<?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">GEP</journal-id><journal-title-group><journal-title>Journal of Geoscience and Environment Protection</journal-title></journal-title-group><issn pub-type="epub">2327-4336</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/gep.2022.105002</article-id><article-id pub-id-type="publisher-id">GEP-117110</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>
 
 
  Heavy Metals in the Northwest Agricultural Region Dominican Republic
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Ramón</surname><given-names>Delanoy</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>Carime</surname><given-names>Matos Espinosa</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>Yamilesa</surname><given-names>Herrera</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>Institute of Physics, Faculty of Sciences, Autonomous University of Santo Domingo, Ministry of Higher Education Science and Technology, Santo Domingo, Dominican Republic</addr-line></aff><pub-date pub-type="epub"><day>09</day><month>05</month><year>2022</year></pub-date><volume>10</volume><issue>05</issue><fpage>16</fpage><lpage>24</lpage><history><date date-type="received"><day>8,</day>	<month>April</month>	<year>2022</year></date><date date-type="rev-recd"><day>10,</day>	<month>May</month>	<year>2022</year>	</date><date date-type="accepted"><day>13,</day>	<month>May</month>	<year>2022</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 currently represent a very important source of contamination, since their intake by humans and animals in many cases is the cause of serious damage to health. Soil, air, water and food are the most common pathways for heavy metals to reach organisms. Since soil is their origin, in this study we focus on soil analysis to determine the concentration of Cr, Ni, Cu, Zn, As, Hg, Cd and Pb, which are the most toxic metals. The study site is the agricultural soils of the northwestern region of the Dominican Republic where bananas and rice are the main crops grown. Chromium levels in most samples exceeded the NOAA-USEPA Probable Effects Level (PEL). Other heavy metals were within the acceptable ranges for healthy soil, according to the Food and Agriculture Organization (FAO).
 
</p></abstract><kwd-group><kwd>Heavy Metals</kwd><kwd> Soil Contamination</kwd><kwd> Agricultural Soils</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>The northwestern region of the Dominican Republic economically dedicated to agricultural activities (Londo&#241;o-Franco et al., 2016) represents a great food source for the Dominican people and the border towns (Butterlini, 1955). The presence of heavy metals in agricultural soils (Romic &amp; Romic, 2003) of heavy metals such as Cr, Ni, Cu, Zn, As, Hg, Cd and Pb could represent a health risk (Al-Taani et al., 2021). In the earth’s crust, all these metals are found in small quantities in the form of traces, except in mining areas (Rudnick &amp; Gaos, 2003). Heavy metals are a group of chemical whose density is greater 7.0 gr∙cm<sup>−3</sup>. Many heavy metals are also called trace element, because their concentration does not reach 0.1% in rocks and soils (Duffus, 2002). The cultivation of bananas and rice covers almost all the areas of agricultural soils in the sedimentary plains of the Yaque of the Norte River (Fuentes-Hern&#225;ndez et al., 2019), which are products of erosion (Fonseca et al., 2011) of the northern slope of the central mountain range and the southern slope of the northern mountain range during the recent Quaternary and today. The texture of the soils is sand, silt and clay dragged by the Yaque of the Norte and its tributaries Bao, Guanajuma, J&#225;nico, Amina, Mao and Jicome. This is the reason why the composition of these soils is basically the mineralogical composition of both mountain ranges, which varies along the banks of the Yaque of the Norte River and its tributaries. The geological formations of Tireo, Loma Caribe, Loma la Peguera (McDonald et al., 2010; Vyzmalov&#225; et al., 2012) and Guanajuma mainly structured by peridotites (Marchesi et al., 2016) and composed of harzburgite minerals, lherzolites, tholeiitic, komatiitic and gabbro (IGME-BRGM-Inipsa, 2010) are made up of chromium spinel (Lewis et al., 2006) and nickel (Aiglsperger et al., 2015), which contribute to the presence of these trace metals in the agricultural soils of the northwestern region of the Dominican Republic. Nickel and chromium are elements that bioaccumulate (Barea-Sep&#250;lveda et al., 2022) in the husks of rice (Aqeel Kamran et al., 2016; Raju et al., 2016). So, the frequent intake of brown rice can represent a risk to health if it is grown in soils with a high content of these metals, which are bioavailable (Shahbaz et al., 2018).</p><p>Heavy metals can accumulate in agricultural soils, posing a health risk for soil organisms and humans, its negative effects depending on the concentrations of the metals and specific properties of the soil (Gjoka et al., 2010). Therefore, the presence of trace metals in soils is of great importance (Xuan et al., 2017). However, in appropriate concentrations, crops use them as nutrients to synthesize fruits which constitute the most important source of nutrition. Such is the case of Chromium that helps metabolize sugars, but in excess, especially Cr<sup>+6</sup>, is very harmful to health (Turner &amp; Lewis, 2018). Other elements that in appropriate concentrations are good for nutrition are Ni and Zn, and in the same way could be fatal in high concentrations (Prieto-M&#233;ndez et al., 2009). High concentrations of heavy metals can inhibit the development of crops and their fruits when absorbed by the roots (P&#233;rez-Olvera et al., 2008). Leachate from these soils can contaminate surface and underground aquifers (Bravo-Covarrubias et al., 2020), and make the waters toxic to plants, animals and humans, through the food chain (Mart&#237;nez-Alva et al., 2020). In addition, crops that bioaccumulate (Mesa-P&#233;rez et al., 2015) these metals would become a danger to the health of those who consume them (Vinodhini et al., 2008).</p>Study Zone<p>The study site is the soils of several towns that are dedicated to the cultivation of rice and bananas, especially in the provinces of Mao and Montecristi and the adjoining town of Navarrete, belonging to the province of Santiago, approximate area of 450 km<sup>2</sup> (<xref ref-type="fig" rid="fig1">Figure 1</xref>).</p></sec><sec id="s2"><title>2. Materials and Methods</title><sec id="s2_1"><title>2.1. Sampling</title><p>Soil sampling was carried out by plots, referencing the sampling site with GPS. These points were taken randomly depending on the access facilities and the distribution of the crops. A plastic shovel was used to collect approximately 1.0 kg of soil, both at the surface level and at a depth of 30 cm. To take the sample at a depth of 30 centimeters, a hole was made with a stainless steel tool. Then they were packed in plastic bags to be transported.</p></sec><sec id="s2_2"><title>2.2. Drying</title><p>The samples were dried, first at room temperature, and then to remove all humidity in an oven at a temperature between 30 - 100 degrees Celsius; for slow drying and to decrease the possibility that some elements will evaporate along with the water.</p></sec><sec id="s2_3"><title>2.3. Sample Preparation</title><p>After drying, the samples were crushed in a mortar and then sieved at 75 microns. This sieve mesh was chosen because the texture of the soils in the region is composed of a significant amount of sand. About 3 g were taken, measured on a 0.1 mg precision balance. With this mass of soil, using a press (15 tons), a tablet with a diameter of 2.0 cm was made.</p></sec><sec id="s2_4"><title>2.4. Methodology and Analysis</title><p>The tablet was taken and placed in an x-ray fluorescence spectrometer (Roca &amp; Bayon, 1981; Fern&#225;ndez-Ruiz, 2009) brand Skyray EDX36000B. The excitation voltage of the X-ray emitting source was 40 kV and 600 μA (Margu&#237; et al., 2011). The spectrometer was previously calibrated using standard sediment and soil samples certified to ISO/IEC 17025 and ISO Guide 34 by Sigma-Aldrich (TraceCert; NIST, IAEA) and BAM-CRM (SRM1944, SRM2707, SRM1646a and IAEA356). The quality of the heavy metal determinations was verified using the certified materials BCR277, SRM2710a, SRM2711a. The values of the NOAA-SQuiRTs and USEPA guide, which are for marine sediments, fresh waters and soils, coincide with the Canadian agricultural sediments and soils guide (CCME, 2014). For this reason we compare the Threshold Effects Levels (TEL) of a metal with the limits of the guide for a healthy soil in relation to this metal, they coincide in both guides. They were also compared to FAO data, for common agricultural soil concentrations (<xref ref-type="table" rid="table1">Table 1</xref>).</p></sec></sec><sec id="s3"><title>3. Results</title><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Concentration of heavy metals in agricultural soils expressed in mg.kg<sup>−1</sup> (Source: Freedman, 2018)</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Elem</th><th align="center" valign="middle" >Granite</th><th align="center" valign="middle" >Basalt</th><th align="center" valign="middle" >Shale</th><th align="center" valign="middle" >Limestone</th><th align="center" valign="middle" >Sandstone</th><th align="center" valign="middle" >Soils</th></tr></thead><tr><td align="center" valign="middle" >Cd</td><td align="center" valign="middle" >0.09</td><td align="center" valign="middle" >0.13</td><td align="center" valign="middle" >0.22</td><td align="center" valign="middle" >0.03</td><td align="center" valign="middle" >0.05</td><td align="center" valign="middle" >0.35</td></tr><tr><td align="center" valign="middle" >Co</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >35</td><td align="center" valign="middle" >19</td><td align="center" valign="middle" >0.1</td><td align="center" valign="middle" >0.3</td><td align="center" valign="middle" >8</td></tr><tr><td align="center" valign="middle" >Cr</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >90</td><td align="center" valign="middle" >90</td><td align="center" valign="middle" >11</td><td align="center" valign="middle" >35</td><td align="center" valign="middle" >70</td></tr><tr><td align="center" valign="middle" >Cu</td><td align="center" valign="middle" >13</td><td align="center" valign="middle" >90</td><td align="center" valign="middle" >39</td><td align="center" valign="middle" >5.5</td><td align="center" valign="middle" >30</td><td align="center" valign="middle" >30</td></tr><tr><td align="center" valign="middle" >Ni</td><td align="center" valign="middle" >0.5</td><td align="center" valign="middle" >150</td><td align="center" valign="middle" >68</td><td align="center" valign="middle" >7</td><td align="center" valign="middle" >9</td><td align="center" valign="middle" >50</td></tr><tr><td align="center" valign="middle" >Pb</td><td align="center" valign="middle" >24</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >23</td><td align="center" valign="middle" >5.7</td><td align="center" valign="middle" >10</td><td align="center" valign="middle" >35</td></tr><tr><td align="center" valign="middle" >Zn</td><td align="center" valign="middle" >52</td><td align="center" valign="middle" >100</td><td align="center" valign="middle" >120</td><td align="center" valign="middle" >20</td><td align="center" valign="middle" >30</td><td align="center" valign="middle" >90</td></tr></tbody></table></table-wrap><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Maximum, minimum and average levels of Heavy Metals in Rice cultivation areas in the municipality of Esperanza, Mao Province; Casta&#241;uela, Montecristi province. Threshold Effects Levels (TEL) and Probable Effects Levels (PEL), NOAA-USEPA</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="3"  >Element</th><th align="center" valign="middle" >Sed</th><th align="center" valign="middle" >Soil</th><th align="center" valign="middle" >TEL</th><th align="center" valign="middle" >PEL</th><th align="center" valign="middle"  colspan="4"  >Esperanza (54)</th><th align="center" valign="middle"  colspan="3"  >Casta&#241;uela (20)</th></tr></thead><tr><td align="center" valign="middle"  colspan="4"   rowspan="2"  >(&#181;g/g)</td><td align="center" valign="middle"  colspan="2"  >Min</td><td align="center" valign="middle" >Max</td><td align="center" valign="middle" >Mean</td><td align="center" valign="middle" >Min</td><td align="center" valign="middle" >Max</td><td align="center" valign="middle" >Mean</td></tr><tr><td align="center" valign="middle"  colspan="4"  >(&#181;g/g)</td><td align="center" valign="middle"  colspan="3"  >(&#181;g/g)</td></tr><tr><td align="center" valign="middle" >Cr</td><td align="center" valign="middle" >37.3</td><td align="center" valign="middle" >64</td><td align="center" valign="middle" >52.30</td><td align="center" valign="middle" >160.0</td><td align="center" valign="middle"  colspan="2"  >75</td><td align="center" valign="middle" >430.2</td><td align="center" valign="middle" >268.5</td><td align="center" valign="middle" >278.9</td><td align="center" valign="middle" >628.2</td><td align="center" valign="middle" >378.5</td></tr><tr><td align="center" valign="middle" >Ni</td><td align="center" valign="middle" >17.0</td><td align="center" valign="middle" >45</td><td align="center" valign="middle" >15.90</td><td align="center" valign="middle" >42.8</td><td align="center" valign="middle"  colspan="2"  >0</td><td align="center" valign="middle" >111.2</td><td align="center" valign="middle" >37.4</td><td align="center" valign="middle" >20.3</td><td align="center" valign="middle" >69.8</td><td align="center" valign="middle" >40.0</td></tr><tr><td align="center" valign="middle" >Cu</td><td align="center" valign="middle" >35.7</td><td align="center" valign="middle" >63</td><td align="center" valign="middle" >18.70</td><td align="center" valign="middle"  colspan="2"  >108.0</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >56.3</td><td align="center" valign="middle" >11.8</td><td align="center" valign="middle" >2.0</td><td align="center" valign="middle" >7.2</td><td align="center" valign="middle" >4.2</td></tr><tr><td align="center" valign="middle" >Zn</td><td align="center" valign="middle" >123</td><td align="center" valign="middle" >250</td><td align="center" valign="middle" >124.00</td><td align="center" valign="middle"  colspan="2"  >271.0</td><td align="center" valign="middle" >15.1</td><td align="center" valign="middle" >129.5</td><td align="center" valign="middle" >55.9</td><td align="center" valign="middle" >21.0</td><td align="center" valign="middle" >68.9</td><td align="center" valign="middle" >40.5</td></tr><tr><td align="center" valign="middle" >As</td><td align="center" valign="middle" >5.9</td><td align="center" valign="middle" >5.2</td><td align="center" valign="middle" >7.24</td><td align="center" valign="middle"  colspan="2"  >41.2</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >4.4</td><td align="center" valign="middle" >1.3</td><td align="center" valign="middle" >2.2</td><td align="center" valign="middle" >4.1</td><td align="center" valign="middle" >2.9</td></tr><tr><td align="center" valign="middle" >Hg</td><td align="center" valign="middle" >0.17</td><td align="center" valign="middle" >6.6</td><td align="center" valign="middle" >0.13</td><td align="center" valign="middle"  colspan="2"  >0.7</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >0</td></tr><tr><td align="center" valign="middle" >Cd</td><td align="center" valign="middle" >0.6</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >0.6</td><td align="center" valign="middle"  colspan="2"  >3.5</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >2.1</td><td align="center" valign="middle" >3.1</td><td align="center" valign="middle" >2.5</td></tr><tr><td align="center" valign="middle" >Pb</td><td align="center" valign="middle" >35.0</td><td align="center" valign="middle" >70</td><td align="center" valign="middle" >30.20</td><td align="center" valign="middle"  colspan="2"  >112.0</td><td align="center" valign="middle" >21.2</td><td align="center" valign="middle" >53.9</td><td align="center" valign="middle" >37.7</td><td align="center" valign="middle" >12.3</td><td align="center" valign="middle" >58.7</td><td align="center" valign="middle" >38.8</td></tr><tr><td align="center" valign="middle" ></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><td align="center" valign="middle" ></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><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr></tbody></table></table-wrap><p>The values of Sediment (Sed) correspond to the maximum levels in sediments and those of Soil to the maximum values in agricultural soil according to the Canadian guide (CCME, 2014).</p></sec><sec id="s4"><title>4. Discussion</title><p>The Cr values in the municipality of Casta&#241;uela (20 samples), Monte Cristi province were higher than in the municipality of Esperanza (54 samples) (<xref ref-type="table" rid="table2">Table 2</xref>),</p><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> Values of trace elements in soil samples by village (sample number in parentheses)</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="3"  >Element</th><th align="center" valign="middle"  colspan="3"  >Jicome (10)</th><th align="center" valign="middle"  colspan="3"  >Villa V&#225;squez (10)</th><th align="center" valign="middle"  colspan="3"  >Navarrete(7)</th></tr></thead><tr><td align="center" valign="middle" >Min</td><td align="center" valign="middle" >Max</td><td align="center" valign="middle" >Mean</td><td align="center" valign="middle" >Min</td><td align="center" valign="middle" >Max</td><td align="center" valign="middle" >Mean</td><td align="center" valign="middle" >Min</td><td align="center" valign="middle" >Max</td><td align="center" valign="middle" >Mean</td></tr><tr><td align="center" valign="middle"  colspan="3"  >(&#181;g/g)</td><td align="center" valign="middle"  colspan="3"  >(&#181;g/g)</td><td align="center" valign="middle"  colspan="3"  >(&#181;g/g)</td></tr><tr><td align="center" valign="middle" >Cr</td><td align="center" valign="middle" >122.5</td><td align="center" valign="middle" >628.5</td><td align="center" valign="middle" >347.5</td><td align="center" valign="middle" >161.1</td><td align="center" valign="middle" >396.3</td><td align="center" valign="middle" >288.9</td><td align="center" valign="middle" >66.7</td><td align="center" valign="middle" >386.6</td><td align="center" valign="middle" >164.5</td></tr><tr><td align="center" valign="middle" >Ni</td><td align="center" valign="middle" >7.8</td><td align="center" valign="middle" >183.7</td><td align="center" valign="middle" >62.2</td><td align="center" valign="middle" >4.3</td><td align="center" valign="middle" >85.0</td><td align="center" valign="middle" >41.2</td><td align="center" valign="middle" >51.6</td><td align="center" valign="middle" >217.2</td><td align="center" valign="middle" >114.3</td></tr><tr><td align="center" valign="middle" >Cu</td><td align="center" valign="middle" >20</td><td align="center" valign="middle" >14.4</td><td align="center" valign="middle" >5.4</td><td align="center" valign="middle" >2.7</td><td align="center" valign="middle" >9.0</td><td align="center" valign="middle" >5.7</td><td align="center" valign="middle" >8.5</td><td align="center" valign="middle" >68.2</td><td align="center" valign="middle" >25.2</td></tr><tr><td align="center" valign="middle" >Zn</td><td align="center" valign="middle" >20.4</td><td align="center" valign="middle" >68.9</td><td align="center" valign="middle" >37</td><td align="center" valign="middle" >23.4</td><td align="center" valign="middle" >58.1</td><td align="center" valign="middle" >39.1</td><td align="center" valign="middle" >29.6</td><td align="center" valign="middle" >58.4</td><td align="center" valign="middle" >43.3</td></tr><tr><td align="center" valign="middle" >As</td><td align="center" valign="middle" >2</td><td align="center" valign="middle" >4.1</td><td align="center" valign="middle" >3.1</td><td align="center" valign="middle" >2.1</td><td align="center" valign="middle" >3.5</td><td align="center" valign="middle" >2.8</td><td align="center" valign="middle" >2.1</td><td align="center" valign="middle" >3.7</td><td align="center" valign="middle" >2.9</td></tr><tr><td align="center" valign="middle" >Hg</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><td align="center" valign="middle" ></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><tr><td align="center" valign="middle" >Cd</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >3.5</td><td align="center" valign="middle" >3.5</td><td align="center" valign="middle" >3.5</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >Pb</td><td align="center" valign="middle" >6.3</td><td align="center" valign="middle" >58.7</td><td align="center" valign="middle" >34.6</td><td align="center" valign="middle" >20.0</td><td align="center" valign="middle" >57.4</td><td align="center" valign="middle" >32.1</td><td align="center" valign="middle" >24.5</td><td align="center" valign="middle" >39.3</td><td align="center" valign="middle" >31.4</td></tr></tbody></table></table-wrap><p>Valverde Mao province (<xref ref-type="fig" rid="fig2">Figure 2</xref>(a)), exceeding the PEL (<xref ref-type="fig" rid="fig3">Figure 3</xref>(a)). Ni was another element that, according to the spatial distribution (<xref ref-type="fig" rid="fig2">Figure 2</xref>(b)), had concentrations higher than PEL in several places (<xref ref-type="fig" rid="fig3">Figure 3</xref>(b)). Cd and Pb exceeded the TEL on average, but did not exceed the PEL. In both places the values of the metals were similar with little difference. All the samples taken in Casta&#241;uela were in rice cultivation; those of Esperanza were mixed between cultivation of bananas and rice. It is noted that mercury was not found above 0.3 mg/kg, which is the quantification limit of the equipment. We compare the values of the metals in the superficial samples with the deeper ones, in some cases the superficial ones contain higher values and in other cases the deeper ones. In the case of Cd, only two samples had quantifiable concentration levels with the equipment used. Hg was not determined in any of the samples.</p><p><xref ref-type="table" rid="table3">Table 3</xref> shows that the average Cr exceeded the PEL in the samples from the three cultivation areas. The Ni in Jicome and Navarrete exceeded the PEL. The concentrations of the other metals were still below the TEL.</p></sec><sec id="s5"><title>5. Conclusion</title><p>The concentrations of heavy metals were found, in most cases exceeding the Probable Effect Levels (PEL) established by USEPA and CEQGs. These heavy metal concentrations are traceable to their origin as the Yaque of the Norte River eroded the mountains to form peridotite rocks composed of spinel minerals containing Chromium and Nickel, such as harzburgites, lherzolites, tholeiites, komatiites and gabbros. Therefore, these soils can be considered free of heavy metal contamination due to human activities in the area. The high concentrations of Cr and Ni, which exceed the PEL levels, are of natural origin, a product of the geochemistry of the rocks that gave rise to the soils of the Cibao valley basin in the northwest of the Dominican Republic, not due to the anthropogenic activities.</p></sec><sec id="s6"><title>Acknowledgements</title><p>To Ministry of higher education, science and technology for its financing. To the staff of the Dean of the Faculty of Sciences of the Autonomous University of Santo Domingo, especially Dean Radhames Silverio for his support in the administrative procedures. Kendrick P&#233;rez and Thara Caba for help in sample preparation and Juan Pablo Gonz&#225;lez for his support in taking samples. To the reviewers for their comments.</p></sec><sec id="s7"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s8"><title>Cite this paper</title><p>Delanoy, R., Espinosa, C. M., &amp; Herrera, Y. (2022). Heavy Metals in the Northwest Agricultural Region Dominican Republic. Journal of Geoscience and Environment Protection, 10, 16-24. https://doi.org/10.4236/gep.2022.105002</p></sec></body><back><ref-list><title>References</title><ref id="scirp.117110-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Aiglsperger, T., Proenza, J. A., Zaccarini, F. et al. (2015). Platinum Group Minerals (PGM) in the Falcondo Ni-Laterite Deposit, Loma Caribe Peridotite (Dominican Republic). Miner Deposita, 50, 105-123. https://doi.org/10.1007/s00126-014-0520-9.</mixed-citation></ref><ref id="scirp.117110-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Al-Taani, A. A., Nazzal, Y., Howari, F. M., Iqbal, J., Bou Orm, N., Xavier, C. M., B&amp;#259;rbulescu, A., Sharma, M., &amp; Dumitriu, C.-S. (2021). Contamination Assessment of Heavy Metals in Agricultural Soil, in the Liwa Area (UAE). Toxics, 9, Article No. 53. https://doi.org/10.3390/toxics9030053</mixed-citation></ref><ref id="scirp.117110-ref3"><label>3</label><mixed-citation publication-type="other" xlink:type="simple">Aqeel Kamran, M., Syed, A., Musstjab Akber, S., Bibi, S., Xu, R., Hussain-Monis, M. F., Katsoyiannis, A., Bokhari, H., Chaudhary, H., &amp; Chaudhary, J. (2016). Bioaccumulation of Nickel by E. sativa and Role of Plant Growth Promoting Rhizobacteria (PGPRs) under Nickel Stress. Ecotoxicology and Environmental Safety, 126, 256-263. https://doi.org/10.1016/j.ecoenv.2016.01.002</mixed-citation></ref><ref id="scirp.117110-ref4"><label>4</label><mixed-citation publication-type="other" xlink:type="simple">Barea-Sepúlveda, M., Espada-Bellido, E, Ferreiro-González, M., Bouziane, H., López-Castillo, J. G., Palma, M., &amp; Barbero, G. F. (2022). Toxic Elements and Trace Elements in Macrolepiota procera Mushrooms from Southern Spain and Northern Morocco. Journal of Food Composition and Analysis, 108, Article ID: 104419. https://doi.org/10.1016/j.jfca.2022.104419</mixed-citation></ref><ref id="scirp.117110-ref5"><label>5</label><mixed-citation publication-type="other" xlink:type="simple">Bravo-Covarrubias, A., Torres, E., Ayora, C., &amp; Ramos-Arroyo, Y. R. (2020). Movilidad de arsénico en los sedimentos de una presa que recibe escurrimientos de minas epitermales. Revista Internacional de Contaminación Ambiental, 36, 797-811. https://doi.org/10.20937/RICA.53318</mixed-citation></ref><ref id="scirp.117110-ref6"><label>6</label><mixed-citation publication-type="other" xlink:type="simple">Butterlini, J. (1955). La Geología de la República de Haití. Revista Geográfica, 16, 151-167. http://www.jstor.org/stable/40996381.</mixed-citation></ref><ref id="scirp.117110-ref7"><label>7</label><mixed-citation publication-type="other" xlink:type="simple">Canadian Council of Ministers of the Environment (CCME) (2014). Canadian Environmental Quality Guidelines (CEQGs).</mixed-citation></ref><ref id="scirp.117110-ref8"><label>8</label><mixed-citation publication-type="other" xlink:type="simple">Duffus, J. H. (2002). ‘Heavy Metals’—A Meaningless Term? Pure and Applied Chemistry, 74, 793-807. https://doi.org/10.1351/pac200274050793</mixed-citation></ref><ref id="scirp.117110-ref9"><label>9</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Fernández-Ruiz</surname><given-names> R. </given-names></name>,<etal>et al</etal>. (<year>2009</year>)<article-title>. Fluorescencia de Rayos X por Reflexión Total (TXRF): Una gran desconocida</article-title><source> Anales de Química</source><volume> 106</volume>,<fpage> 5</fpage>-<lpage>12</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.117110-ref10"><label>10</label><mixed-citation publication-type="other" xlink:type="simple">Fonseca, B., Figueiredo, H., Rodrigues, J., Queiroz, A., &amp; Tavares, T. (2011). Mobility of Cr, Pb, Cd, Cu and Zn in a Loamy Sand Soil: A Comparative Study. Geoderma, 164, 232-237. https://doi.org/10.1016/j.geoderma.2011.06.016 https://www.sciencedirect.com/science/article/pii/S0016706111001856</mixed-citation></ref><ref id="scirp.117110-ref11"><label>11</label><mixed-citation publication-type="other" xlink:type="simple">Freedman, B. (2018). Environmental Science. The Environment. Dalhousie University Libraries Digital Editions. https://digitaleditions.library.dal.ca/environmentalscience/chapter/chapter-18-toxic-elements/</mixed-citation></ref><ref id="scirp.117110-ref12"><label>12</label><mixed-citation publication-type="other" xlink:type="simple">Fuentes-Hernández, M. V., Sanguinetti-Gamboa, O. A., &amp; Rojas-De-Astudillo, L. L. (2019). Evaluación Del Riesgo Ambiental De Metales Pesados En Los Sedimentos Superficiales Del Saco Del Golfo De Cariaco. Revista Internacional de Contaminación Ambiental, 35, 101-114. https://doi.org/10.20937/RICA.2019.35.01.07 https://www.revistascca.unam.mx/rica/index.php/rica/article/view/RICA.2019.35.01.07</mixed-citation></ref><ref id="scirp.117110-ref13"><label>13</label><mixed-citation publication-type="other" xlink:type="simple">Gjoka, M., Kurant, M., Butts, C. T., &amp; Markopoulou, A. (2010, March). Walking in Facebook: A Case Study of Unbiased Sampling of OSNs. In 2010 Proceedings IEEE INFOCOM (pp. 1-9). Institute of Electrical and Electronics Engineers. https://doi.org/10.1109/INFCOM.2010.5462078</mixed-citation></ref><ref id="scirp.117110-ref14"><label>14</label><mixed-citation publication-type="other" xlink:type="simple">IGME-BRGM-Inipsa (2010). Hoja La Vega (6073-I). Cartografía Geotemática. Servicio Geológico Nacional, República Dominicana. http://repo.sgn.gob.do/memogeo50/MemoG_6073_I_LaVega.pdf</mixed-citation></ref><ref id="scirp.117110-ref15"><label>15</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Lewis</surname><given-names> J. F.</given-names></name>,<name name-style="western"><surname> Draper</surname><given-names> G.</given-names></name>,<name name-style="western"><surname> Proenza</surname><given-names> J. A.</given-names></name>,<name name-style="western"><surname> Espaillat</surname><given-names> J.</given-names></name>,<name name-style="western"><surname> &amp; Jiménez</surname><given-names> J. </given-names></name>,<etal>et al</etal>. (<year>2006</year>)<article-title>. Ophiolite-Related Ultramafic Rocks (Serpentinites) in the Caribbean Region: A Review of Their Occurrence, Composition, Origin, Emplacement and Nickel Laterite Soils</article-title><source> Geologica Acta</source><volume> 4</volume>,<fpage> 237</fpage>-<lpage>263</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.117110-ref16"><label>16</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Londo&amp;#241;o-Franco</surname><given-names> L. F.</given-names></name>,<name name-style="western"><surname> Londo&amp;#241;o-Mu&amp;#241;oz</surname><given-names> P. T.</given-names></name>,<name name-style="western"><surname> &amp; Mu&amp;#241;oz-García</surname><given-names> F. G. </given-names></name>,<etal>et al</etal>. (<year>2016</year>)<article-title>. The Risks of Heavy Metals in Human and Animal Health</article-title><source> Biotecnología en el Sector Agropecuario y Agroindustrial</source><volume> 14</volume>,<fpage> 145</fpage>-<lpage>153</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.117110-ref17"><label>17</label><mixed-citation publication-type="other" xlink:type="simple">Marchesi, C., Garrido, C. J., Proenza, J. A., Hidas, K., Varas-Reus, M. I., Butjosa, L., &amp; Lewis, J. F. (2016). Geochemical Record of Subduction Initiation in the Sub-Arc Mantle: Insights from the Loma Caribe Peridotite (Dominican Republic). Lithos, 252, 1-15. https://doi.org/10.1016/j.lithos.2016.02.009</mixed-citation></ref><ref id="scirp.117110-ref18"><label>18</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Marguí</surname><given-names> E.</given-names></name>,<name name-style="western"><surname> Gonzalez</surname><given-names> O.</given-names></name>,<name name-style="western"><surname> Hidalgo</surname><given-names> M.</given-names></name>,<name name-style="western"><surname> Pardini</surname><given-names> G.</given-names></name>,<name name-style="western"><surname> &amp; Queralt</surname><given-names> I. </given-names></name>,<etal>et al</etal>. (<year>2011</year>)<article-title>. Aplicación de la técnica de espectrometría de fluorescencia de rayos-X en el estudio de la dispersión de metales en áreas mineras</article-title><source> Boletín Geológico y Minero</source><volume> 122</volume>,<fpage> 273</fpage>-<lpage>286</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.117110-ref19"><label>19</label><mixed-citation publication-type="other" xlink:type="simple">Martínez-Alva, G., Gheno-Heredia, Y. A., Vieyra-Reyes, P., Martínez-Campos, A. R., Castillo-Cadena, J., López-Arriaga, J. A., Manzur-Quiroga, M. A., &amp; Arteaga-Reyes, T. T. (2020). Geodisponibilidad de elementos potencialmente tóxicos en suelos agrícolas que representan riesgo para el ambiente y la salud de la población del Nevado de Toluca. México. Revista Internacional de Contaminacion Ambiental, 36, 847-856. https://doi.org/10.20937/RICA.53614</mixed-citation></ref><ref id="scirp.117110-ref20"><label>20</label><mixed-citation publication-type="other" xlink:type="simple">McDonald, A. M., Proenza, J. A., Zaccarini, F., Rudashevsky, N. S., Cabri, L. J., Stanley, C. J., Rudashevsky, V. N., Melgarejo, J. C., Lewis, J. F., Longo, F., &amp; Bakker, R. J. (2010). Garutiite, (Ni, Fe, Ir), a New Hexagonal Polymorph of Native Ni from Loma Peguera, Dominican Republic. European Journal of Mineralogy, 22, 293-304. https://doi.org/10.1127/0935-1221/2010/0022-2007</mixed-citation></ref><ref id="scirp.117110-ref21"><label>21</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Mesa-Pérez</surname><given-names> A.</given-names></name>,<name name-style="western"><surname> Díaz-Rizo</surname><given-names> O.</given-names></name>,<name name-style="western"><surname> Sánchez-Pérez</surname><given-names> J. M.</given-names></name>,<name name-style="western"><surname> Baqué</surname><given-names> D.</given-names></name>,<name name-style="western"><surname> &amp; Tavella</surname><given-names> M. </given-names></name>,<etal>et al</etal>. (<year>2015</year>)<article-title>. Bioacumulación de metales pesados en arroz cultivado bajo condiciones de contaminación en la subcuenca Mampostón</article-title><source> Revista Ciencias Técnicas Agropecuarias</source><volume> 24</volume>,<fpage> 25</fpage>-<lpage>30</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.117110-ref22"><label>22</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Pérez-Olvera</surname><given-names> M. A.</given-names></name>,<name name-style="western"><surname> García-Mateos</surname><given-names> R.</given-names></name>,<name name-style="western"><surname> Vázquez-Alarcón</surname><given-names> A.</given-names></name>,<name name-style="western"><surname> Colinas-León</surname><given-names> T.</given-names></name>,<name name-style="western"><surname> Pérez-Grajales</surname><given-names> M.</given-names></name>,<name name-style="western"><surname> &amp; Navarro-Garza</surname><given-names> H. </given-names></name>,<etal>et al</etal>. (<year>2008</year>)<article-title>. Concentración de Pb, Cd, Ni y Zn en Suelos contaminados y su transferencia a la pella de Brócoli</article-title><source> Terra Latinoamericana</source><volume> 26</volume>,<fpage> 215</fpage>-<lpage>225</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.117110-ref23"><label>23</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Prieto-Méndez</surname><given-names> J.</given-names></name>,<name name-style="western"><surname> González-Ramírez</surname><given-names> C. A.</given-names></name>,<name name-style="western"><surname> Román-Gutiérrez</surname><given-names> A. D.</given-names></name>,<name name-style="western"><surname> &amp; Prieto-García</surname><given-names> F. </given-names></name>,<etal>et al</etal>. (<year>2009</year>)<article-title>. Pollution and Phytotoxicity in Plants by Heavy Metals from Soils and Water</article-title><source> Tropical and Subtropical Agroecosystems</source><volume> 10</volume>,<fpage> 29</fpage>-<lpage>44</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.117110-ref24"><label>24</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Raju</surname><given-names> L. K.</given-names></name>,<name name-style="western"><surname> Vishnuvardhan</surname><given-names> V.</given-names></name>,<name name-style="western"><surname> Middepogu</surname><given-names> A. R.</given-names></name>,<name name-style="western"><surname> &amp; Damodhraram</surname><given-names> T. </given-names></name>,<etal>et al</etal>. (<year>2016</year>)<article-title>. Evaluation of Accumulated Heavy Metals in Soil and Plant Bodies of Oryza sativa L. and Triticumvulgare</article-title><source> Innoriginal International Journal of Sciences</source><volume> 3</volume>,<fpage> 13</fpage>-<lpage>17</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.117110-ref25"><label>25</label><mixed-citation publication-type="other" xlink:type="simple">Roca, M. &amp; Bayon, A. (1981). Determination of Copper in Geological Materials by X-Ray Fluorescence (JEN-491). Spain. http://inis.iaea.org/search/search.aspx?orig_q=RN:39036509</mixed-citation></ref><ref id="scirp.117110-ref26"><label>26</label><mixed-citation publication-type="other" xlink:type="simple">Romic, M., &amp; Romic, D. (2003). Heavy Metals Distribution in Agricultural Topsoils in Urban Area. EnvironmentalGeology, 43, 795-805. https://doi.org/10.1007/s00254-002-0694-9</mixed-citation></ref><ref id="scirp.117110-ref27"><label>27</label><mixed-citation publication-type="other" xlink:type="simple">Rudnick, R. L., &amp; Gao, S. (2003). Composition of the Continental Crust. Treatise on Geochemistry, 3, 1-64. https://doi.org/10.1016/B0-08-043751-6/03016-4</mixed-citation></ref><ref id="scirp.117110-ref28"><label>28</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Shahbaz</surname><given-names> A.</given-names></name>,<name name-style="western"><surname> Iqbal</surname><given-names> M.</given-names></name>,<name name-style="western"><surname> Jabbar</surname><given-names> A.</given-names></name>,<name name-style="western"><surname> Hussain</surname><given-names> S.</given-names></name>,<name name-style="western"><surname> &amp; Ibrahim</surname><given-names> M. </given-names></name>,<etal>et al</etal>. (<year>2018</year>)<article-title>. Assessment of Nickel Bioavailability through Chemical Extractants and Red Clover (Trifoliumpratense L.) in an Amended Soil: Related Changes in Various Parameters of Red Clover</article-title><source> Ecotoxicology and Environmental Safety</source><volume> 149</volume>,<fpage> 116</fpage>-<lpage>127</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.117110-ref29"><label>29</label><mixed-citation publication-type="other" xlink:type="simple">Turner, A. &amp; Lewis, M. (2018). Lead and Other Heavy Metals in Soils Impacted by Exterior Legacy Paint in Residential Areas of South West England. Science of the Total Environment, 619, 1206-1213. https://doi.org/10.1016/j.scitotenv.2017.11.041https://www.sciencedirect.com/science/article/pii/S0048969717330991</mixed-citation></ref><ref id="scirp.117110-ref30"><label>30</label><mixed-citation publication-type="other" xlink:type="simple">Vinodhini, R. &amp; Narayanan, M. (2008). Bioaccumulation of Heavy Metals in Organs of Fresh Water Fish Cyprinus carpio (Common Carp). International Journal of Environmental Science and Technology, 5, 179-182. https://doi.org/10.1007/BF03326011</mixed-citation></ref><ref id="scirp.117110-ref31"><label>31</label><mixed-citation publication-type="other" xlink:type="simple">Vyzmalová, A., Laufer, F., Drábek, M., Stanley, C., Bakker, R. J., Bermejo, R., Garuti, G., Thalhammer, O., Proenza, J. A., &amp; Longo, F. (2012). Zaccariniite, RhNiAs, a New Platinum-Group Mineral Species from Loma Peguera, Dominican Republic. Canadian Mineralogist, 50, 1321-1329. https://doi.org/10.3749/canmin.50.5.1321</mixed-citation></ref><ref id="scirp.117110-ref32"><label>32</label><mixed-citation publication-type="other" xlink:type="simple">Xuan, T., Nguyen, T., Amyot, M., &amp; Labrecque, M. (2017). Differential Effects of Plant Root Systems on Nickel, Copper and Silver Bioavailability in Contaminated Soil. Chemosphere, 168, 131-138. https://doi.org/10.1016/j.chemosphere.2016.10.047</mixed-citation></ref></ref-list></back></article>