palm waste during the fermentation. The highest value was obtained at day 0 with 32.65˚C and the lowest at day1 with 29.50˚C.</p></sec></sec><sec id="s4"><title>4. Discussion</title><p><xref ref-type="table" rid="table1">Table 1</xref> shows the microbial population of oil palm waste during fermentation. Oil palm wastes bacterial load ranged from 1.0 &#215; 10<sup>8</sup> - 1.6 &#215; 10<sup>7</sup> cfu/ml. While the fungi growth ranged from 1 &#215; 10<sup>3</sup> - 2 &#215; 10<sup>4</sup> sfu/ml. These show there were more bacterial activities in the medium than fungal activities [<xref ref-type="bibr" rid="scirp.69433-ref9">9</xref>] .</p><p>The microorganisms isolated were probably acidophiles either strict acidophile or facultative acidophiles. Since the pH of the fermentation process was acidic throughout the five days period, their survival show they were acid tolerant microbes. Bacillus spp, Aspergillus niger and Saccharomyces cerevisae are common fermentative microbes [<xref ref-type="bibr" rid="scirp.69433-ref10">10</xref>] - [<xref ref-type="bibr" rid="scirp.69433-ref16">16</xref>] , their isolation in this study further confirms this. This further shows their versatility</p><fig id="fig2"  position="float"><label><xref ref-type="fig" rid="fig2">Figure 2</xref></label><caption><title> Titratable acidity of fermented oil palm waste</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/6-2270781x7.png"/></fig><fig id="fig3"  position="float"><label><xref ref-type="fig" rid="fig3">Figure 3</xref></label><caption><title> Temperatures of the fermentation process of oil palm waste</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/6-2270781x8.png"/></fig><p>in nutrient usage, substrate usage and their fermentative involvement [<xref ref-type="bibr" rid="scirp.69433-ref15">15</xref>] [<xref ref-type="bibr" rid="scirp.69433-ref17">17</xref>] [<xref ref-type="bibr" rid="scirp.69433-ref18">18</xref>] .</p><p>The fermentation medium was acidic throughout the period in view which was evident in the values of the pH (<xref ref-type="fig" rid="fig1">Figure 1</xref>), though varied from day to day. This might be due to the microbial activities in the medium [<xref ref-type="bibr" rid="scirp.69433-ref19">19</xref>] . Acidic products or by-products must have been released to the medium to have kept the pH values low. This fermentation probably resulted from acidic pathway(s), further research can confirm this. The 3<sup>rd</sup> day had the highest pH value (4.60) this probably was the highest period of release of acidic products into the medium. At the same time, the titratable acidity followed similar trend as the pH values (<xref ref-type="fig" rid="fig2">Figure 2</xref>), showing close relationship between the two parameters. This agreed with the report of [<xref ref-type="bibr" rid="scirp.69433-ref20">20</xref>] that variation in titratable acidity and pH is a function of the fermentative activities of microorganisms present in a product and the length of fermentation.</p><p>The temperature values (<xref ref-type="fig" rid="fig3">Figure 3</xref>) which ranged from 29.5˚C - 32.5˚C revealed the fermentation process occurred under moderate temperatures. This shows the fermentation of oil palm fruit waste was not a high heat producing process.</p></sec><sec id="s5"><title>5. Conclusion</title><p>In conclusion, several tons of oil palm pericarp waste can be properly or optimally fermented with insight this research has thrown into the fermentation of oil palm waste. Fermentation had been known to improved food qualities therefore fermented oil palm waste may be used to improve farm animals’ feeds when incorporated. This can in a way reduce the cost spent by farmers in producing animal feeds and as well reduce environmental pollution that would have resulted leaving this oil palm fruit waste in the environment.</p></sec><sec id="s6"><title>Acknowledgements</title><p>The research was supported by Costech Canada Inc. and is gratefully acknowledged. The authors would also like to express their gratitude to the Department of Microbiology, Federal University of Technology, Akure, Ondo State, Nigeria for providing a conducive research environment.</p></sec><sec id="s7"><title>Cite this paper</title><p>M. Adedolapo Orimoloye,A. Isaac Sanusi, (2016) Proliferation of Microorganisms in Acidic Fermentation of Elaeis guineensis L. Waste. Advances in Microbiology,06,644-649. doi: 10.4236/aim.2016.69063</p></sec></body><back><ref-list><title>References</title><ref id="scirp.69433-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Block, D. and Glen, J. 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