<?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">OJMS</journal-id><journal-title-group><journal-title>Open Journal of Marine Science</journal-title></journal-title-group><issn pub-type="epub">2161-7384</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/ojms.2021.112007</article-id><article-id pub-id-type="publisher-id">OJMS-108866</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Earth&amp;Environmental Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Seasonal Variation of Heavy Metals in the Intertidal Gastropod Trochus radiatus of Gulf of Mannar
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Theivasigamani</surname><given-names>Mohanraj</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>Maxwalt</surname><given-names>Sheeba</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>Siluvai</surname><given-names>Regi Thomas Sherly Cross</given-names></name><xref ref-type="aff" rid="aff3"><sup>3</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Thangaraj</surname><given-names>Jebarani Rajathy</given-names></name><xref ref-type="aff" rid="aff4"><sup>4</sup></xref></contrib></contrib-group><aff id="aff2"><addr-line>Department of Zoology, PSGR Krishnammal College for Women, Coimbatore, India</addr-line></aff><aff id="aff3"><addr-line>Department of Zoology, St. Mary’s College, Thoothukudi, India</addr-line></aff><aff id="aff1"><addr-line>Department of PG Zoology, Aditanar College of Arts and Science, Tiruchendur, India</addr-line></aff><aff id="aff4"><addr-line>Centre of Advanced Study in Marine Biology, Faculty of Marine Sciences, Parangipettai, India</addr-line></aff><pub-date pub-type="epub"><day>06</day><month>04</month><year>2021</year></pub-date><volume>11</volume><issue>02</issue><fpage>92</fpage><lpage>102</lpage><history><date date-type="received"><day>11,</day>	<month>October</month>	<year>2020</year></date><date date-type="rev-recd"><day>27,</day>	<month>April</month>	<year>2021</year>	</date><date date-type="accepted"><day>30,</day>	<month>April</month>	<year>2021</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>
 
 
  Heavy metals are considered to be the most common environmental pollutants in waters and biota; that indicate presence of effluents associated with industrial and domestic sources. The present study aimed to evaluate the trace metal accumulation (Fe, Mn, Zn, Cu, Cd, Pd and Ni) in the tissue of radiate top shell, the sediment and water samples collected from the Hare Island, Tuticorin, during May 2015 to April 2016. During the study, the metal accumulation in the Water, Sediment and Tissue were in the order of Zn &gt; Pb &gt; Cu &gt; Cd; Fe &gt; Mn &gt; Zn &gt; Cu &gt; Cd; Fe &gt; Zn &gt; Mn &gt; Cu &gt; Cd &gt; Pb &gt; Ni respectively. The concentration of Fe dominated in the sediment and tissue sample throughout the study period. Elevated levels of trace metals especially Fe, Mn, Cu, Pb and Zn was observed during October to December, 
  i.e.
  , during the northeast monsoon in all the samples. One way ANOVA indicated statistically no significant difference (p &gt; 0.01) in the variation of Fe, Mn and Ni within the samples.
 
</p></abstract><kwd-group><kwd>Heavy Metal</kwd><kwd> Trochus radiatus</kwd><kwd> Accumulation</kwd><kwd> Sediment</kwd><kwd> Tissue</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>The Ocean and coastal waters constitute a variety of human activities that primarily includes fisheries, agriculture, navigation, oil and mineral exploration and waste disposal [<xref ref-type="bibr" rid="scirp.108866-ref1">1</xref>]. Due to easy accessibility and subsequently high human intrusion, rivers, estuaries and coastal waters are found to be more susceptible to pollution [<xref ref-type="bibr" rid="scirp.108866-ref2">2</xref>]. Among the pollutants, trace metals are a serious threat as most of them have detrimental effect on living organisms [<xref ref-type="bibr" rid="scirp.108866-ref3">3</xref>] [<xref ref-type="bibr" rid="scirp.108866-ref4">4</xref>]. The heavy metal pollution chiefly results from the effluents that are discharged untreated into the sea and river mainly from the industrial and municipal sources [<xref ref-type="bibr" rid="scirp.108866-ref5">5</xref>] [<xref ref-type="bibr" rid="scirp.108866-ref6">6</xref>] [<xref ref-type="bibr" rid="scirp.108866-ref7">7</xref>]. These heavy metals are easily accumulated by the primary consumers especially the algae, and are further biomagnified through their transmission across the higher levels of the food chain thus resulting in a direct impact on the human health [<xref ref-type="bibr" rid="scirp.108866-ref8">8</xref>]. Hutton [<xref ref-type="bibr" rid="scirp.108866-ref9">9</xref>] reported Lead, copper, cadmium, Chromium and arsenic to be the most toxic heavy metal pollutants.</p><p>Marine pollution especially in India started long back, but has exaggerated during the last few decades and now the situation is turning out to be more dreadful at alarming rate [<xref ref-type="bibr" rid="scirp.108866-ref10">10</xref>]. The distribution of heavy metals in natural waters has widely been recognised as a major aspect in the geochemical behaviour, trans- port and biological effects of these elements [<xref ref-type="bibr" rid="scirp.108866-ref11">11</xref>] [<xref ref-type="bibr" rid="scirp.108866-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.108866-ref13">13</xref>]. The evidence from experimental studies on heavy metal contamination in estuaries and coastal waters on Littorina sp. that feeds on fucoid seaweeds, suggests that the diet is the most important source of these heavy metal intake [<xref ref-type="bibr" rid="scirp.108866-ref14">14</xref>] [<xref ref-type="bibr" rid="scirp.108866-ref15">15</xref>].</p><p>Tuticorin is one of the significant and foremost port hubs that handle several hundreds of ships in a year. It is integrated with several major chemical industries like SPIC, Copper smelting plant, Thermal power station and small scale industrial units of SIPCOT complex. The main source of heavy metal pollution along Tuticorin coastal waters is the effluent discharges especially from the Thermal power station that has a direct effluent (ash) dumping point into the open sea; besides, the fishing operation by mechanized boats also to an extent liberates effluents and petrochemical products into the sea. Earlier investigations by Easterson [<xref ref-type="bibr" rid="scirp.108866-ref16">16</xref>] and Murugan and Edward [<xref ref-type="bibr" rid="scirp.108866-ref17">17</xref>] reveal that in the past few years Tuticorin waters have been adversely affected by industrialization.</p><p>A study by Ganesan and Kannan [<xref ref-type="bibr" rid="scirp.108866-ref18">18</xref>] evidenced a higher concentration of Fe and Mn in the sea water, sediment and algae in the vicinity of Tuticorin Port. Palanichamy and Rajendran [<xref ref-type="bibr" rid="scirp.108866-ref7">7</xref>] noticed elevated levels of Cd and Pb in the bottom waters than the surface waters off Tuticorin. Similar surveillance of heavy metals by Baskaran et al., [<xref ref-type="bibr" rid="scirp.108866-ref19">19</xref>] observed a relatively higher concentration of Fe, Cu, Zn and Al in the fly ash dumping area than in the deeper waters off Tuticorin. The intensity of trace metals and nutrients are relatively higher in low saline inshore waters, but lowers with increased salinity [<xref ref-type="bibr" rid="scirp.108866-ref20">20</xref>].</p><p>Marine fauna and flora including sea grass, fish and bivalves have the capacity to absorb heavy metals and nutrients from both sediments and sea water [<xref ref-type="bibr" rid="scirp.108866-ref21">21</xref>] [<xref ref-type="bibr" rid="scirp.108866-ref22">22</xref>]. Past studies concerning mussels and oysters from the southeast coast of India show that seasonal variation appear to have an increased metal load, especially during monsoon period [<xref ref-type="bibr" rid="scirp.108866-ref23">23</xref>]. Terlizzi et al., [<xref ref-type="bibr" rid="scirp.108866-ref24">24</xref>] assessed the impact of sewage on rocky shore substrate along the south west Apulian coast, Italy and the results indicated that these effluents could modify the assemblage and natural distribution patterns of sessile organisms. Accordingly in the present study an attempt has been made to determine the levels of seven important trace metals such as Zinc, Iron, Manganese, Copper, Cadmium, Nickel and Lead in the water, sediment as well as the tissue of radiate top shell Trochus radiatus, from the Tuticorin waters at different seasons.</p></sec><sec id="s2"><title>2. Materials and Methods</title><sec id="s2_1"><title>2.1. Study Area</title><p>Hare Island (8'47&quot;N and 78'12&quot;E) is located along Tuticorin coast, having sandy substratum, with corals and rocky patches that have luxuriant growth of marine plants, sea grasses and algae (<xref ref-type="fig" rid="fig1">Figure 1</xref>). The total length of this island is 2.59 Kilometers that is predominantly covered by the trochus bed which is fully exposed during the low tide. Out of the various species of sea weeds inhabiting the study area, Ulva lactuca and Gracillaria sp. prefer trochus shells as a substratum for its attachment as well as form the primary food source for Trochus radiatus. During the rainy season forms a small seasonal stream from east side of the Island that is well connected with the Tuticorin Thermal Power Station’s thermal effluent dumping point which leads to mixing of fly ash water with the Island’s terrestrial and marine ecosystem. From this study site Water, sediment and radiate top shells were collected manually once every month for heavy metal analysis. The heavy metals namely Fe, Ni, Zn, Mn, Cu, Pb and Cd in the samples were evaluated and the values of each metal were tabulated to check the analysis of variance (ANOVA).</p></sec><sec id="s2_2"><title>2.2. Tissue Sample</title><p>Trochus which isa genus of small sea snails, known as top snails or top shells, inhabit the upper intertidal zone on rocky shores, where they graze on algal films or macroscopic algae. The accumulation of heavy metals was studied over a period of one year i.e. from May 2015 to April 2016. The shells were collected manually, washed and kept in filtered sea water to empty the gut. Subsequently</p><p>the whole body tissues of animals excluded from the shell were rinsed in distilled water for further drying in the oven at 80˚C &#177; 2˚C. Trace metals were extracted from finely ground tissue by following acid digestion procedure [<xref ref-type="bibr" rid="scirp.108866-ref25">25</xref>] and were identified using Perkin Elmer AAS (Model 2380) in an air acetylene flame.</p></sec><sec id="s2_3"><title>2.3. Water Samples</title><p>Water samples from the surface up to 1 m depth were collected from the study area. The heavy metals in sea water were analysed using Stripping Voltametry in a 757 VA Computrace attached to 765 Dosimat (Metrohm, Switzerland) following the method outlined by Anoop et al., [<xref ref-type="bibr" rid="scirp.108866-ref26">26</xref>].</p></sec><sec id="s2_4"><title>2.4. Sediment Samples</title><p>The sediment samples were collected in polythene bags using Van Veen grab and were brought to the laboratory. The samples were dried and finely ground to extract the metals following acid digestion procedure [<xref ref-type="bibr" rid="scirp.108866-ref25">25</xref>] and were detected on a Perkin Elmer AAS (Model 2380) in an air acetylene flame.</p></sec></sec><sec id="s3"><title>3. Results and Discussion</title><p>Heavy metal pollutants are often lethal to marine biota. They have been considered as an important group of toxic contaminants because of their high toxicity and persistency in all aquatic systems. Cadmium, Copper and Zinc are the metals with most potential impacts that enter the environment in elevated concentrations through waste water discharges as a result of agriculture and industrial activities [<xref ref-type="bibr" rid="scirp.108866-ref27">27</xref>]. In the present study the trace metals such as Fe, Mn, Cu, Pb and Zn were predominantly higher during the northeast monsoon (October to December) in all the samples, mainly due to the high level input of land based discharges and as a result of surface run off [<xref ref-type="bibr" rid="scirp.108866-ref18">18</xref>]. During the study, the metals accumulated in the Water, Sediment and Tissue are as follows: Zn &gt; Pb &gt; Cu &gt; Cd; Fe &gt; Mn &gt; Zn &gt; Cu &gt; Cd; Fe &gt; Zn &gt; Mn &gt; Cu &gt; Cd &gt; Pb &gt; Ni, which corresponds to the observations made by Ganesan et al., [<xref ref-type="bibr" rid="scirp.108866-ref28">28</xref>] in Bay of Bengal, Kaladharan et al., [<xref ref-type="bibr" rid="scirp.108866-ref29">29</xref>] in Kochi waters, Senthilnathan et al., [<xref ref-type="bibr" rid="scirp.108866-ref23">23</xref>] along selected areas of southeast coast of India and Chandrasekar [<xref ref-type="bibr" rid="scirp.108866-ref30">30</xref>] in Tuticorin waters.</p><p>The sediment sample showed the higher trace metal composition for Fe (1928.04 μg·g<sup>−1</sup>) and Mn (108.89 μg·g<sup>−1</sup>) followed by minimal levels of Zn (23.33 μg·g<sup>−1</sup>) and Cu (12.36 μg·g<sup>−1</sup>) (<xref ref-type="fig" rid="fig2">Figure 2</xref>). Meetu et al., [<xref ref-type="bibr" rid="scirp.108866-ref31">31</xref>] observed similar results in the tissue samples of plants growing in the fly ash areas of northern India. Copper is an essential element that serves as a cofactor in a number of enzyme systems, but very high intake of Cu can cause adverse health effect problems for most living organisms. The presence of copper in all the samples may be due to the intrusion of domestic and industrial waste. The mean concentration of Fe and Mn in the sediment samples varied between 1365.04 to 1928.04 μg·g<sup>−1</sup> and 78.19 to 108.89 μg·g<sup>−1</sup> respectively; which are higher than those recorded previously by Ganesan and Kannan [<xref ref-type="bibr" rid="scirp.108866-ref18">18</xref>] and Baskaran et al., [<xref ref-type="bibr" rid="scirp.108866-ref19">19</xref>], off</p><p>Tuticorin, revealing enhanced industrial pollution especially due to fly ash dumping dyke at Tuticorin Thermal Power Plant. A similar higher value of Fe and Mn was observed by Kupekar and Kulkarni [<xref ref-type="bibr" rid="scirp.108866-ref32">32</xref>] in the sediments collected from the intertidal zone of Uran coast.</p><p>The water sample comprised only Cu, Cd, Pb and Zn metals during the study period (<xref ref-type="fig" rid="fig3">Figure 3</xref>), with Cadmium being present in lowest concentration (0.49 to 0.89 μg·g<sup>−1</sup>). Cadmium is highly toxic non-essential heavy metal which does not have any role in biological process of living organisms. Thus even in meagre concentration, cadmium could be harmful to living organisms [<xref ref-type="bibr" rid="scirp.108866-ref33">33</xref>]. During the study period Pb dominated in the water sample that varied between 6.01 to 9.21 μg·g<sup>−1</sup>. Moreover, Lead is one of the toxic metals which can cause musculo-ske- letal, renal, ocular, neurological, immunological, reproductive and developmental effects [<xref ref-type="bibr" rid="scirp.108866-ref34">34</xref>] in all life forms. Introduction of Lead in the marine environment could be mainly attributed to the usage of fuels by way of mechanized boats [<xref ref-type="bibr" rid="scirp.108866-ref35">35</xref>].</p><p>Gastropod shells are used as bioindicators for determining the extent of biotransformation in aquatic food webs and as a vital component of risk assessment of heavy metals. During the study tissue sample of Trochus radiatus accumulated metals such as Cu, Cd, Fe, Zn, Mn, Pb and Ni; of which Fe was recorded to be having the highest concentration (144.54 μg·g<sup>−1</sup>) followed by Zn, Mn, Cu, Cd, Pb and finally Ni with lowest concentration of 0.04 μg·g<sup>−1</sup> (<xref ref-type="fig" rid="fig4">Figure 4</xref>). Heavy metal assessment of gastropods by Kupekar and Kulkarni [<xref ref-type="bibr" rid="scirp.108866-ref32">32</xref>] recorded higher accumulation of Cu in tissue of Hemifusus pugilinus than tissues of Bursa spinosa. Marine gastropods normally accumulate and store Cu and utilize them for synthesizing the blood pigment hemocyanin [<xref ref-type="bibr" rid="scirp.108866-ref36">36</xref>]. According to Pyatt et al., [<xref ref-type="bibr" rid="scirp.108866-ref37">37</xref>], concentration of metals in the soft tissues of molluscs can be attributed to the measure of metal bioavailability originating from both natural and anthropogenic sources.</p><p>The presence of high levels of Fe, Cu, Cd than Ni in the soft tissues of T. radiatus could be due to their roles as components of metabolically important</p><p>biomolecules including enzymes, metalloenzymes and respiratory pigments [<xref ref-type="bibr" rid="scirp.108866-ref32">32</xref>] [<xref ref-type="bibr" rid="scirp.108866-ref38">38</xref>]. It is usually observed that soft tissues of molluscs accumulate higher concentrations of Cu, Zn and Fe than the shells [<xref ref-type="bibr" rid="scirp.108866-ref39">39</xref>] [<xref ref-type="bibr" rid="scirp.108866-ref40">40</xref>] and their surrounding environment. Further seasonal variation in the amount of heavy metals accumulated by T.radiatus could be associated with food supply, changes in runoff particulate material during precipitation and variations related to the reproductive cycle [<xref ref-type="bibr" rid="scirp.108866-ref41">41</xref>]. According to Fang et al., [<xref ref-type="bibr" rid="scirp.108866-ref42">42</xref>] out of the 14 edible molluscs the concentration of Cd, Pb, Ni, Cr, Sb and Sn were observed within the local regulatory limits in only three of the species (Ruditapes philippinarum,Perna viridis andHemifusus tuba). Most of the samples collected from Hong Kong had significantly higher contents of Pb and Sb. Over 60% of bivalves exceeded maximum permitted level of Cd (2 μg·g<sup>−1</sup>) and Cr (1 μg·g<sup>−1</sup>), while over 40% of gastropod species exceeded the maximum level of Sb (1 μg·g<sup>−1</sup>) and Cr (1 μg·g<sup>−1</sup>). In the present study the one way analysis of variance indicated that statistically no significant difference (p &gt; 0.01) was noticed in the seasonal variation of heavy metals between the samples except for the Cu, Cd, Zn and Pb metals (Tables 1-3).</p><p>The determination of heavy metals in seawater and sediment is the area of key interest in the current research scenario, since these trace metals greatly interact with water and sediment and are ultimately ingested by aquatic organisms. Heavy metals such as Cd, Ni, As, Hg, etc. in seawater have been estimated to pose potential threat to the ecosystem [<xref ref-type="bibr" rid="scirp.108866-ref43">43</xref>], which in fact needs continuous effort to assess the impact of these metals on faunal community. In environmental research, owing to their biological non degradability and chronic toxicity of trace metals particularly Cd, Pb, Hg, As, Ni, Cr, etc. are becoming increasingly significant as a result of their accumulation in vital organs of man [<xref ref-type="bibr" rid="scirp.108866-ref44">44</xref>]. Warwick [<xref ref-type="bibr" rid="scirp.108866-ref45">45</xref>] investigated the effects of metal contamination on the intertidal macrobenthic assemblages of the Fal estuary and concluded that of all the environmental factors, heavy metal concentration correlated strongly with composition of biological communities.</p><p>In concordance with the present study concentration of heavy metals in the tissue was generally more than that of water and sediment. Nearly all industrial practices concerning water are potential sources of metallic contamination in coastal waters [<xref ref-type="bibr" rid="scirp.108866-ref46">46</xref>]. Dumping industrial wastes in the sea is very common phenomenon in the study area that is toxic and persistent in the sea for a long time finally accumulating in the marine organism in the form of Persistent Organic Pollutants (POPs) which is one of the most serious concerns worldwide. From the environmental perspective, coastal zones are considered as the geographical space of interaction between terrestrial and marine ecosystem which is of great</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> One way analysis of variance for sediment sample</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Source of variation</th><th align="center" valign="middle" >SS</th><th align="center" valign="middle" >df</th><th align="center" valign="middle" >MS</th><th align="center" valign="middle" >F</th><th align="center" valign="middle" >P-value</th><th align="center" valign="middle" >F crit</th></tr></thead><tr><td align="center" valign="middle" >Between Groups</td><td align="center" valign="middle" >93,017.74</td><td align="center" valign="middle" >11</td><td align="center" valign="middle" >8456.158</td><td align="center" valign="middle"  rowspan="2"  >0.023655</td><td align="center" valign="middle"  rowspan="2"  >1</td><td align="center" valign="middle"  rowspan="2"  >1.924308</td></tr><tr><td align="center" valign="middle" >Within Groups</td><td align="center" valign="middle" >25,738,101</td><td align="center" valign="middle" >72</td><td align="center" valign="middle" >357,473.6</td></tr><tr><td align="center" valign="middle" >Total</td><td align="center" valign="middle" >25,831,118</td><td align="center" valign="middle" >83</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr></tbody></table></table-wrap><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> One way analysis of variance for water sample</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Source of variation</th><th align="center" valign="middle" >SS</th><th align="center" valign="middle" >df</th><th align="center" valign="middle" >MS</th><th align="center" valign="middle" >F</th><th align="center" valign="middle" >P-value</th><th align="center" valign="middle" >F crit</th></tr></thead><tr><td align="center" valign="middle" >Between Groups</td><td align="center" valign="middle" >16.41767</td><td align="center" valign="middle" >11</td><td align="center" valign="middle" >1.492515</td><td align="center" valign="middle"  rowspan="2"  >0.102401</td><td align="center" valign="middle"  rowspan="2"  >0.999881</td><td align="center" valign="middle"  rowspan="2"  >1.924308</td></tr><tr><td align="center" valign="middle" >Within Groups</td><td align="center" valign="middle" >1049.414</td><td align="center" valign="middle" >72</td><td align="center" valign="middle" >14.5752</td></tr><tr><td align="center" valign="middle" >Total</td><td align="center" valign="middle" >1065.832</td><td align="center" valign="middle" >83</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr></tbody></table></table-wrap><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> One way analysis of variance for tissue sample</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Source of variation</th><th align="center" valign="middle" >SS</th><th align="center" valign="middle" >df</th><th align="center" valign="middle" >MS</th><th align="center" valign="middle" >F</th><th align="center" valign="middle" >P-value</th><th align="center" valign="middle" >F crit</th></tr></thead><tr><td align="center" valign="middle" >Between Groups</td><td align="center" valign="middle" >4970.212</td><td align="center" valign="middle" >11</td><td align="center" valign="middle" >451.8375</td><td align="center" valign="middle"  rowspan="2"  >0.305708</td><td align="center" valign="middle"  rowspan="2"  >0.982574</td><td align="center" valign="middle"  rowspan="2"  >1.924308</td></tr><tr><td align="center" valign="middle" >Within Groups</td><td align="center" valign="middle" >106,416.2</td><td align="center" valign="middle" >72</td><td align="center" valign="middle" >1478.003</td></tr><tr><td align="center" valign="middle" >Total</td><td align="center" valign="middle" >111,386.5</td><td align="center" valign="middle" >83</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr></tbody></table></table-wrap><p>importance for survival of large variety of plants, animals and marine species [<xref ref-type="bibr" rid="scirp.108866-ref47">47</xref>]. Any adverse anthropogenic effects on the coastal environment including eutrophication, heavy metal, organic and microbial pollution and Oils spills [<xref ref-type="bibr" rid="scirp.108866-ref48">48</xref>] could threaten these marine lives.</p></sec><sec id="s4"><title>4. Conclusion</title><p>The results of the findings, give valuable information on the heavy metal level in Water, Sediment and the selected gastropod Trochus radiatus. The industrial effluents discharged into the study area are causing an increased level of metal inclusion, which proves that heavy metal concentration will be a bigger problem for this Marine Reserve in the near future. Hence appropriate measures are needed to safeguard our marine system that could possibly be achieved by way of reducing the pollution load into this susceptible environment.</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>Mohanraj, T., Sheeba, M., Cross, S.R.T.S. and Rajathy, T.J. (2021) Seasonal Variation of Heavy Metals in the Intertidal Gastropod Trochus radiatus of Gulf of Mannar. Open Journal of Marine Science, 11, 92-102. https://doi.org/10.4236/ojms.2021.112007</p></sec></body><back><ref-list><title>References</title><ref id="scirp.108866-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Joint Group of Experts on the Scientific Aspects of Marine Pollution (GESAMP) (1982) The Review of the Health of Oceans. 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