<?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">AMPC</journal-id><journal-title-group><journal-title>Advances in Materials Physics and Chemistry</journal-title></journal-title-group><issn pub-type="epub">2162-531X</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/ampc.2021.113006</article-id><article-id pub-id-type="publisher-id">AMPC-107986</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Chemistry&amp;Materials Science</subject><subject> Physics&amp;Mathematics</subject></subj-group></article-categories><title-group><article-title>
 
 
  Determination of Natural Radioactivity of the &lt;i&gt;Hibiscus sabdariffa&lt;/i&gt; Linn (Roselle) Used in C&amp;#244;te d’Ivoire (Ivory Coast)
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Agbo</surname><given-names>Djoman Djama Alfred</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>Djagouri</surname><given-names>Koudou</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>Brigui</surname><given-names>Olkalé Jean-Claude</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff2"><addr-line>Ecole Normale Supérieure of Abidjan, C&amp;amp;#244;te d’Ivoire, Laboratoire des Sciences de la Matière, de l’Environnement et de l’Energie solaire (LASMES) of Felix Houphouet Boigny University, Abidjan, C&amp;amp;#244;te d’Ivoire</addr-line></aff><aff id="aff1"><addr-line>Laboratoire des Sciences de la Matière, de l’Environnement et de l’Energie Solaire (LASMES) of Felix Houphouet Boigny University, Abidjan C&amp;amp;#244;te, Felix Houphouet Boigny University, Abidjan, C&amp;amp;#244;te d’Ivoire</addr-line></aff><pub-date pub-type="epub"><day>25</day><month>03</month><year>2021</year></pub-date><volume>11</volume><issue>03</issue><fpage>59</fpage><lpage>66</lpage><history><date date-type="received"><day>13,</day>	<month>February</month>	<year>2021</year></date><date date-type="rev-recd"><day>22,</day>	<month>March</month>	<year>2021</year>	</date><date date-type="accepted"><day>25,</day>	<month>March</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>
 
 
  In this work, ten medicinal and nutritional leaves samples of 
  <em>Hibiscus sabdariffa</em> Linn imported from Mali and Burkina Faso in C
  &amp;#244;te d’Ivoire and sold on the market were collected. The analysis of these plants using High Purity Germanium detector (HPGE) gamma spectrometry showed the activity concentrations of 
  <sup>226</sup>Ra, 
  <sup>232</sup>Th, and 
  <sup>40</sup>K varied respectively in the range of (1.74 - 0.11) &#215; 10
  <sup>&amp;#8722;3</sup> Bq/kg, (6.72 - 0.61) &#215; 10
  <sup>&amp;#8722;4</sup> Bq/kg and (4.65 - 0.54) &#215; 10
  <sup>&amp;#8722;3</sup> Bq/kg1 in the leaves of 
  <em>H. sabdariffa</em>. The Average Annual Committed Effective Dose (AACED) values from leaves this plant varied from 251.492 &#215; 10
  <sup>&amp;#8722;6</sup> to 68.133 &#215; 10
  <sup>&amp;#8722;6</sup> mSv/y. These values found are below 0.30 mSv/y, the world average value for an individual. These results show that there is no radiological risk in consuming “bissap” leaves.
 
</p></abstract><kwd-group><kwd>Natural Radioactivity</kwd><kwd> HPGe Gamma Spectrometry</kwd><kwd> Activity Concentration</kwd><kwd> Medicinal and Nutritional Plant</kwd><kwd> C&amp;#244;te d’Ivoire</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Hibiscus sabdariffa Linn is to the family of the plant called malvaceae and it is usually called “bissap” in Burkina Faso, Senegal, Togo, Mali and C&#244;te d’Ivoire [<xref ref-type="bibr" rid="scirp.107986-ref1">1</xref>]. The fruit of the plant is used in nutrition for making juice extract [<xref ref-type="bibr" rid="scirp.107986-ref2">2</xref>] in Africa. It is also well known traditionally that fruits including juice from H. sabdariffa are rich in vitamin C. These leaves are also used to treat diseases like kidneystone, liver damage, hypertension and leukemia [<xref ref-type="bibr" rid="scirp.107986-ref3">3</xref>]. The works of Mensah and Golomeke have allowed discovering that extracted juice of H. sabdariffa has antioxidant properties [<xref ref-type="bibr" rid="scirp.107986-ref4">4</xref>]. In C&#244;te d’Ivoire, the most populations drink “bissap” juice, it is said to be rich in vitamin B6, calcium, potassium and other several elements that are yet to be isolated and characterized. In order to assess the radiological risks linked to the consumption of this plant and its derivatives by the population, we focused this study to determine the natural radioactivity levels from this plant and also evaluated the Average Annual Committed Effective Dose (AACED) due to the ingestion of radionuclides from H. sabdariffa.</p></sec><sec id="s2"><title>2. Methodology</title><p>Sample preparation</p><p>Samples of leaves of H. sabdariffa imported to C&#244;te d’Ivoire were collected from the local markets of C&#244;te d’Ivoire (<xref ref-type="fig" rid="fig1">Figure 1</xref>), these different varieties of leaves shown in <xref ref-type="table" rid="table1">Table 1</xref>. Samples were dried in the range of 25˚C at ambient air and grinded into a fine powder with a particle size &lt; 1 mm, 500 mg of each samples were put into standard Marinelli beaker and the activity concentrations for the natural radionuclide’s in the measured samples were computed. Samples were placed in Marinelli beaker sealed off and kept for one month, the time to achieve radioactive secular equilibrium between <sup>226</sup>Ra and <sup>222</sup>Rn and daughter nuclei. In order to determine the background distribution due to naturally occurring radionuclide’s in the environment around the detector, an empty Marinelli beaker container was counted in the same manner as the samples.</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Herbal samples investigated in this study</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Samples codes</th><th align="center" valign="middle" >Traditional name in C&#244;te d’Ivoire and parts used</th><th align="center" valign="middle" >Geographical of species Origin (Country)</th></tr></thead><tr><td align="center" valign="middle" >S01</td><td align="center" valign="middle" >Bissap-leaves</td><td align="center" valign="middle" >Burkina Faso</td></tr><tr><td align="center" valign="middle" >S02</td><td align="center" valign="middle" >Bissap-leaves</td><td align="center" valign="middle" >Burkina Faso</td></tr><tr><td align="center" valign="middle" >S03</td><td align="center" valign="middle" >Bissap-leaves</td><td align="center" valign="middle" >Burkina Faso</td></tr><tr><td align="center" valign="middle" >S04</td><td align="center" valign="middle" >Bissap-leaves</td><td align="center" valign="middle" >Burkina Faso</td></tr><tr><td align="center" valign="middle" >S05</td><td align="center" valign="middle" >Bissap-leaves</td><td align="center" valign="middle" >Burkina Faso</td></tr><tr><td align="center" valign="middle" >S06</td><td align="center" valign="middle" >Bissap-leaves</td><td align="center" valign="middle" >Burkina Faso</td></tr><tr><td align="center" valign="middle" >S07</td><td align="center" valign="middle" >Bissap-leaves</td><td align="center" valign="middle" >Burkina Faso</td></tr><tr><td align="center" valign="middle" >S08</td><td align="center" valign="middle" >Bissap-leaves</td><td align="center" valign="middle" >Burkina Faso</td></tr><tr><td align="center" valign="middle" >S09</td><td align="center" valign="middle" >Bissap-leaves</td><td align="center" valign="middle" >Mali</td></tr><tr><td align="center" valign="middle" >S10</td><td align="center" valign="middle" >Bissap-leaves</td><td align="center" valign="middle" >Mali</td></tr></tbody></table></table-wrap><p>Instrumentation and Calibration: Direct instrumental analysis without pre-treatment (non-destructive) was used for the measurement of gamma rays for the water samples using a High Purity Germanium detector (HPGE). The gamma spectrometry system consists of an n-type HPGE detector coupled to a computer based multi-channel analyzer (MCA). The relative efficiency of the detector is 25% with energy resolution of 1.8 keV at gamma-ray energy of 1332 keV of <sup>60</sup>Co. The identification of individual radionuclides was performed using their gamma-ray energies and the quantitative analysis of radionuclides was performed using gamma-ray spectrum analysis software, GENIE 2000. The detector is mounted in a cylindrical lead shield (100 mm) lined with copper, cadmium and plexiglass (3 mm each) to reduce the background radiation. The detector is cooled in liquid nitrogen at a temperature of −196˚C (77˚K). In order to determine the background distribution in the environment around the detector, ten empty Marinelli beakers were thoroughly cleaned and filled with distilled water and counted for 36,000 s in the same geometry as the samples. The background spectra were used to correct the net peak area of gamma rays of measured isotopes. The energy calibration of the spectrometry chain consists of establishing the relationship between channels and energy in the spectra. This was done using a set of gamma-emitting radionuclides (<sup>60</sup>Co and <sup>137</sup>Cs). The main parameter necessary to quantify radionuclide activity is the full energy peak efficiency. The efficiency calibrations were carried out by counting standard radionuclides of known activities with well-defined energies in the energy range of 60 keV to −2000 keV. After carrying out these operations, we determined the specific activity of the radionuclides like uranium (<sup>226</sup>Ra), thorium (<sup>232</sup>Th) and potassium (<sup>40</sup>K). The <sup>226</sup>Ra activity was measured by taking the mean activity of the two separate photo peaks of the daughter nuclides: <sup>214</sup>Pb at 351.9 keV and <sup>214</sup>Bi at 609.3 keV, the activity of <sup>232</sup>Th was determined using photo peaks of <sup>228</sup>Ac at 911.1 keV and the photopeak of <sup>212</sup>Pb at 238.6 keV and the activity of <sup>40</sup>K was directly determined using its gamma rays emitted at 1460.8 keV.</p><p>After measurement and subtraction of the background, the activity concentrations were calculated. The analytical expression used in the calculation of the activity concentrations in Bq/Kg for water samples is as shown in Equation (1)</p><p>A = N e λ t d P ⋅ T c ⋅ γ ⋅ M (1)</p><p>where N is the net counts of the radionuclide in the samples,t<sub>d</sub> is the delay time between sampling and counting, P is the gamma-ray emission probability (gamma-ray yield), γ is the absolute counting efficiency of the detector system, T<sub>c</sub> is the sample counting time, m is the mass of the sample (kg), exp(λt<sub>d</sub>) is the decay correction factor for delay between time of sampling and counting and λ is the decay constant of the parent radionuclide.</p><p>At energy E, M is the dry-weight of samples (kg).</p><p>The average annual committed effective dose, E<sub>ave</sub>, for ingestion of NORMS in the medicinal plants was calculated using the expression in Equation (2):</p><p>E a v e = I p ⋅ D C F i n g ⋅ A S p (2)</p><p>where DCF<sub>ing</sub> is the dose conversion factor for ingestion, for each radionuclide (i.e., 4.5 &#215; 10<sup>−5</sup> mSv/Bq, 2.3 &#215; 10<sup>−4</sup> mSv/Bq and 6.2 &#215; 10<sup>−6</sup> mSv/Bq for <sup>238</sup>U, <sup>232</sup>Th and <sup>40</sup>K respectively for an adult) [<xref ref-type="bibr" rid="scirp.107986-ref5">5</xref>], I<sub>p</sub> is the consumption rate from intake of NORMS in medicinal plants and A<sub>Sp</sub> is the activity concentration in the plant sample.</p></sec><sec id="s3"><title>3. Results and Discussion</title><p>In the second column of <xref ref-type="table" rid="table2">Table 2</xref> of radionuclides, the highest <sup>226</sup>Ra activity is (1.74) &#215; 10<sup>−3</sup> Bq/Kg of H. sabdariffa leaves from samples sold at the “march&#233; de Bingerville”, the lowest concentration (1.14) &#215; 10<sup>−4</sup> Bq/Kg measured corresponds to leaves of this species at the Marcory site. An average concentration activity level of (5.99 &#177; 0.31) &#215; 10<sup>−5</sup> Bq/Kg in <sup>226</sup>Ra is noted. Column three (3) of this table reports the activity concentrations in <sup>232</sup>Th, the maximum value is (6.72) &#215; 10<sup>−4</sup> Bq/Kg of H. sabdariffa . leaves at the Cocody site and the minimum is (6.08) &#215; 10<sup>−5</sup> Bq/Kg at the “march&#233; de Marcory”. The mean value is (1.59) &#215; 10<sup>−4</sup> Bq/Kg in <sup>232</sup>Th. The radionuclide <sup>40</sup>K has the most significant activity concentrations. The concentrations vary from (4.65) &#215; 10<sup>−3</sup> to (5.44) &#215; 10<sup>−4</sup> Bq/Kg respectively in Treichville site and “Grand-march&#233; de Koumassi” with an average of (1.95) &#215; 10<sup>−3</sup> Bq/Kg</p><p><xref ref-type="fig" rid="fig2">Figure 2</xref> shows the histograms of the radionuclides. We note a significant concentration of <sup>40</sup>K, when detected at sites S01, S02, S03, S05, S07 and S010 in the ten (10) collection markets. We also note a lower concentration than <sup>226</sup>Ra in market S06. The regular absorption and accumulation of this radionuclide over a given period of time may be one of the reasons for its higher concentration.in plants. Chethan Rao’s studies in 2012 showed that <sup>40</sup>K is an important radionuclide in plant metabolic activities [<xref ref-type="bibr" rid="scirp.107986-ref6">6</xref>]. The high concentration of potassium activity recorded may explain the use of the leaves of this plant for the treatment of hypertension since patients suffering from hypertension have a low concentration of potassium in their blood [<xref ref-type="bibr" rid="scirp.107986-ref7">7</xref>]. Among <sup>226</sup>Ra and <sup>232</sup>Th, <sup>226</sup>Ra is relatively higher, and it may be due to the fact that radium is chemically similar to calcium and calcium being one of the nutrients plants may absorb with radium, which will result in relatively more concentration of radium. The low <sup>232</sup>Th content of the plant can be explained by their insolubility and low specific activity. Ions of <sup>232</sup>Th bind weakly to soil particles that are not absorbed by the plant [<xref ref-type="bibr" rid="scirp.107986-ref8">8</xref>] (<xref ref-type="table" rid="table3">Table 3</xref>).</p><p>At the AACED level, the highest and lowest values are respectively at the Marcory site (251.492) nSv/y and the large at “march&#233; Gouro d’Adjam&#233;” (2.806) nSv/y. It is noted that these values are insignificant compared to the value of 0.3 mSv/y which can cause diseases to adults who regularly use H. sabdariffa leaves during the year. There is thus no radiological risk to consume this plant (<xref ref-type="table" rid="table4">Table 4</xref>).</p><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Activity concentrations of samples studied</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Site Codes</th><th align="center" valign="middle"  colspan="3"  >Radionuclides</th><th align="center" valign="middle" >Market</th></tr></thead><tr><td align="center" valign="middle"  rowspan="2"  ></td><td align="center" valign="middle"  colspan="3"  >Bq/Kg</td><td align="center" valign="middle"  rowspan="2"  ></td></tr><tr><td align="center" valign="middle" >Ra-226</td><td align="center" valign="middle" >Th-232</td><td align="center" valign="middle" >K-40</td></tr><tr><td align="center" valign="middle" >S01</td><td align="center" valign="middle" >(1.74)E−03</td><td align="center" valign="middle" >(6.89)E−05</td><td align="center" valign="middle" >(4.04)−03</td><td align="center" valign="middle" >March&#233; de Bingerville</td></tr><tr><td align="center" valign="middle" >S02</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >(1.28)E−04</td><td align="center" valign="middle" >(1.95)E−03</td><td align="center" valign="middle" >March&#233; GOURO d’Adjam&#233;</td></tr><tr><td align="center" valign="middle" >S03</td><td align="center" valign="middle" >(2.23)E−04</td><td align="center" valign="middle" >(1.72)E−04</td><td align="center" valign="middle" >(4.65)E−03</td><td align="center" valign="middle" >Grand march&#233; de Treichville</td></tr><tr><td align="center" valign="middle" >S04</td><td align="center" valign="middle" >(2.70)E−04</td><td align="center" valign="middle" >(1.40)E−04</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >Grand march&#233; de Port-Bouet</td></tr><tr><td align="center" valign="middle" >S05</td><td align="center" valign="middle" >(3.85)E−04</td><td align="center" valign="middle" >(1.12)E−04</td><td align="center" valign="middle" >(2.15)E−03</td><td align="center" valign="middle" >March&#233; Dj&#232; Konan de Koumassi</td></tr><tr><td align="center" valign="middle" >S06</td><td align="center" valign="middle" >(1.04)E−03</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >(5.44)E−04</td><td align="center" valign="middle" >Grand-march&#233; de Koumassi</td></tr><tr><td align="center" valign="middle" >S07</td><td align="center" valign="middle" >(1.71)E−03</td><td align="center" valign="middle" >(6.71)E−04</td><td align="center" valign="middle" >(3.26)E−03</td><td align="center" valign="middle" >March&#233; of Cocody</td></tr><tr><td align="center" valign="middle" >S08</td><td align="center" valign="middle" >(1.14)E−04</td><td align="center" valign="middle" >(6.08)E−05</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >March&#233; de Marcory</td></tr><tr><td align="center" valign="middle" >S09</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >(1.22)E−04</td><td align="center" valign="middle" >ND</td><td align="center" valign="middle" >March&#233; de Bingerville 2</td></tr><tr><td align="center" valign="middle" >S10</td><td align="center" valign="middle" >(5.11)E−04</td><td align="center" valign="middle" >(1.17)E−04</td><td align="center" valign="middle" >(2.94)E−03</td><td align="center" valign="middle" >March&#233; gouro Adjam&#233;</td></tr><tr><td align="center" valign="middle" >Mean</td><td align="center" valign="middle" >(5.99)E−04</td><td align="center" valign="middle" >(1.59)E−04</td><td align="center" valign="middle" >(1.95)E−03</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> The Average annual committed effective dose (AACED) of plant samples</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Site Codes</th><th align="center" valign="middle" >AACED (nSv/y)</th></tr></thead><tr><td align="center" valign="middle" >S01</td><td align="center" valign="middle" >119.195</td></tr><tr><td align="center" valign="middle" >S02</td><td align="center" valign="middle" >15.08</td></tr><tr><td align="center" valign="middle" >S03</td><td align="center" valign="middle" >7.425</td></tr><tr><td align="center" valign="middle" >S04</td><td align="center" valign="middle" >15.37</td></tr><tr><td align="center" valign="middle" >S05</td><td align="center" valign="middle" >107.823</td></tr><tr><td align="center" valign="middle" >S06</td><td align="center" valign="middle" >38.408</td></tr><tr><td align="center" valign="middle" >S07</td><td align="center" valign="middle" >25,492</td></tr><tr><td align="center" valign="middle" >S08</td><td align="center" valign="middle" >19.114</td></tr><tr><td align="center" valign="middle" >S09</td><td align="center" valign="middle" >2.806</td></tr><tr><td align="center" valign="middle" >S10</td><td align="center" valign="middle" >68.133</td></tr><tr><td align="center" valign="middle" >Mean</td><td align="center" valign="middle" >33.589</td></tr></tbody></table></table-wrap><table-wrap id="table4" ><label><xref ref-type="table" rid="table4">Table 4</xref></label><caption><title> Comparison of the annual committed effective doses (Eave) due to the natural radionuclides in the medicinal plant with others countries</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Country</th><th align="center" valign="middle" >Range</th><th align="center" valign="middle" >Samples</th><th align="center" valign="middle" >Reference</th></tr></thead><tr><td align="center" valign="middle" >C&#244;te d’Ivoire</td><td align="center" valign="middle" >2.8 - 251.5 nSv/Y</td><td align="center" valign="middle" >H. sabdariffa_leaf</td><td align="center" valign="middle" >present work</td></tr><tr><td align="center" valign="middle" >Ghana</td><td align="center" valign="middle" >9000 - 14,000 nSv</td><td align="center" valign="middle" >Medicinal plants</td><td align="center" valign="middle" >[<xref ref-type="bibr" rid="scirp.107986-ref9">9</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ><sup>238</sup>U: 0.7 - 9.7 nSv</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >Serbia</td><td align="center" valign="middle" ><sup>232</sup>Th: 0.3 - 2.8 nSv/y</td><td align="center" valign="middle" >Tea herb</td><td align="center" valign="middle" >[<xref ref-type="bibr" rid="scirp.107986-ref10">10</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ><sup>40</sup>K: 1026 - 10,132.2 nSv/y</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >Iraq</td><td align="center" valign="middle" >1380 - 1950 nSv/y</td><td align="center" valign="middle" >Medicinal plants0</td><td align="center" valign="middle" >[<xref ref-type="bibr" rid="scirp.107986-ref11">11</xref>]</td></tr></tbody></table></table-wrap><p>The average annual committed effective dose due to <sup>238</sup>U, <sup>232</sup>Th and <sup>40</sup>K for this study was relatively low compared to that which was reported for medicinal plants from [<xref ref-type="bibr" rid="scirp.107986-ref9">9</xref>] and [<xref ref-type="bibr" rid="scirp.107986-ref10">10</xref>], almost similar than [<xref ref-type="bibr" rid="scirp.107986-ref11">11</xref>] for herbal tea.</p></sec><sec id="s4"><title>4. Conclusion</title><p>In this work, the AACED results obtained show that there is no radiological fear to use this plant because they are far below the world value for an individual which is 0.30 mSv/y. The element potassium which has an important role in the treatment of hypertension and radium which is similar to calcium which strengthens the strength of skeletal bones, leads us to conclude that this plant has therapeutic and nutritional virtues.</p></sec><sec id="s5"><title>Availability of Supporting Data</title><p>The datasets supporting the conclusions of this article are included within the article.</p></sec><sec id="s6"><title>Funding</title><p>This research was supported by the Laboratory of Nuclear physics and Radiation protection of the University Felix Houphouet-Boigny of Cocody, Abidjan, C&#244;te d’Ivoire.</p></sec><sec id="s7"><title>Contributions</title><p>ADA, DL, and BO designed the experiment. ADA, BO, and DL carried out the experimental studies and collection, analysis, and interpretation of data. ADA wrote the manuscript. BO helped to draft and revised the manuscript. The authors read and approved the final manuscript.</p></sec><sec id="s8"><title>Acknowledgements</title><p>The authors thank the Institute for Radiation Protection (RPI) of the Ghana Atomic Energy Commission (GAEC) for the use of their facilities.</p></sec><sec id="s9"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s10"><title>Cite this paper</title><p>Alfred, A.D.D., Koudou, D. and Jean-Claude, B.O. (2021) Determination of Natural Radioactivity of the Hibiscus sabdariffa Linn (Roselle) Used in C&#244;te d’Ivoire (Ivory Coast). Advances in Materials Physics and Chemistry, 11, 59-66. https://doi.org/10.4236/ampc.2021.113006</p></sec><sec id="s11"><title>Abbreviations</title><p><sup>60</sup>Co: Cobalt 60</p><p><sup>137</sup>Cs: Cesium 137</p><p>Bi: Bismuth</p><p>Ac: Actinium</p><p>Pb: Lead</p><p><sup>232</sup>Th: Thorium</p><p><sup>238 </sup>U: Uranium</p><p><sup>226 </sup>Ra: Radium</p><p><sup>40</sup>K: Potassium</p><p>NORMS: Naturally Occurring Radioactive Materials</p><p>H. sabdariffa: Hisbiscus sabdariffa</p><p>HPGE: High Purity Germanium detector</p><p>MCA: multi-channel analyzer</p><p>AACED: The average annual committed effective dose</p></sec></body><back><ref-list><title>References</title><ref id="scirp.107986-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Jevremovic, M., Lazarevic, N., Pavlovic, S. and Orlic, M. 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