<?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">FNS</journal-id><journal-title-group><journal-title>Food and Nutrition Sciences</journal-title></journal-title-group><issn pub-type="epub">2157-944X</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/fns.2019.107062</article-id><article-id pub-id-type="publisher-id">FNS-94049</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>
 
 
  Odor-Active Volatile Compounds from the Gonads of the Sea Urchin &lt;i&gt;Mesocentrotus nudus&lt;/i&gt; in the Wild in Miyagi Prefecture, Tohoku, Japan
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Yoichi</surname><given-names>Sato</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Satomi</surname><given-names>Takagi</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Eri</surname><given-names>Inomata</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Yukio</surname><given-names>Agatsuma</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib></contrib-group><aff id="aff2"><addr-line>Laboratory of Marine Plant Ecology, Graduate School of Agricultural Science, Tohoku University, Aoba, Sendai, Miyagi, Japan</addr-line></aff><aff id="aff1"><addr-line>Bio-Resources Business Development Division, Riken Food Co., Ltd., Miyauchi, Tagajyo, Miyagi, Japan</addr-line></aff><pub-date pub-type="epub"><day>08</day><month>07</month><year>2019</year></pub-date><volume>10</volume><issue>07</issue><fpage>860</fpage><lpage>875</lpage><history><date date-type="received"><day>27,</day>	<month>June</month>	<year>2019</year></date><date date-type="rev-recd"><day>28,</day>	<month>July</month>	<year>2019</year>	</date><date date-type="accepted"><day>31,</day>	<month>July</month>	<year>2019</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>
 
 
  <b>Background and Aims: </b>
  <b>&lt;i&gt;</b>
  Mesocentrotus nudus
  &lt;/i&gt;
   is commercially harvested from shallow rocky bottoms in northern Japan. The gonads are targeted as an edible product. The objective of this study was to identify odor-active volatile organic compounds (VOCs) from the gonads of adult 
  &lt;i&gt;
  M. nudus
  &lt;/i&gt;
   collected at a fishing ground in Miyagi Prefecture, Tohoku, Japan. <b>Methods and Results: </b>Gas chromatography-mass spectrometry analysis and gas chromatography-sniffing techniques identified 42 compounds categorized as alcohols, aldehydes, aromatic hydrocarbons, esters, halomethanes, hydrocarbons, ketones, sulfur-containing compounds, and nitrogen-containing compounds. GC-sniffing analysis characterized four compounds with preferable odors of sea urchin gonads; limonene, propyl acetate, acetone, dibromochloromethane. On the other hand, the analysis characterized three compounds with unpreferable odors; methyl mercaptane, dimethyl sulfide, and s-methyl thioacetate. Several VOCs from the gonads were derived from seaweeds, terrestrial plants, and fish flesh as food because 
  &lt;i&gt;
  M. nudus
  &lt;/i&gt;
   is omnivorous. <b>Conclusion: </b>This is the first study to identify VOCs from edible sea urchin gonads in the wild in Japan. These VOC data comprise a typical standard in order to evaluate a higher quality of sea urchin gonads.
 
</p></abstract><kwd-group><kwd>Sea Urchin</kwd><kwd> &lt;i&gt;Mesocentrotus nudus&lt;/i&gt;</kwd><kwd> Gonad Flavor</kwd><kwd> GC/MS</kwd><kwd> Sniffing Analysis</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Over the past two decades, catches of edible sea urchins have declined from 120, 306 t in 1995 [<xref ref-type="bibr" rid="scirp.94049-ref1">1</xref>] to 69,314 t in 2016 (http://www.fao.org/fishery/en, accessed on 2 November, 2018). In particular, the catch of Chilean sea urchin Loxechinus albus, representing the largest in the world, increased to a peak at 54,740 t in 1995 due to the rapid expansion of fishery, followed by its full exploitation, and then declined to 30,199 t in 2016 (http://www.fao.org/fishery/en, accessed on 2 November, 2018). The catches of Strongylocentrotus droebachiensis in Maine and Mesocentrotus franciscanus along the western seaboard of North America from Baja California to Alaska dramatically declined following a peak in 1993 and 1989, respectively, due to overfishing [<xref ref-type="bibr" rid="scirp.94049-ref1">1</xref>] .</p><p>A recognition that diminished wild stock cannot meet a strong demand has increased the amount of research on sea urchin aquaculture since the mid 1990’s [<xref ref-type="bibr" rid="scirp.94049-ref2">2</xref>] . Among this research, some attention has been focused on the improvement of gonad qualities (texture, taste, and color) of hatchery-raised adults [<xref ref-type="bibr" rid="scirp.94049-ref3">3</xref>] - [<xref ref-type="bibr" rid="scirp.94049-ref10">10</xref>] . In contrast, research on the improvement of gonad quality of adult Mesocentrotus nudus, which densely inhabit crustose coralline “barrens” (reviewed by Agatsuma [<xref ref-type="bibr" rid="scirp.94049-ref11">11</xref>] ), by feeding on fresh Saccharina japonica kelp, has been advancing in northern Japan [<xref ref-type="bibr" rid="scirp.94049-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref13">13</xref>] .</p><p>The free amino acids, glycine, alanine, valine, glutamic acid, and methionine, are closely associated with sea urchin gonad taste [<xref ref-type="bibr" rid="scirp.94049-ref14">14</xref>] . Phillips et al. [<xref ref-type="bibr" rid="scirp.94049-ref15">15</xref>] indicated that the umami and sweet tastes of wild Evechinus chloroticus testes and ovaries are correlated with glutamate (glutamic acid) and glycine concentrations, respectively. Takagi et al. [<xref ref-type="bibr" rid="scirp.94049-ref12">12</xref>] reported a marked increase in sweet tasting alanine contents of the gonads of M. nudus that were collected from barren and fed fresh S. japonica kelp for 42 days from April to June. Thereby, their sensory scores were significantly higher than those from a barren, but not significantly different from those collected from an Eisenia bicyclis kelp bed (fishing ground) in June.</p><p>In addition to taste, the flavor is an important factor of the sensory quality of sea urchin gonads [<xref ref-type="bibr" rid="scirp.94049-ref10">10</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref16">16</xref>] . Phillips et al. [<xref ref-type="bibr" rid="scirp.94049-ref16">16</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref17">17</xref>] assessed the gonad flavor of E. chloroticus and S. droebachiensis according to descriptive analysis [<xref ref-type="bibr" rid="scirp.94049-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref19">19</xref>] . Furthermore, in parallel with the above assessment of gonad flavor, the associated components were identified and quantified using volatile analyses [<xref ref-type="bibr" rid="scirp.94049-ref20">20</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref21">21</xref>] . To date, no odor active volatile compounds have been identified from the gonads of edible sea urchins in Japan. In sea urchin gonads, somatic nutritive phagocytes store extensive nutrient reserves before gametogenesis [<xref ref-type="bibr" rid="scirp.94049-ref22">22</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref23">23</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref24">24</xref>] . Hence, gonad size, color, taste, and flavor would be greatly influenced by food type because nutrient reserves are caused by food consumption.</p><p>Mesocentrotus nudus is commercially harvested in northern Japan. Together with Strongylocentrotus intermedius, it accounts for more than two-thirds of the total sea urchin landing in Japan [<xref ref-type="bibr" rid="scirp.94049-ref25">25</xref>] . The objective of the current study was to identify odor active volatile compounds in the gonads of adult M. nudus collected from a fishing ground in Miyagi Prefecture, Tohoku, Japan.</p></sec><sec id="s2"><title>2. Methods</title><sec id="s2_1"><title>2.1. Sea Urchin Samples</title><p>Mesocentrotus nudus were collected from a subtidal sea floor, where drift Ecklonia bicyclis kelp was concentrated, by scuba diving at the depths of 6 - 7 m off Naburi Bay (38˚53'N, 141˚50'E), Miyagi Prefecture on July 19, 2016. Three adult sea urchins with ca. 55 - 70 mm test diameter [<xref ref-type="bibr" rid="scirp.94049-ref26">26</xref>] , larger than a legal size (50 mm) in Miyagi Prefecture, were randomly selected. The sea urchins were held in a polystyrene box filled with newspapers immersed in sea water and ice packs, and transferred to a laboratory of Riken Food Co., Ltd. in Tagajyo within 2 hours after collection. These sea urchins were dissected, and the gonads were removed and soaked three times in 5˚C sterile seawater. Thereafter, they were drained on bleached cotton at 4˚C for 30 minutes according to a previous study [<xref ref-type="bibr" rid="scirp.94049-ref27">27</xref>] . Gamete release from the gonads was not observed. The gonads were stored in a polystyrene storage container at 4˚C until further analyses.</p></sec><sec id="s2_2"><title>2.2. Large Volume Static Headspace Sampling</title><p>For analysis of the volatile organic compounds (VOCs) of sea urchin gonads, headspace volatile compounds were collected in a large volume static headspace system (Entech 7100A series; Entech Instruments Inc., Simi Valley, CA, USA). Sea urchin gonads were analyzed within 48 hours after collection. Each 5 g sample of the gonads from urchins was sealed in a 375 ml glass jar for measurement of large volume static headspace, which was stored in an incubator (DK400, Yamato Scientific Co., Ltd., Tokyo, Japan) at 30˚C for 10 minutes. Three batches were prepared and used for the following analysis. After incubation, 150 ml of headspace gas was vacuum-extracted from the glass jar. The VOCs were desorbed by thermos desorption using a pre-concentrator (Entech 7100A series; Entech Instruments Inc.) and applied to the gas chromatography-mass spectrometry (GC/MS) system.</p></sec><sec id="s2_3"><title>2.3. GC/MS Analysis</title><p>Quantification of the volatile compounds was performed using an Agilent 6890 series gas chromatograph (Agilent Technologies Inc., Palo Alto, CA, USA) equipped with an Agilent 5975B mass-selective detector and a sniffing port. One half of the column flow was directed to the MS system, while the other half was directed to a heated sniffing port. The GC/MS system was equipped with a DB-WAX column (60 m &#215; 0.25 mm i.d., 0.5 μm film thickness; 122-7063; Agilent Technologies Inc.). The GC operation conditions comprised an injector temperature of 250˚C. Analyses were carried out using helium as the carrier gas at an average flow rate of 27 cm∙sec<sup>−1</sup> with the following temperature program: 40˚C for 5 min, increased at 5˚C∙min<sup>−1</sup> to 240˚C, followed by a final 5 minutes hold at 240˚C.</p><p>Mass spectrometry was carried out in scan mode using an electron ionization voltage of 70 eV and a scan range from m/z 10 to 300 every 1.58 every sec. Analysis of VOCs was performed using Powered Pro software (Willey 11N17main, Agilent Technologies Inc.). The relative amounts of VOCs were calculated based on the peak areas in the chromatograms.</p></sec><sec id="s2_4"><title>2.4. Gas Chromatography-Olfactometry Analysis</title><p>The type and composition ratio of VOCs can be revealed by GC/MS analysis; however, since its peak is large, it does not necessarily have a large contribution to sample scent. Thereby, gas chromatography-olfactometry techniques were conducted in the present study; these can obtain information on the quality and strength of odors by human sniffing the smell of ingredients introduced from GC [<xref ref-type="bibr" rid="scirp.94049-ref28">28</xref>] . One half of the column flow was directed to a heated sniffing port (ODP2 Oflactory Detection Port, Gerstel GmbH &amp; Co.KG, M&#252;lheim an der Ruhr, Germany). To the sniffing port, humidified air (50% - 75% relative humidity) was carried at 1.02 ml∙min<sup>−1</sup> in order to prevent the drying out of the nose, causing considerable discomfort for assessors and degradation of sensitivity [<xref ref-type="bibr" rid="scirp.94049-ref29">29</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref30">30</xref>] . The panelist recorded the retention time and the description of the aroma compounds [<xref ref-type="bibr" rid="scirp.94049-ref16">16</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref31">31</xref>] . Each gonad from three sea urchins was used for the sniffing analysis. When a volatile compound was detected in all gonads, this analysis was determined to be a declared aroma compound related to sea urchin gonads.</p></sec></sec><sec id="s3"><title>3. Results and Discussion</title><p>The VOCs of the gonads from three sea urchins collected in Naburi Bay, Miyagi Prefecture were analyzed by GC/MS. Typical total ion chromatograms of VOCs from sea urchin gonads are shown in <xref ref-type="fig" rid="fig1">Figure 1</xref>. A total of 42 compounds were identified from all gonads. These compounds can be categorized into the following chemical families; alcohols (5), aldehydes (8), aromatic ring-structured compounds (7), esters (5), halomethanes (3), hydrocarbons (5), ketones (5), and others (4; methyl mercaptan [MM], dimethyl sulfide [DMS], acetonitrile, and Bis-(methylthio)-methane) (<xref ref-type="table" rid="table1">Table 1</xref>). Among them, 22 compounds were identified by GC-sniffing analyses (<xref ref-type="table" rid="table2">Table 2</xref>). VOCs were detected from fresh and canned gonads of Paracentrotus lividus collected from Galicia in Spain [<xref ref-type="bibr" rid="scirp.94049-ref32">32</xref>] , and from testes and ovaries of Evechinus chloroticus collected from the North and South Islands of New Zealand [<xref ref-type="bibr" rid="scirp.94049-ref21">21</xref>] . The 13 compounds of these two previous studies were also detected in the present study (<xref ref-type="table" rid="table1">Table 1</xref>).</p><sec id="s3_1"><title>3.1. Alcohols</title><p>The five compounds of saturated alcohols: methanol, 2-propanol, ethanol, 2-butanol, and 2-ethyl hexanol were detected in the present study. Methanol and 2-ethyl hexanol were also found in the gonads of E. chloroticus as possible compounds [<xref ref-type="bibr" rid="scirp.94049-ref20">20</xref>] . Unsaturated alcohols could significantly contribute to odor due to their relatively low odor threshold value [<xref ref-type="bibr" rid="scirp.94049-ref33">33</xref>] . On the other hand, saturated alcohols could have insignificant contributions to odor due to their rela</p><table-wrap-group id="1"><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Volatile composition of volatile organic compounds (VOCs) in gonads of Mesocentrotus nudus</title></caption><table-wrap id="1_1"><table><tbody><thead><tr><th align="center" valign="middle" >No.</th><th align="center" valign="middle"  colspan="2"  >Volatile compounds</th><th align="center" valign="middle" >Retention time (min)</th><th align="center" valign="middle" >Relative content (%)</th></tr></thead><tr><td align="center" valign="middle" ></td><td align="center" valign="middle"  colspan="2"  >Alcohols (5)</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >10</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Methanol<sup>a</sup></td><td align="center" valign="middle" >12.05</td><td align="center" valign="middle" >0.42</td></tr><tr><td align="center" valign="middle" >13</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >2-Propanol</td><td align="center" valign="middle" >13.21</td><td align="center" valign="middle" >0.41</td></tr><tr><td align="center" valign="middle" >14</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Ethanol</td><td align="center" valign="middle" >13.46</td><td align="center" valign="middle" >47.06</td></tr><tr><td align="center" valign="middle" >21</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >2-Butanol</td><td align="center" valign="middle" >16.57</td><td align="center" valign="middle" >0.05</td></tr><tr><td align="center" valign="middle" >39</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >2-Ethyl haxanol</td><td align="center" valign="middle" >30.41</td><td align="center" valign="middle" >2.45</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle"  colspan="2"  >Aldehydes (8)</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Acetaldehyde<sup>a</sup></td><td align="center" valign="middle" >5.87</td><td align="center" valign="middle" >7.13</td></tr><tr><td align="center" valign="middle" >3</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Dimethoxy methane</td><td align="center" valign="middle" >6.74</td><td align="center" valign="middle" >0.11</td></tr><tr><td align="center" valign="middle" >6</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Propanal<sup>a</sup></td><td align="center" valign="middle" >8.24</td><td align="center" valign="middle" >0.48</td></tr><tr><td align="center" valign="middle" >9</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Acetal</td><td align="center" valign="middle" >11.78</td><td align="center" valign="middle" >0.01</td></tr><tr><td align="center" valign="middle" >12</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >3-Methyl butanal<sup>a</sup></td><td align="center" valign="middle" >12.75</td><td align="center" valign="middle" >0.06</td></tr><tr><td align="center" valign="middle" >37</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Nonanal<sup>b</sup></td><td align="center" valign="middle" >28.12</td><td align="center" valign="middle" >0.07</td></tr><tr><td align="center" valign="middle" >40</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Decanal<sup>b</sup></td><td align="center" valign="middle" >30.92</td><td align="center" valign="middle" >0.11</td></tr><tr><td align="center" valign="middle" >41</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Benzaldehyde<sup>a,b</sup></td><td align="center" valign="middle" >32.01</td><td align="center" valign="middle" >0.01</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle"  colspan="2"  >Aromatic ring-structured compounds (7)</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >5</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Methyl cyclohexane</td><td align="center" valign="middle" >7.79</td><td align="center" valign="middle" >0.20</td></tr></tbody></table></table-wrap><table-wrap id="1_2"><table><tbody><thead><tr><th align="center" valign="middle" >23</th><th align="center" valign="middle" ></th><th align="center" valign="middle" >Toluene<sup>a</sup></th><th align="center" valign="middle" >17.26</th><th align="center" valign="middle" >3.15</th></tr></thead><tr><td align="center" valign="middle" >27</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Ethyl benzene<sup>b</sup></td><td align="center" valign="middle" >19.87</td><td align="center" valign="middle" >0.19</td></tr><tr><td align="center" valign="middle" >29</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Xylene<sup>a</sup></td><td align="center" valign="middle" >20.34</td><td align="center" valign="middle" >0.17</td></tr><tr><td align="center" valign="middle" >32</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Styrene</td><td align="center" valign="middle" >24.23</td><td align="center" valign="middle" >0.28</td></tr><tr><td align="center" valign="middle" >36</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Trimethyl benzene</td><td align="center" valign="middle" >26.77</td><td align="center" valign="middle" >0.04</td></tr><tr><td align="center" valign="middle" >38</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Dichlorobenzene<sup>b</sup></td><td align="center" valign="middle" >29.74</td><td align="center" valign="middle" >0.17</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle"  colspan="2"  >Esters (5)</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >8</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Ethyl acetate</td><td align="center" valign="middle" >11.56</td><td align="center" valign="middle" >0.81</td></tr><tr><td align="center" valign="middle" >15</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Propyl acetate</td><td align="center" valign="middle" >14.80</td><td align="center" valign="middle" >0.19</td></tr><tr><td align="center" valign="middle" >24</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >S-Methyl thioacetate</td><td align="center" valign="middle" >17.48</td><td align="center" valign="middle" >2.95</td></tr><tr><td align="center" valign="middle" >26</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >S-Methyl propanethioate</td><td align="center" valign="middle" >19.75</td><td align="center" valign="middle" >0.22</td></tr><tr><td align="center" valign="middle" >28</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >S-Methyl thiobutyrate</td><td align="center" valign="middle" >20.18</td><td align="center" valign="middle" >0.07</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle"  colspan="2"  >Halomethanes (3)</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >20</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Chloroform</td><td align="center" valign="middle" >16.26</td><td align="center" valign="middle" >0.23</td></tr><tr><td align="center" valign="middle" >30</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Dibromomethane</td><td align="center" valign="middle" >21.02</td><td align="center" valign="middle" >0.10</td></tr><tr><td align="center" valign="middle" >34</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Dibromochloromethane</td><td align="center" valign="middle" >25.29</td><td align="center" valign="middle" >0.12</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle"  colspan="2"  >Hydrocarbons (5)</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >17</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Decane</td><td align="center" valign="middle" >15.53</td><td align="center" valign="middle" >0.08</td></tr><tr><td align="center" valign="middle" >22</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >α-Pinene</td><td align="center" valign="middle" >16.68</td><td align="center" valign="middle" >0.02</td></tr><tr><td align="center" valign="middle" >25</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Undecane</td><td align="center" valign="middle" >18.56</td><td align="center" valign="middle" >0.08</td></tr><tr><td align="center" valign="middle" >31</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Limonene<sup>a,b</sup></td><td align="center" valign="middle" >22.15</td><td align="center" valign="middle" >0.13</td></tr><tr><td align="center" valign="middle" >33</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Tridecane</td><td align="center" valign="middle" >24.61</td><td align="center" valign="middle" >0.02</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle"  colspan="2"  >Ketones (5)</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >7</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Acetone</td><td align="center" valign="middle" >9.12</td><td align="center" valign="middle" >6.15</td></tr><tr><td align="center" valign="middle" >11</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >2-Butanone</td><td align="center" valign="middle" >12.13</td><td align="center" valign="middle" >0.80</td></tr><tr><td align="center" valign="middle" >16</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >2-Pentanone</td><td align="center" valign="middle" >15.00</td><td align="center" valign="middle" >0.09</td></tr><tr><td align="center" valign="middle" >19</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >4-Methyl-2-pentanone</td><td align="center" valign="middle" >16.06</td><td align="center" valign="middle" >0.10</td></tr><tr><td align="center" valign="middle" >42</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Acetophenone</td><td align="center" valign="middle" >35.20</td><td align="center" valign="middle" >0.08</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle"  colspan="2"  >Other compounds (4)</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Methyl mercaptane</td><td align="center" valign="middle" >5.42</td><td align="center" valign="middle" >0.21</td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Dimethyl sulfide<sup>a</sup></td><td align="center" valign="middle" >7.09</td><td align="center" valign="middle" >23.19</td></tr><tr><td align="center" valign="middle" >18</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Acetonitrile</td><td align="center" valign="middle" >15.72</td><td align="center" valign="middle" >1.70</td></tr><tr><td align="center" valign="middle" >35</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Bis-(methylthio)-methane</td><td align="center" valign="middle" >25.42</td><td align="center" valign="middle" >0.12</td></tr></tbody></table></table-wrap></table-wrap-group><p>a) Niimi et al. (2010), b) De Quiros et al. (2001).</p><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Volatile compounds of Mesocentrotus nudus with their odour descriptions</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >No.</th><th align="center" valign="middle" >Compounds</th><th align="center" valign="middle" >Retention time (min)</th><th align="center" valign="middle" >Odour description</th></tr></thead><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" >Methyl mercaptane</td><td align="center" valign="middle" >5.42</td><td align="center" valign="middle" >Eggs, Fish</td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" >Acetaldehyde</td><td align="center" valign="middle" >5.87</td><td align="center" valign="middle" >Metalic</td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" >Dimethyl sulfide</td><td align="center" valign="middle" >7.09</td><td align="center" valign="middle" >Marine, Fish</td></tr><tr><td align="center" valign="middle" >6</td><td align="center" valign="middle" >Propanal</td><td align="center" valign="middle" >8.24</td><td align="center" valign="middle" >Heavy, Metaric</td></tr><tr><td align="center" valign="middle" >7</td><td align="center" valign="middle" >Acetone</td><td align="center" valign="middle" >9.12</td><td align="center" valign="middle" >Sweet</td></tr><tr><td align="center" valign="middle" >14</td><td align="center" valign="middle" >2-Propanol</td><td align="center" valign="middle" >13.21</td><td align="center" valign="middle" >Kelp, Dry</td></tr><tr><td align="center" valign="middle" >16</td><td align="center" valign="middle" >Propyl actate</td><td align="center" valign="middle" >14.80</td><td align="center" valign="middle" >Sweet, Sugar</td></tr><tr><td align="center" valign="middle" >18</td><td align="center" valign="middle" >Trichloroethene</td><td align="center" valign="middle" >15.39</td><td align="center" valign="middle" >Dusty</td></tr><tr><td align="center" valign="middle" >23</td><td align="center" valign="middle" >2-Butanol</td><td align="center" valign="middle" >16.57</td><td align="center" valign="middle" >Fish, Marine</td></tr><tr><td align="center" valign="middle" >24</td><td align="center" valign="middle" >α-Pinene</td><td align="center" valign="middle" >16.68</td><td align="center" valign="middle" >Burning</td></tr><tr><td align="center" valign="middle" >26</td><td align="center" valign="middle" >S-Methyl thioacetate</td><td align="center" valign="middle" >17.48</td><td align="center" valign="middle" >Sulfer, Fishly, Fish oil, Ammonia</td></tr><tr><td align="center" valign="middle" >28</td><td align="center" valign="middle" >S-Methyl propanethioate</td><td align="center" valign="middle" >19.75</td><td align="center" valign="middle" >Ozone</td></tr><tr><td align="center" valign="middle" >29</td><td align="center" valign="middle" >Ethyl benzene</td><td align="center" valign="middle" >19.87</td><td align="center" valign="middle" >Fish oil</td></tr><tr><td align="center" valign="middle" >30</td><td align="center" valign="middle" >S-Methyl thiobutyrate</td><td align="center" valign="middle" >20.18</td><td align="center" valign="middle" >Metalic</td></tr><tr><td align="center" valign="middle" >33</td><td align="center" valign="middle" >Limonene</td><td align="center" valign="middle" >22.15</td><td align="center" valign="middle" >Floral, Binegar</td></tr><tr><td align="center" valign="middle" >34</td><td align="center" valign="middle" >Styrene</td><td align="center" valign="middle" >24.23</td><td align="center" valign="middle" >Heavy, Metalic</td></tr><tr><td align="center" valign="middle" >35</td><td align="center" valign="middle" >Tridecane</td><td align="center" valign="middle" >24.61</td><td align="center" valign="middle" >Ozone</td></tr><tr><td align="center" valign="middle" >36</td><td align="center" valign="middle" >Dibromochloromethane</td><td align="center" valign="middle" >25.29</td><td align="center" valign="middle" >Bitter, Sweet</td></tr><tr><td align="center" valign="middle" >37</td><td align="center" valign="middle" >Bis(methyl thio)methane</td><td align="center" valign="middle" >25.42</td><td align="center" valign="middle" >Ozone, Sulfer</td></tr><tr><td align="center" valign="middle" >38</td><td align="center" valign="middle" >Trimethyl benzene</td><td align="center" valign="middle" >26.77</td><td align="center" valign="middle" >Bitter, Sweet</td></tr><tr><td align="center" valign="middle" >39</td><td align="center" valign="middle" >Nonanal</td><td align="center" valign="middle" >28.12</td><td align="center" valign="middle" >Dusty, Ozone</td></tr><tr><td align="center" valign="middle" >42</td><td align="center" valign="middle" >Decanal</td><td align="center" valign="middle" >30.92</td><td align="center" valign="middle" >Vinegar, Sweet, Armond</td></tr></tbody></table></table-wrap><p>tively high odor threshold value [<xref ref-type="bibr" rid="scirp.94049-ref34">34</xref>] . Therefore, the contributions of the five compounds of sa-turated alcohols to the aroma of sea urchin gonads might be inconsiderable. Ethanol was the highest value of relative content.</p></sec><sec id="s3_2"><title>3.2. Aldehydes</title><p>The eight compounds of aldehydes: acetaldehyde, dimethoxy methane, propanal, acetal, 3-methyl butanal, nonanal, decanal, and benzaldehyde were identified from the gonads of M. nudus in the present study. Of them, six aldehydes: acetaldehyde, propanal, 3-methyl butanal, nonanal, decanal, and benzaldehyde were common in the gonads of P. lividus [<xref ref-type="bibr" rid="scirp.94049-ref32">32</xref>] and E. chloroticus [<xref ref-type="bibr" rid="scirp.94049-ref21">21</xref>] . Aldehydes are produced by oxidative degradation of fatty acids, and they have been detected in many fish and shellfish including crabs (Chionoecetes japonicus) [<xref ref-type="bibr" rid="scirp.94049-ref35">35</xref>] , scallops (Mizuhopecten yessoensis) [<xref ref-type="bibr" rid="scirp.94049-ref36">36</xref>] , sea bream (Sparus aurata) [<xref ref-type="bibr" rid="scirp.94049-ref37">37</xref>] , and Ayu fish (Plecoglossus altivelis) [<xref ref-type="bibr" rid="scirp.94049-ref38">38</xref>] . Aldehydes could have significant contributions to odor in various species due to their relatively low odor threshold values [<xref ref-type="bibr" rid="scirp.94049-ref39">39</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref40">40</xref>] . Furthermore, nonanal and benzaldehyde were detected in three kombu kelps (Saccharina japonica, S. japonica var. ochotensis, and S. angustata) [<xref ref-type="bibr" rid="scirp.94049-ref41">41</xref>] and two Rhodophytes (Pterocladiella capillacea and Osmundaria obtusiloba) [<xref ref-type="bibr" rid="scirp.94049-ref42">42</xref>] . Nonanal, benzaldehyde, and decanal have been detected in Ulva pertusa [<xref ref-type="bibr" rid="scirp.94049-ref43">43</xref>] , suggesting these compounds originated from seaweeds, which are principal foods for M. nudus. Among these compounds, benzaldehyde has a pleasant almond nutty and stone fruit aroma [<xref ref-type="bibr" rid="scirp.94049-ref44">44</xref>] , suggesting that this compound may have a desirable effect on the aroma of sea urchin gonads [<xref ref-type="bibr" rid="scirp.94049-ref32">32</xref>]</p></sec><sec id="s3_3"><title>3.3. Aromatic Hydrocarbons</title><p>The seven compounds of aromatic hydrocarbons: methyl cyclohexane, toluene, ethyl benzene, xylene, styrene, trimethyl benzene, and dichlorobenzene were identified. These compounds are known as the derivatives from thermal decomposition of sugars and amino acids [<xref ref-type="bibr" rid="scirp.94049-ref45">45</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref46">46</xref>] , and oxidation degradation of carotenoids [<xref ref-type="bibr" rid="scirp.94049-ref32">32</xref>] .</p><p>Styrene and ethyl benzene are related to the xenobiotic-metabolizing enzymes of Strongylocentrotus purpuratus [<xref ref-type="bibr" rid="scirp.94049-ref47">47</xref>] , and ethyl benzene has been tentatively identified from P. lividus [<xref ref-type="bibr" rid="scirp.94049-ref32">32</xref>] and E. chloroticus [<xref ref-type="bibr" rid="scirp.94049-ref20">20</xref>] . The present study findings suggest the existence of the same enzyme from the gonads of M. nudus. Additionally, GC sniffing-analysis indicated that ethylbenzene had a scent comparable to “fish oil”, which is reminiscent of the pleasant aroma of fresh sea urchin gonads (<xref ref-type="table" rid="table2">Table 2</xref>).</p></sec><sec id="s3_4"><title>3.4. Esters</title><p>The five compounds of esters: ethyl acetate, propyl acetate, S-methyl thioacetate, S-methyl propanethioate, and S-methyl thiobutyrate were identified. Although esters have rarely been detected in edible fishes and shellfishes, these compounds are important contributors to the sweet aroma of various fruits [<xref ref-type="bibr" rid="scirp.94049-ref48">48</xref>] . Therefore, these ester compounds possibly affect the sweet aroma of M. nudus gonads [<xref ref-type="bibr" rid="scirp.94049-ref12">12</xref>] .</p></sec><sec id="s3_5"><title>3.5. Halomethanes</title><p>Of the VOCs, two halomethane compounds: Dibromomethane and dibromo-chloromethane were first detected in the present study. In the past, these compounds were not found in sea urchin gonads and other edible shellfish. Crustose and articulated coralline algae (Rhodophyta) produce halomethane compounds [<xref ref-type="bibr" rid="scirp.94049-ref49">49</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref50">50</xref>] , among which dibromomethane is known as an inducer of settlement and metamorphosis of M. nudus larvae [<xref ref-type="bibr" rid="scirp.94049-ref51">51</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref52">52</xref>] . Halomethane compounds detected in the present study are derived from crustose and/or articulated coralline algae ingested as food sources [<xref ref-type="bibr" rid="scirp.94049-ref53">53</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref54">54</xref>] .</p></sec><sec id="s3_6"><title>3.6. Hydrocarbons</title><p>The five compounds of hydrocarbons: decane, α-pinene, undecane, limonene, and tridecane were identified in the gonads. Hydrocarbons constitute the most important family of VOCs in the gonads of P. lividus [<xref ref-type="bibr" rid="scirp.94049-ref32">32</xref>] , although the large amounts of these VOCs did not appear to contribute significantly to flavor due to their high flavor thresholds [<xref ref-type="bibr" rid="scirp.94049-ref55">55</xref>] . These compounds are derived from the decarboxylation reaction of fatty acid and thermal decomposition of carotenoids [<xref ref-type="bibr" rid="scirp.94049-ref56">56</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref57">57</xref>] . Of them, limonene has a flavor comparable to sweet citrus with a freshness. This hydrocarbon has been detected in other sea urchin species [<xref ref-type="bibr" rid="scirp.94049-ref21">21</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref32">32</xref>] , fish (Notropsis atherinoides) [<xref ref-type="bibr" rid="scirp.94049-ref39">39</xref>] , prawn (Pleoticus muelleri) [<xref ref-type="bibr" rid="scirp.94049-ref58">58</xref>] , scallop (Placopecten magellanicus) [<xref ref-type="bibr" rid="scirp.94049-ref57">57</xref>] , and the seaweeds U. pertusa [<xref ref-type="bibr" rid="scirp.94049-ref43">43</xref>] and S. japonica, S. japonica var. ochotensis, and S. angustata [<xref ref-type="bibr" rid="scirp.94049-ref41">41</xref>] . This compound can accumulate in the gonads of M. nudus through consumption of seaweeds. Alpha-pinene is a principle VOC derived from coniferous trees such as pine [<xref ref-type="bibr" rid="scirp.94049-ref59">59</xref>] ; it is rarely detected in sea urchins, fishes, and other shellfish. Mesocentrotus nudus consume seaweeds and also other organisms [<xref ref-type="bibr" rid="scirp.94049-ref11">11</xref>] . Coniferous leaves and branches that have been transferred from land to the seabed would be consumed and accumulated in the gonads.</p></sec><sec id="s3_7"><title>3.7. Ketones</title><p>The five compounds of ketones, acetone, 2-butanone, 2-pentanone, 4-methyl2-pentaone, and acetophenone, were detected in the gonads. Ketones are produced by oxidative degradation of fatty acid. They have been detected from various edible fishes and shellfish species, comparable to aldehydes [<xref ref-type="bibr" rid="scirp.94049-ref36">36</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref55">55</xref>] . The compound 4-methyl-2-pentanone was found in canned products of sea urchin gonads of P. lividus [<xref ref-type="bibr" rid="scirp.94049-ref32">32</xref>] . Detection of this compound in the raw urchin gonads inferred that the unsaturated fatty acid was quickly oxidized and decomposed even during cold storage.</p></sec><sec id="s3_8"><title>3.8. Other Compounds</title><p>Four other compounds, DMS, MM, Bis-(methylthio)-methane, and acetonitrile were detected. DMS, MM, and Bis-(methylthio)-methane were sulfur-containing. These were derived from the decomposition of sulfur-containing proteins in vivo and might have a strong effect on the overall flavor due to their low threshold [<xref ref-type="bibr" rid="scirp.94049-ref60">60</xref>] . Sulfur and fish smells were noted at the peak of MM according to gas chromatography-olfactometry analyses in the present study. The relative content of DMS showed the second highest value among all the compounds. DMS has been detected from several edible fishes and shellfish including the gonads of E. chloroticus [<xref ref-type="bibr" rid="scirp.94049-ref21">21</xref>] , red queen crab (Chionoecetes japonicus) [<xref ref-type="bibr" rid="scirp.94049-ref35">35</xref>] , scallops (Mizuhopecten yessoensis) [<xref ref-type="bibr" rid="scirp.94049-ref36">36</xref>] , and Nile tilapia (Oreochromis niloticus) [<xref ref-type="bibr" rid="scirp.94049-ref61">61</xref>] . These sulfur-containing compounds contributed to odors of “sulfur and rubber” in the sea fig (Microcosmus vulgaris) [<xref ref-type="bibr" rid="scirp.94049-ref62">62</xref>] and an odor of “sulfur” in the oyster (Crassostrea gigas) [<xref ref-type="bibr" rid="scirp.94049-ref63">63</xref>] . These compounds detected in the present study appeared to be affected not only by in vivo metabolism, but also by direct ingestion of dead fish flesh [<xref ref-type="bibr" rid="scirp.94049-ref64">64</xref>] , followed by digestion and absorption as sulfur-containing proteins. Additionally, DMS is regarded as a typical compound produced by cutting U. pertusa [<xref ref-type="bibr" rid="scirp.94049-ref43">43</xref>] and has been identified as a typical VOC of Ulva species [<xref ref-type="bibr" rid="scirp.94049-ref65">65</xref>] . Therefore, these sulfur-containing compounds from the sea urchin gonads might have been also derived from Ulva species.</p></sec><sec id="s3_9"><title>3.9. Gonad VOCs</title><p>The number of VOCs detected from M. nudus gonads in the present study was larger than that from the gonads of other sea urchin species observed in previous studies [<xref ref-type="bibr" rid="scirp.94049-ref21">21</xref>] [<xref ref-type="bibr" rid="scirp.94049-ref32">32</xref>] . The compounds detected in the GC-sniffing analyses included some that had odors comparable to those of the sea urchin gonads such as limonene (floral, vinegar), propyl acetate (sweet, sugar), acetone (sweet), and dibromochloromethane (bitter, sweet). These compounds constitute mainly preferable flavor of sea urchin gonads. On the other hand, MM (egg, fish), DMS (marine, fish), and s-methyl thioacetate (sulfur) were noted as unpreferable odors (<xref ref-type="table" rid="table2">Table 2</xref>). The relative content of these compounds was not necessarily large (<xref ref-type="table" rid="table1">Table 1</xref>), thereby the sniffing analysis is an important method for evaluating the contribution to the flavor of sea urchin gonads. Since odor is an important factor in determining the quality of sea urchin gonads at the market, the balance of these VOCs would influence their evaluation. VOCs from gonads before gametogenesis are derived from various foods such as seaweeds, terrestrial plants, and fish flesh because M. nudus is an omnivore [<xref ref-type="bibr" rid="scirp.94049-ref11">11</xref>] . In fish aquaculture, feed odors reflect their meat [<xref ref-type="bibr" rid="scirp.94049-ref66">66</xref>] . Miyasaki and Kitamura [<xref ref-type="bibr" rid="scirp.94049-ref61">61</xref>] used feeds prepared with feed oil, with many aldehydes and DMS (experimental), and soybean oil with low compounds (control) fed to Nile tilapia (Oreochromis niloticus). As a result, the flesh and inward organs of individuals fed the experimental feed had a larger number of VOCs and area of GC/MS analysis than the control group. The sensory evaluation confirmed an unpleasant odor. Phillips et al. [<xref ref-type="bibr" rid="scirp.94049-ref16">16</xref>] reported that the gonads of E. chloroticus fed a diet with high glutamate and glycine contents had a sweeter taste than those fed a diet with high valine and methionine contents, which had marine and sulfur odors. These studies indicated a possibility that preparing feed, of which unpleasant odor compounds were suppressed, improved sea urchin gonad flavor. In focusing on the VOCs of sea urchin gonads, improvement of gonad flavor, in addition to gonad size, texture, color, and taste, would require high-level techniques of sea urchin aquaculture. To the best of the authors’ knowledge, this study was the first to identify VOCs from edible sea urchin gonads in a kelp bed (fishing ground) in Japan. The VOC data obtained comprise a typical standard that can contribute to the evaluation of higher quality sea urchin gonads.</p></sec></sec><sec id="s4"><title>Acknowledgements</title><p>We sincerely thank Tokumi Goshima of the Ogatsu Branch of the Miyagi Fisheries Cooperative Association for sea urchin collection. We are also very grateful to Atsuko Kokubun of Riken Vitamin Co., Ltd. for GC/MS analyses.</p></sec><sec id="s5"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s6"><title>Cite this paper</title><p>Sato, Y., Takagi, S., Inomata, E. and Agatsuma, Y. (2019) Odor-Active Volatile Compounds from the Gonads of the Sea Urchin Mesocentrotus nudus in the Wild in Miyagi Prefecture, Tohoku, Japan. 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