<?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">JACEN</journal-id><journal-title-group><journal-title>Journal of Agricultural Chemistry and Environment</journal-title></journal-title-group><issn pub-type="epub">2325-7458</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/jacen.2022.113013</article-id><article-id pub-id-type="publisher-id">JACEN-119129</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> Earth&amp;Environmental Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Typology of Crop Residues and Energy Recovery in Heavily Agricultural Areas: Case of the Departments of Soubr&#233;, Daloa, Issia and Sassandra (C&amp;ocirc;te d’Ivoire)
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Amenan</surname><given-names>Anne Mary Kouassi-Kouadio</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>Pétémanagnan</surname><given-names>Jean-Marie Ouattara</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>Talnan</surname><given-names>Jean Honoré Coulibaly</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>Franck</surname><given-names>Michaël Zahui</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>Lacina</surname><given-names>Coulibaly</given-names></name><xref ref-type="aff" rid="aff4"><sup>4</sup></xref></contrib></contrib-group><aff id="aff4"><addr-line>University of Man, Man, C&amp;amp;ocirc;te d’Ivoire</addr-line></aff><aff id="aff2"><addr-line>Laboratoire Géosciences et Environnement, Université Nangui Abrogoua, Abidjan, C&amp;amp;ocirc;te d’Ivoire</addr-line></aff><aff id="aff1"><addr-line>Laboratory of Environment and Aquatic Biology, Department of Sciences and Environment Management, NANGUI ABROGOUA University, Abidjan, C&amp;amp;ocirc;te d’Ivoire</addr-line></aff><aff id="aff3"><addr-line>Department of Agronomic, Forestry and Environmental Engineering, University of Man, Man, C&amp;amp;ocirc;te d’Ivoire</addr-line></aff><pub-date pub-type="epub"><day>05</day><month>07</month><year>2022</year></pub-date><volume>11</volume><issue>03</issue><fpage>196</fpage><lpage>208</lpage><history><date date-type="received"><day>2,</day>	<month>June</month>	<year>2022</year></date><date date-type="rev-recd"><day>9,</day>	<month>August</month>	<year>2022</year>	</date><date date-type="accepted"><day>12,</day>	<month>August</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>
 
 
  The valorization of crop residues could constitute an energy source (biogas) allowing to reduce the energy needs of populations in agricultural regions, improve their living conditions and slow down deforestation as well as greenhouse gas emissions. This work aims to determine the typology of agricultural waste in the departments of Soubr&#233;, Sassandra, Daloa and Issia, to determine the number of residues generated in these departments, and to assess the biogas potential of these departments said residues. Field observations were made to identify the different types of waste, then, based on agricultural statistical data from the Ministry of Agriculture and biogas productivity indexes, the quantities of agricultural residues and biogas were estimated. Agricultural residues consist of pods (50%), stalks (19%), cobs (3%), Straws (8%), stalks (2%), shells (9%), fibers (7%), husks (1%), and bunches (1%). In addition, these localities have 465266.3 t of pods, 173583.2 t of stalks, 84280.0 t of shells, 75,857 t of straws, 12,000 t of husks, 10,987 t of bunches and 6793.0 t of fibers. The departments of Soubr&#233;, Sassandra, Daloa and Issia contain a total potential energy of 235.87 &#215; 10
  <sup>6</sup> m
  <sup>3</sup> of biogas. However, this is unevenly distributed among the localities. The volume of biogas recorded is higher in the department of Soubr&#233; (74.91 &#215; 10
  <sup>6</sup> m
  <sup>3</sup>) which is followed respectively by the departments of Daloa (62.27 &#215; 10
  <sup>6</sup> m
  <sup>3</sup>), Issia (52.77 &#215; 10
  <sup>6</sup> m
  <sup>3</sup> and Sassandra (45.93 &#215; 10
  <sup>6</sup> m
  <sup>3</sup>). The departments of Soubr&#233;, Sassandra, Daloa and Issia have a very large potential for the production of agricultural residues that may be of interest to economic operators for recovery in biogas production units.
 
</p></abstract><kwd-group><kwd>Agriculture</kwd><kwd> Crop Residues</kwd><kwd> Biogas</kwd><kwd> Sassandra</kwd><kwd> Daloa</kwd><kwd> Issia</kwd><kwd> Soubr&#233;</kwd><kwd> C&amp;ocirc;te d’Ivoire</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Since its independence, C&#244;te d’Ivoire has focused its economic development on the agricultural sector, creating more than 47% of national added [<xref ref-type="bibr" rid="scirp.119129-ref1">1</xref>] . Annual productions are 1,300,000 tons of cocoa, 120,000 tons of coffee [<xref ref-type="bibr" rid="scirp.119129-ref2">2</xref>] . 131,000 tons of cotton, 300,000 tons of oil palm and 630,000 tons of cashew [<xref ref-type="bibr" rid="scirp.119129-ref3">3</xref>] . These farming activities generate large quantities of waste composed mainly of organic residues, of which the mismanagement constitutes a proven source of pollution of the components of the environment [<xref ref-type="bibr" rid="scirp.119129-ref4">4</xref>] . A study carried out on the method of managing agropastoral waste in the Sassandra watershed revealed that this waste was mostly incinerated in the open air or used to meet the energy needs of the populations [<xref ref-type="bibr" rid="scirp.119129-ref5">5</xref>] . However, incineration could lead to bush fires that would devastate surrounding plantations, plant cover as well as biodiversity. In addition, the smoke emitted would cause respiratory problems to populations. Thus, controlling the management of crop waste could constitute a major issue that would be part of an overall strategy to reduce environmental impacts. In addition, this waste could constitute a source of wealth for rural populations (waste producers) and a mine of raw materials for economic operators [<xref ref-type="bibr" rid="scirp.119129-ref6">6</xref>] . The departments of Soubr&#233;, Sassandra, Daloa and Issia constitute one of the main agricultural areas of the country [<xref ref-type="bibr" rid="scirp.119129-ref7">7</xref>] . These departments are teeming with several crops of cash crops (cocoa, coffee, oil palm and rubber) and food crops (rice, maize, cassava) [<xref ref-type="bibr" rid="scirp.119129-ref2">2</xref>] which could generate huge quantities of residues. This study aims to characterize the typology of crop residues, to assess their availability, and to quantify the volume of biogas likely to be produced in the different localities.</p></sec><sec id="s2"><title>2. Materials and Methods</title><sec id="s2_1"><title>2.1. Study Area</title><p><xref ref-type="fig" rid="fig1">Figure 1</xref> presents the areas surveyed in this study. These areas belong to the southern agricultural watershed basin of Sassandra, particularly in the center-west (Daloa and Issia) and south-west (Soubr&#233; and Sassandra) of C&#244;te d’Ivoire. The departments of Daloa and Issia are located between longitudes 5˚75 and 8˚16 West and latitudes 5˚56 and 9˚75 North [<xref ref-type="bibr" rid="scirp.119129-ref8">8</xref>] . The respective populations of these localities are 591.693 inhabitants (Daloa) for an area of 38.76 km<sup>2</sup> and 327.901 inhabitants (Issia) for an area of 5.658 km<sup>2</sup>. As for the Sassandra and Soubr&#233; departments, they are located between longitude 7˚08 and 6˚12 West and latitude</p><p>5˚19 and 6˚34 north. Sassandra covers an area of 25.800 km<sup>2</sup> with an estimated population of 299.500 inhabitants [<xref ref-type="bibr" rid="scirp.119129-ref9">9</xref>] . On the other hand, Soubr&#233; has 464.554 inhabitants for an area of 8.500 km<sup>2</sup>. The economic activities carried on these different localities are: agriculture, trade and transport. However, agriculture remains the main economic activity, practiced by 60% of the population [<xref ref-type="bibr" rid="scirp.119129-ref9">9</xref>] . Agricultural dynamic is essentially based on cash crops (coffee, cocoa, rubber and oil palm) and food and market gardening crops.</p></sec><sec id="s2_2"><title>2.2. Material</title><p>The equipment used for the preparation of this study is composed of a cameras for taking pictures of the various types of crop wastes, agricultural statistical data 2015 provided by the Department of Statistics, Documentation and Information Technology of the Ministry of agriculture of C&#244;te d’Ivoire. The quantities of agricultural residues generated as well as the equivalent volume of biogas for each type of residues were estimated using productivity indexes [<xref ref-type="bibr" rid="scirp.119129-ref10">10</xref>] .</p></sec><sec id="s2_3"><title>2.3. Method</title><sec id="s2_3_1"><title>2.3.1. Wastes Identification</title><p>To identify crop wastes produced in the departments of Soubr&#233;, Sassandra, Daloa and Issia, different farms were visited. The types of wastes identified were photographed.</p></sec><sec id="s2_3_2"><title>2.3.2. Estimation of the Quantities of Crop Wastes</title><p>The quantities of residues (QR) from the crops were determined from the relation (1) described according to [<xref ref-type="bibr" rid="scirp.119129-ref10">10</xref>]</p><p>QR = m &#215; Cres (1)</p><p>where:</p><p>m: Mass of the production for the considered crop (kg),</p><p>Cres: Coefficient relating to the quantity of residues generated according to agricultural production.</p></sec><sec id="s2_3_3"><title>2.3.3. Quantities of Biogas Estimation</title><p>The potential of annual biogas production from agricultural residues was estimated from the quantity of dry matter (QMS) of said residues. This quantity of dry matter was calculated according to the relation (2):</p><p>QMS = m &#215; Cres &#215; Cms (2)</p><p>The potential of agricultural residues biogas (PAg) was evaluated according to the Equation (3).</p><p>PAg = QMS &#215; Ip (3)</p><p>where:</p><p>Cms: Proportion of dry matter contained in the residue,</p><p>Ip: Productivity index.</p><p>The values of Cms, Cres and Ip used are consigned in <xref ref-type="table" rid="table1">Table 1</xref>.</p></sec></sec></sec><sec id="s3"><title>3. Results and Discussion</title><sec id="s3_1"><title>3.1. Typology of Crop Residues</title><p>Crops residues are made up of bunches, fibers, shells, pods, straws, husks, cobs,</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Cms, Cres and Ip values [<xref ref-type="bibr" rid="scirp.119129-ref10">10</xref>] [<xref ref-type="bibr" rid="scirp.119129-ref11">11</xref>] </title></caption><table><tbody><thead><tr><th align="center" valign="middle"  colspan="2"   rowspan="2"  >Wastes typology by culture</th><th align="center" valign="middle"  colspan="3"  >Values and references</th></tr></thead><tr><td align="center" valign="middle" >[<xref ref-type="bibr" rid="scirp.119129-ref10">10</xref>]</td><td align="center" valign="middle" >[<xref ref-type="bibr" rid="scirp.119129-ref10">10</xref>]</td><td align="center" valign="middle" >[<xref ref-type="bibr" rid="scirp.119129-ref11">11</xref>]</td></tr><tr><td align="center" valign="middle" >Cultures</td><td align="center" valign="middle" >Wastes</td><td align="center" valign="middle" >Cres</td><td align="center" valign="middle" >Cms</td><td align="center" valign="middle" >Ip (m<sup>3</sup>/t of MS)</td></tr><tr><td align="center" valign="middle"  rowspan="2"  >Rice</td><td align="center" valign="middle" >Straw</td><td align="center" valign="middle" >1.757</td><td align="center" valign="middle" >0.87</td><td align="center" valign="middle" >360</td></tr><tr><td align="center" valign="middle" >Husk</td><td align="center" valign="middle" >0.267</td><td align="center" valign="middle" >0.98</td><td align="center" valign="middle" >300</td></tr><tr><td align="center" valign="middle"  rowspan="3"  >Maize</td><td align="center" valign="middle" >Stalk</td><td align="center" valign="middle" >0.20</td><td align="center" valign="middle" >0.89</td><td align="center" valign="middle" >300</td></tr><tr><td align="center" valign="middle" >Cob</td><td align="center" valign="middle" >0.273</td><td align="center" valign="middle" >0.93</td><td align="center" valign="middle" >300</td></tr><tr><td align="center" valign="middle" >Stem</td><td align="center" valign="middle" >2.00</td><td align="center" valign="middle" >0.85</td><td align="center" valign="middle" >295</td></tr><tr><td align="center" valign="middle"  rowspan="3"  >Palm oil</td><td align="center" valign="middle" >Cluster</td><td align="center" valign="middle" >0.23</td><td align="center" valign="middle" >0.50</td><td align="center" valign="middle" >300</td></tr><tr><td align="center" valign="middle" >Fibre</td><td align="center" valign="middle" >0.14</td><td align="center" valign="middle" >0.60</td><td align="center" valign="middle" >300</td></tr><tr><td align="center" valign="middle" >Shell</td><td align="center" valign="middle" >0.065</td><td align="center" valign="middle" >0.90</td><td align="center" valign="middle" >300</td></tr><tr><td align="center" valign="middle" >Cocoa</td><td align="center" valign="middle" >Pods</td><td align="center" valign="middle" >1.00</td><td align="center" valign="middle" >0.85</td><td align="center" valign="middle" >300</td></tr><tr><td align="center" valign="middle" >Coffee</td><td align="center" valign="middle" >Shell</td><td align="center" valign="middle" >2.10</td><td align="center" valign="middle" >0.85</td><td align="center" valign="middle" >300</td></tr><tr><td align="center" valign="middle" >Cassava</td><td align="center" valign="middle" >Stem</td><td align="center" valign="middle" >0.062</td><td align="center" valign="middle" >0.85</td><td align="center" valign="middle" >300</td></tr></tbody></table></table-wrap><p>stalks and stems. These wastes come from cocoa (pod), coffee (shell), oil palm (cluster, fiber, shell, straw), manioc (stem), maize (cobs, stem, stalk) and rice (straw, husk, stem) <xref ref-type="fig" rid="fig2">Figure 2</xref>. This typology of wastes is similar to that obtained by Coulibaly et al. [<xref ref-type="bibr" rid="scirp.119129-ref12">12</xref>] in the Como&#233; watershed.</p></sec><sec id="s3_2"><title>3.2. Quantities of Crops</title>Quantities of Crop Residues Available<p>The quantities of agricultural wastes available by locality of the BVS are presented in <xref ref-type="fig" rid="fig3">Figure 3</xref>. These wastes come from cash crops such as cocoa, coffee and oil palm and from food crops such as rice, manioc and maize. We note that the quantities of wastes vary between 190 and 291 thousand tons. However, the quantity of food crop waste is greater in the department of Daloa (217.5 t). As for the residues from cash crops, they are more important in Soubr&#233; (276.5 t) followed respectively by these of Issia (176.2 t), and Sassandra (157.2 t). The aggregate production of agricultural residues of the entire southern BVS, amounts to 930,221 t. Overall, the department of soubr&#233; is full of more than (290,668 t) waste followed respectively by the departments of Daloa (236,123 t), Issia (205,061 t) and Sassandra (198,221 t). This result could be linked to the surfaces of the differentes localities. Indeed, the surface of the differentes localities would make vast cultivated lands available to the populations. In addition, the declassification of certain reserves in the department of Soubr&#233; would have favoured greater agricultural production. This corroborates the results of the report of the CCC coffee and cacao [<xref ref-type="bibr" rid="scirp.119129-ref2">2</xref>] which indicates that cocoa production in Soubr&#233; represents 19% of the national production.</p><p><xref ref-type="fig" rid="fig4">Figure 4</xref> shows the quantities of residues generated according to the type of crop considered. Regarding cash crops, the quantity of residues from cocoa cultivation is higher at soubr&#233; (272,265 t) and Issia (132,244 t). As for the residues from coffee, the highest quantities are recorded in the departments of Sassandra (34,497 t) and Issia (41,538 t). Residues from oil palm are recorded in the department of Sassandra (78,094 t). As for residues from food crops, they are present in almost all localities; the maize cultivation generates more residues with a tonnage of 212,200 t, then that of rice with a production of residues of 87384.8 t and finally these of cassava, with a production of residues 1732.7 t. By</p><p>considering the residues by type of crop, we note that the residues resulting from the highest cultivation activities come from the cultivation of cocoa for cash crops and maize for food crops. The high production of pod residues is said would be due to the high production of cocoa in the agricultural watershed of Sassandra and also to the agricultural policy of the C&#244;te d’Ivoire which encourages the practice of this crop. In addition, the south Sassandra is an agro-ecological area favorable to cocoa and corn crops [<xref ref-type="bibr" rid="scirp.119129-ref13">13</xref>] .</p><p><xref ref-type="fig" rid="fig5">Figure 5</xref> shows the quantities of residues available by locality. Pods are available in large quantities (272295.6 t) in Soubr&#233; and Issia (132.2 t). As for stems (145058.29 t) and straws (33.4 t), they are more available in Daloa than in the other towns. However, shells (41900.44 t) and fibers are more important in Sassandra. The results concerning the quantities of crop residues by locality, showed that the area of Soubr&#233; has the highest production of cocoa residues. This would explain the high production of pods (272,265 t) in this locality. This result is of the same order as the results of the CCC [<xref ref-type="bibr" rid="scirp.119129-ref2">2</xref>] . This production of waste from cocoa would also present some possible ways for recovery for composting and/or biogas production [<xref ref-type="bibr" rid="scirp.119129-ref14">14</xref>] . This city could be considered as a waste warehouse where recovery units can be installed. Relatively, the low production of clusters from oil palm cultivation in the watershed would be due to the fact that it is only in the Sassandra area that palm plantations have been recorded. In addition, we note in this locality the presence of a palm oil processing unit. The husks produced during rice husking are estimated at between 15% and 20% of</p><p>the total weight of the paddy. The work of Kumar et al. [<xref ref-type="bibr" rid="scirp.119129-ref15">15</xref>] showed daring rice hulling could be used for the production of bio-charcoal [<xref ref-type="bibr" rid="scirp.119129-ref16">16</xref>] . Rice hulls have made it possible to reduce the use of firewood, by limiting the pressure on the forest, thus slowing deforestation and, in turn, greenhouse gas emissions [<xref ref-type="bibr" rid="scirp.119129-ref17">17</xref>] [<xref ref-type="bibr" rid="scirp.119129-ref18">18</xref>] .</p></sec><sec id="s3_3"><title>3.3. Volume of Biogas Estimated</title><sec id="s3_3_1"><title>3.3.1. Volume of Biogas Estimated from Food Crops</title><p><xref ref-type="fig" rid="fig6">Figure 6</xref> shows the variations in the volume of biogas resulting from the residues of the various food crops grown in the departments of Soubr&#233;, Sassandra, Daloa and Issia. In general, we note a strong contribution of residues from rice and maize crops (99%) in gas production in the departments. The maximum volume of biogas is obtained at Daloa (58.2 &#215; 10<sup>6</sup> m<sup>3</sup>) while the minimum volume was recorded at Soubr&#233; (4 &#215; 10<sup>6</sup> m<sup>3</sup>). With the exception of Daloa where the contribution of maize residues in the total production of biogas is greater (66%), in the other localities, this production is dominated by the contribution of rice residues. The contribution of residues generated by cassava cultivation is negligible in all localities. However, this contribution is very low (1%). Regarding the biogas potential from food crops, rice and corn residues are the most used (99%) in gas production in the departments. This result is similar to that of [<xref ref-type="bibr" rid="scirp.119129-ref19">19</xref>] [<xref ref-type="bibr" rid="scirp.119129-ref20">20</xref>] who showed that in Germany the highest biogas potential is obtained by residues from the cultivation of maize. The total volume of biogas estimated from the residues of rice and maize is 81.27 &#215; 10<sup>6</sup> m<sup>3</sup>.</p></sec><sec id="s3_3_2"><title>3.3.2. Volume of Biogas Estimated from Cash Crops</title><p><xref ref-type="fig" rid="fig7">Figure 7</xref> shows the variation in the volume of biogas resulting from the residues of each type of cash crop cultivated in the departments of Soubr&#233;, Sassandra, Daloa and Issia. It is found that the biogas potential of cash crops is dominated by residues from coffee and cocoa crops. In Issia and Soubr&#233;, this potential is dominated by cocoa residues while in Sassandra, it is mainly due to oil palm residues. The biogas potential obtained from coffee residues is recorded in the localities of Sassandra and Issia. The volume of biogas recorded in the localities is higher in the department of Soubr&#233; (70.5 &#215; 10<sup>6</sup> m<sup>3</sup>) which is followed respectively by the departments of Issia (44.7 &#215; 10<sup>6</sup> m<sup>3</sup>), Sassandra (34 &#215; 10<sup>6</sup> m<sup>3</sup>) and Daloa (4 &#215; 10<sup>6</sup> m<sup>3</sup>). For cash crops, the biogas potential relies mainly on coffee and cocoa crops. This result would be linked to the high production of these types of residues. The maximum estimated biogas production in the departments of Soubr&#233;, Sassandra, Daloa and Issia would therefore be influenced by a significant contribution from cash crop residues, especially coffee and cocoa.</p></sec><sec id="s3_3_3"><title>3.3.3. Volume of Biogas Estimated from All Crop Residues</title><p><xref ref-type="fig" rid="fig8">Figure 8</xref> shows the variation in the potential volume of biogas estimated from all agricultural residues of WS. A high proportion of biogas resulting from cash crop waste (74% - 94%) is observed in the towns of Issia, Sassandra and Soubr&#233;. However, in Daloa, the trend is reversed. In this locality, the contribution of residues generated by food crops dominates the production of biogas (93%). the results obtained show the importance of agricultural residues as a substrate for</p><p>biogas production [<xref ref-type="bibr" rid="scirp.119129-ref21">21</xref>] . The absence of a biogas production unit in the departments of Soubr&#233;, Sassandra, Daloa and Issia while the potential in organic substrates for the production of this type of energy in the said departments is enormous, could be explained by the absence of a policy of popularization and dissemination of biogas production unit in rural areas as well as in Nepal, China and India [<xref ref-type="bibr" rid="scirp.119129-ref22">22</xref>] . This situation could help guide technological choices and the methodology for installing biogas units to recover this waste. In the departments of Soubr&#233;, Sassandra, Daloa and Issia, the exploitation of this substrate in rural areas could be done in small biogas units to partially meet the domestic energy needs of rural areas. However, it will be necessary to take into account the cost of transporting said waste in order to properly assess the economic profitability of production [<xref ref-type="bibr" rid="scirp.119129-ref23">23</xref>] . This approach has been used successfully in Nepal, China and India [<xref ref-type="bibr" rid="scirp.119129-ref22">22</xref>] . The results obtained show that agricultural waste contained a large volume of biogas, the implementation of which would slow down deforestation and greenhouse gas emissions. However, the recovery of the mentioned waste into biogas is a relatively complex technology which requires grinding before digestion. In addition, the use of people equipped in the field is necessary.</p></sec></sec></sec><sec id="s4"><title>4. Conclusion</title><p>At the end of this study, it emerges that in the departments of Soubr&#233;, Daloa, Issia and Sassandra, there are several types of crop waste, namely: straw, clusters, stems, ears, stalks, shell, pods, husk and fibers. The estimated quantities for perennial crop residues are 465266.3 t for cocoa, 82022.7 t for oil palm ones, and 81175.0 t for coffee ones. As for food crop residues, they are 212493.9 t for maize, 212493.9 t for rice and 1732.7 t for casava. Agricultural wastes are unevenly distributed between the localities of the watershed. Overall, the department of soubr&#233; is full of more waste (290,668 t) followed respectively by the departments of Daloa (236,123 t), Issia (205,061 t) and Sassandra (198,221 t). Regarding biogas potential, the volume of biogas recorded is higher in the department of Soubr&#233; (74.91 &#215; 10<sup>6</sup> m<sup>3</sup>) which is followed respectively by the departments of Daloa (62.27 &#215; 10<sup>6</sup> m<sup>3</sup>), Issia (52.77 &#215; 10<sup>6</sup> m<sup>3</sup>) and Sassandra (45.93 &#215; 10<sup>6</sup> m<sup>3</sup>). The biogas deposit of crop residues can provide a significant amount of energy. Harnessing this energy source would save large areas of forest and alleviate the suffering of women in search of biomass.</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>Kouassi-Kouadio, A.A.M., Ouattara, P.J.-M., Coulibaly, T.J.H., Zahui, F.M. and Coulibaly, L. (2022) Typology of Crop Residues and Energy Recovery in Heavily Agricultural Areas: Case of the Departments of Soubr&#233;, Daloa, Issia and Sassandra (C&#244;te d’Ivoire). Journal of Agricultural Chemistry and Environment, 11, 196-208. https://doi.org/10.4236/jacen.2022.113013</p></sec></body><back><ref-list><title>References</title><ref id="scirp.119129-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Esso, L.J. and Yeo, N. (2014) Transformations structurelles et développement sectoriel en C&amp;ocirc;te d’Ivoire. 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