Research Article | | Peer-Reviewed

Characteristics and Suitability of Mayo-Lemie Soils for Corn Production

Received: 16 September 2025     Accepted: 21 November 2025     Published: 17 December 2025
Views:       Downloads:
Abstract

A study conducted in the Mayo-Lemié region of southwestern Chad aimed to determine the physicochemical characteristics and suitability of a soil for maize cultivation. A soil profile was established and described in the field, and soil samples were then collected from the different horizons. These samples were oven-dried for two weeks, crushed, labeled, and sent to the laboratory for routine analysis. The results of the analyses showed that all the samples analyzed ranged from slightly acidic to acidic with pH between 5.1 and 6.5; similarly, all exchangeable cations were poorly represented. The sum of exchangeable cation decreases with depth, as do the values of other nutrients. The results of the laboratory analyses were compared white the climatic data of the study area for evaluation according to the FAO. The climate assessment shows that the climate is very suitable for maize cultivation with an adjusted climate index of 88.03. It also appears from this study that the land unit concerned is marginally suitable for maize production with a parametric value of 31.82. The sandy texture remains the main limitation. To improve the situation, crop rotation is necessary, stubble should be returned to the fields after harvest, and mineral and organic fertilizers should be applied to improve the physical and chemical characteristics of the soil in order to increase yields.

Published in Agriculture, Forestry and Fisheries (Volume 14, Issue 6)
DOI 10.11648/j.aff.20251406.12
Page(s) 232-239
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2025. Published by Science Publishing Group

Keywords

Cultivation Suitability, Corn, Texture, Fertilization

1. Introduction
Cultivation of soils leads to a rapid decline in soil fertility, while by 2030 the world population could increase by three billion people and food production will have to double . High rates of population growth, combined with widespread poverty and poor land use, are accelerating land degradation . The loss of arable land is a fundamental problem for the future of humanity . Declining soil fertility causes declines in agricultural production, which exacerbates food insecurity in sub-Saharan African countries . The physical and socio-economic characteristics of arid and semi-arid areas make them highly vulnerable to climate change and degradation; yet the soils of arid and semi-arid areas constitute a significant portion of land reserves and ecological resources for the future . To better control the conditions of production and exploitation of soils, it is necessary to know their aptitudes . The Sahel-Sudan region has already largely exceeded its carrying capacity based on traditional agricultural and livestock systems. Thus, when soils are degraded and no longer allow them to ensure functions such as agricultural production and water retention, users have no choice but to migrate to other more productive soils or to limit themselves to subsistence resources . Crises and food shortages can also lead to conflicts resulting in migration . The need to give priority to agricultural production remains essential because it is necessary to meet the growing needs of a constantly increasing population. The objective of this work is to seek to diversify crops by evaluating the suitability of soils for other more promising crops such as maize.
2. Methods and Materials
2.1. Study Area
The study area is located in South-Western Chad, in the middle of the sudano-Sahelian environment. It extends from 10°31' to 11°06' North and 15°00' to 16°30' East (Figure 1). The climate is characterized by a long dry season from October to May and a short rainy season, from June to September. The mean annual rainfall is about 652 mm and the average temperature is 28°C. The main activities of the population are agriculture and animal breeding. Sorghum is the main crop. The geological formations are fluviolacustrine or fluvial, deposited during the various transgressive or regressive phases of the Chad Lake, from the beginning of the Quaternary era to present. The dominant soils are sandy tropical ferruginous soils, poor in organic matter. The vegetation consists of a shrub savannah dominated by Acacias and Balanites, depending on the type of soil, with a grassy carpet made up of Andropogonea.
Figure 1. Location of the Study Area.
2.2. Methods
A soil profile was driven into a ferruginous soil. The profile was described according to ; the description concerned the thickness and limit of the horizons, the color, texture, structure, consistency, porosity, etc. A soil sample was taken from the middle of each horizon to be sent to the laboratory for physicochemical analyses. In addition, climatic data of about thirty years were taken to allow the climatic assessment.
Based on the information on the study site, soil suitability was determined for rainfed maize cultivation. The FAO approach for rainfed agriculture was used as described by Sys . Six suitability classes are used:
1. S1-0: Very high ability, no limitations;
2. S1-1: High ability, slight limitations;
3. S2: Average ability, moderate limitations;
4. S3: Marginal ability, severe limitations;
5. N1: Current inability, very severe but correctable limitations;
6. N2: Permanent inability, very severe limitations that cannot be corrected with the current level of knowledge.
To determine the suitability classes, the three methods for determining land suitability levels were used according to the FAO approach; these are obviously the lowest class method, the method of the number and degree of limitations and then the parametric method.
3. Results
3.1. Morphological Organization of the Profile
The profile named G1 has a thickness of approximately 260 cm. It is located at an altitude of approximately 313 m at 10°54'631'' N and 15°33'132'' E. It presents from top to bottom the succession of the following horizons (Figure 2):
0 - 19 cm. Reddish-yellow horizon (7.5YR7/8) when dry, sandy texture, very weakly expressed polyhedral structure; friable and fragile when dry and non-plastic when wet; presence of numerous roots and rootlets; significant biological porosity, very strong matrix porosity. The limit is progressive and regular;
19 - 124 cm. Red-colored horizon (10YR5/8) when dry. Sub-blunted polyhedral structure, sandy-clayey texture, friable when dry and non-plastic when wet. Presence of millimetric roots and rootlets, low biological porosity, high matrix porosity; the transition with the lower horizon is gradual and regular;
124 - 190 cm. Yellowish-red horizon (5YR, 5/8) when dry; weakly expressed polyhedral structure; sandy-clayey texture, friable when dry and non-plastic when wet. Presence of tiny roots; extremely low biological porosity; high matrix porosity; presence of ferruginous elements (about 5%) of millimetric size; progressive and regular limit;
190 - 200 cm. Yellowish-red horizon (7.5YR, 8/6) when dry; essentially sandy; particulate structure; absence of roots and rootlets.
Figure 2. Morphological Organization of the Profile.
3.2. Physicochemical Characterizations of the G1 Profile
The results of the physicochemical analyses of the soil samples in profile G1 are reported in Table 1; they clearly show that the sandy fraction is the most quantitatively important granulometric fraction followed by the clay fraction and then the silt fraction. Its contents vary from 72.5 to 88.00% with an average of 78.16% and a standard deviation of 5.68. In the first horizon (0-19 cm), a content of 84.5% is observed. Between 19-124 cm, the content decreases to 77.5%; it is 72.5% between 124 and 190 cm; it rises to reach a maximum value beyond 190 cm which represents the last horizon (88%). The clay fraction varies from 10.5 to 21.5% with an average of 16.66% and a standard deviation of 6.02. The increase in clay content is regular from top to bottom up to a depth of 190 cm (21.5%) before decreasing to 10% at the base of the profile. Silt varies from 2 to 6%; an average content of 5% and a standard deviation of 1.00 are obtained. In the four horizons of the profile, the contents are respectively 5%; 4%, 6% and 2%. Grain size analysis of all samples shows that textures vary from sandy to sandy-clayey. All soil samples analyzed were found to be acidic to weakly acidic with pH values ​​ranging from 5.1 to 6.5. Values are higher in the surface horizons and decrease with increasing depth. pHkcl ranges from 4.1 to 5.6 in all horizons. In each horizon, the pHkcl value is lower than the pHwater. The pH variation (ΔpH = pH KCL – pH H2O) is negative throughout the profile. All exchangeable cations are poorly represented. Calcium contents range from 1.32 to 2.64 meq/100g. The highest content is observed at the surface with an average of 2.09 meq/100g. The sodium content does not vary along the profile; it is 0.32 meq/100g. The sum of exchangeable bases varies slightly along the profile (2.64 to 4.32 meq/100g); an average of 3.79 meq/100g is obtained. Surface horizons have higher sums of exchangeable bases than deep horizons. Cation exchange capacities vary from 11.64 to 21.66; unlike some of the elements mentioned above, the highest value is observed from 19-124 cm depth. Magnesium contents range from 0.9 to 1.36 along the profile. Organic carbon contents range from 1.08 to 2.13%. The highest content is observed in the surface horizon. This value decreases progressively with depth. Nitrogen is found in very small quantities in all horizons of the profile. A decrease in its content is also observed with depth (0.37-0.22). The C/N ratio has values ranging from 4.67 to 6.06. The available phosphorus does not vary throughout the profile with a fixed value of 0.5 ppm.
Table 1. Physicochemical Characteristics of Profile G1.

Depth (cm)

0- 19

19-124

124-190

190-200

Min

Max

Average

Standard deviation

Texture (%)

Clay

10,5

18,5

21,5

10,00

10,5

21,5

16,66

6,028

Total silt

5,0

4,0

6,0

02,00

2,0

6,00

5,00

1,000

Sand

84,5

77,5

72,5

88,00

72,5

88,0

80,62

5,686

Textural class

S

SA

SA

S

Organic carbon (%)

2,13

2,00

1,45

1,08

1,08

2,13

1,80

0,361

Organic matter (%)

3,66

3,44

2,49

1,85

1,85

3,66

3,19

0,622

Total nitrogen (%)

0,37

0,33

0,31

0,22

0,22

0,37

0,30

0,078

C/N

5,75

6,06

4,67

4,90

4,67

6,06

6,13

0,425

pHH2O (1/2,5)

6,5

5,7

5,10

5,10

5,10

6,50

5,76

0,702

pHKCl (1/2,5)

5,6

4,4

4,10

4,20

4,10

5,60

4,70

0,794

P Bray II (ppm)

0,5

0,5

0,50

0,50

0,50

0,50

0,50

0,00

Exchangeable bases (meq/100 g of soil)

K+

0,31

0,30

0,12

0,01

0,01

0,31

2,43

0,107

Na+

0,32

0,32

0,32

0,32

0,32

0,32

0,32

0,00

Ca++

2,64

2,00

1,64

1,32

1,32

2,64

2,09

0,506

Mg++

1,04

1,08

1,36

0,90

0,90

1,36

1,16

0,174

Sum of exchangeable bases

4,32

3,62

3,44

2,64

2,64

4,32

3,79

0,960

Base saturation

37,11

16,71

25,59

20,88

16,74

37,11

25,07

0,465

CEC7 (meq/100g of soil)

11,64

21,66

13,44

12,64

11,64

21,66

15,58

5,342

CEC (meq/100g of clay)

110,85

117,08

159,97

126,4

117,1

159,9

138,5

21,88

EC (ms/cm)

0,016

0,01

0,01

0,02

0,01

0,02

0,015

0,004

ESP (%)

2,71

1,47

2,38

2,53

1,47

2,71

2,09

0,00

3.3. Evaluation of Cultivation Suitability
3.3.1. Climatic Evaluation of Maize
The climate assessment of maize cultivation shown in Table 2 shows that the climate is very suitable for maize cultivation with an adjusted climate index of 88.03. This value is obtained thanks to the various parameters which are generally favorable for maize cultivation. The rainfall during the growth cycle being 677 mm occupies the S1 class. It does not represent a limitation. The obtained parameter value is 98.7. The precipitation collected in the first month of the growth cycle and that received in the third month of the cycle have very high values and are therefore not constraints for corn production. The average temperature during the growth cycle gives the smallest parameter value in the table, but the minimum temperatures give an acceptable parameter value (94.75). Relative humidity and other parameters have very high parameter values. The calculated climate index (Table 2) is 88.03; the climate is therefore very suitable for growing maize.
Table 2. Climate Assessment of Corn.

Features

Values

Classes

Limitations

Parametric values

Groupe I: Precipitation

Growth cycle precipitation (mm)

677

S1-1

0

98,7

1st month precipitation of the growth cycle (mm)

127

S1

0

99,8

3rd month precipitation of the growth cycle (mm)

221,6

S1-1

1

94

Groupe II: Temperature

Average temperature of the growth cycle (°C)

27,5

S1

1

87,5

Minimum temperature during the growth cycle (°C)

21,9

S1-0

1

94,75

Relative humidity during the 2nd month

78

S1-1

1

98,8

Relative humidity of the 4th month (%)

61

S1-1

1

89,4

n/N of the cycle during the cycle

0,68

S1

0

100

Calculated Parameter Value (CR)

S1

88,03

3.3.2. Determination of the Suitability of Soil G1 for Growing Maize
The pedoclimatic assessment of profile G1 for maize cultivation is reported in Table 3. It appears from this table that soil G1 is marginally suitable for maize cultivation. The soil index gives a parametric value of 31.82. The class corresponding to this parametric value is S3.s. From the table summarizing the assessment made (Table 3), it appears that the texture and structure constitute moderate limitations (parametric value 40, class S3). Base saturation is a parameter that constitutes a slight limitation (class S2, parameter value 67.29). Apart from the two parameters that constitute limitations, the other parameters are optimal for corn cultivation.
Table 3. Determination of the Suitability of G1 Soil for Growing Corn.

Features

Values

Classes

Limitations

Parametric values

Topography (t)

Slope (%)

1

S1-1

0

95

Humidity (w)

Flood

zero

S1-0

0

100

Drainage

Good

S1-0

0

100

Physical characteristics of the soil (s)

Texture/structure

S

S3

3

40

Soil depth (cm)

> 90

S1-0

0

100

Rough fragment (0-1 m) (%)

-

S1-0

0

100

CaCO3 (%)

0

S1-0

0

100

Gypse (%)

0

S1-0

0

100

Soil fertility (f)

Apparent CEC of clay (meq /100 g of clay)

125,41

S1-0

0

100

Base saturation (%)

32,15

S2

2

67,29

Organic carbon (0-15 cm) (%)

2,20

S1-0

0

100

pH- H2O (0-15 cm)

6,3

S1-0

0

100

Salinity and sodicity (n)

ESP (%)

2,71

S1-0

0

100

Calculated Earth Index (Is)

S3.s

31,82

4. Discussion
All samples were characterized by low nutrient levels. The low OM levels observed during the analysis of soil samples could be due to the continuous cultivation of fields and the burning of crop residues as mentioned ; it could also be the result of rapid mineralization of biomass under the effect of climatic, chemical and physical factors of the soil . Indeed, the importance of organic matter lies in the fact that it releases adsorbed mineral elements and stores nutrients which constitute the source of food for plants. It also plays a physical role in the soil for cohesion, structure, porosity, retention or storage of water, etc. . It also plays a biological role in stimulating biological activity . Thus, it is a potential indicator of the sustainability of cropping systems since it plays an important role in many edaphic properties that partly determine plant production and soil and water conservation . The very low levels of nitrogen, phosphorus and other nutrients are explained by the low level of organic matter . In addition, the type of vegetation and the competition between agriculture and livestock farming accentuate the nutrient deficiency . Soil acidity is characteristic of ferruginous soils ; it is correlated with low base saturation as shown by the work of . pH and organic matter levels decrease with depth as listed by . The decrease in pH and CEC in deep horizons could be explained by the fact that calcium, which is leached or absorbed by plants, is gradually replaced by H+ ions at depth (Sébastien et al., 2008). This decreases in CEC at depth reveals the importance of organic matter in exchange properties. The pHKCl - pHH₂O difference is negative; this result shows the predominance of the negative charge in soils and demonstrates that these soils are well cultivable . The obtained clay CECs are very high (Table 2); These obtained values correspond to the 2:1 type mineral which are often found in low rainfall environments where leaching is not very advanced . The low potassium content can also be attributed to the sandy texture because a soil with low clay and silt content has a reduced capacity to retain potassium. Similarly, phosphorus deficiency in the soil is explained by the fact that its fixation on the clay-humic complex depends on the percentage of organic matter, the percentage of clay, pH and calcium . In semi-arid and sub-humid regions of Africa, phosphorus deficiency in soils is considered one of the major biophysical constraints to agricultural production . The soil is marginally suitable for growing maize; the soil index gives a parametric value of 31.82. This class corresponding to the parametric value is S3.s. Crops under plant cover, direct seeding, inputs of organic matter to the soil and agroecology can be used to improve the fertility of this soil . They have the advantage of increasing the quantity of organic matter and stopping soil erosion. For , monoculture is one of the causes of the decline in agricultural productivity; thus, for many authors, fallow land can be mentioned to compensate for the production which is only decreasing because they promote the production of OM which has the advantage of raising the level of soil fertility on the one hand and limiting its erosion on the other hand.
Abbreviations

FAO

Food And Agricultural Organization of the United Nations

CEC

Cation Exchange Capacity

Conflicts of Interest
The authors declare no conflicts of interest.
References
[1] Mulaji, K. C. (2011). Use of compost from household biowast to improve the fertility of acidic soils in the province of Kinshasa (Democratic Republic of Congo). Doctorat thesis, Liège -Gembloux Qgro-biotech, 220p.
[2] Gruhn, P., Goletti, F. and Yudelman, M. (2000). Integrated nutrient management, soil fertility, and sustainable agriculture: Current issues and future challenges." Food, Agriculture, and the Environment Discussion Paper No. 32, International Food Policy Research Institute, Washington, D. C. 3-31pp.
[3] Gilbey, B., Davies, J., Metternicht, G. and Magero, C. (2019). Taking land degradation neutrality from concept to practice: Early reflections on LDN target setting and planning’. Environmental Science and Policy 100: 230–237.
[4] Jayne, T. S., Mather, D. and Mghenyi, E. (2010). Principal Challenges Confronting Smallholder Agriculture in Sub-Saharan Africa, World Development, 38.1384-1398.
[5] Taylor, P. D. (2017). Fahrig L., Henin K. et Merriam G., Connectivity is a vital element of landscape structure, Oikos 68 (5) 571-572.
[6] Soltani, M. N. (2022). WSN for forest fire monitoring. Master thesis, université Badji Mokhtar-Annaba (Algérie). 60p.
[7] Lewis, P., Monem, M. A. and Kauskhik, P. (2018). Impact of climate change on farming systems and livelihood s in the near East and North Africa. Cairo. FAO. 9-36.
[8] Yerima B. P. K and Van Ranst E. (2005). Introduction to soil science: Soils of the tropics Trafford Publishing, 6E-2333 Government St, Victoria, BC Canada. 442p.
[9] Piéri, C. (1989). Fertility of savannah lands. Review of thirty years of agricultural research and development south of Sahara, Ministry of cooperation/CIRAD, Paris, pp. 213-224.
[10] FAO. (2019). The multiple roles of soil in the Near-East and Africa. Guidance document.
[11] Baize, D. (1995). Guide for soil description. National institute for Agricultural Research (INRA), Paris, France.
[12] Sys, C. (1985). Land evaluation. Part III. International Training Centre for Post Graduate Soil scientists, State University of Ghent. Belgium.
[13] Tsozue, D., Nghonda, J. P. and Mekem, D. L. (2015). Impact of land ´ management system on crop yields and soil fertility in Cameroon, Solid Earth Discussions, vol. 6, pp. 1087–1101.
[14] Nearing, MA., Kimoto, A., Nichols, M. H. and Ritchie, C. (2005). Spatial patterns of soil erosion and deposition in two small semiarid watersheds, Geophys. Res.
[15] Ballot, C. S. A., Mawussi, G., Atakpama, W., Moita, M., Nassy Yangakola T. M., Zinga, I., Silla, S., Kpérkouma, W., Dercon, G., Komlan, B. and Koffi A., (2016). Physicochemical characterization of soils for the purpose of improving cassava (Manihot esculenta) productivity in the Damara region of southeastern Central AFRICAN Republic. African agronomy 28(1) 9-24.
[16] Valery, A. and Pansu, M. (2022). Dynamics of soil organic matter, Proposed models and model-organism relationships. Soil management studies, 29, 169-184.
[17] Honvou, S. H. S., Aboh, A. B., Tèka, O., Sèwadé, C., Gandonou B. C., Oumorou, M., Sinsin, B. (2022). Use and modeling of land use dynamics of transhumant routes in the lower and the middle valley of the Ouémé (Benin). Sciences and Technologies for Sustainable Agriculture. 2(1), 18-29.
[18] Cayuela, M. L., Sinicco, T. and Mondini, C. (2009). Mineralization dynamics and bio?chemical properties during initial decomposition of plant and animal resi?dues in soil. Appl. Soil Ecol., 41, 118-127.
[19] Yerima, B. P. K., Wilding, L. P., Hallmark, C. T. and Calhoun, F. G. (1989). Statistical relationships among seleted properties of Northern Cameroon vertisols and associated alfisols. Soil Sci. Soc. Am. J. 53.
[20] Yemefack, M., Nounamo, L., Njomgang, R. and Bilong, P. (2004). Inluence of agricultural practices on clay content and other agronomic properties of a ferrallitic soil in the southern Cameroon. Tropicultura, 22(1) 3-10.
[21] Dongmo, A. L., Havard, M. and Dugué, P. (2007). Land and plant biomass management: the foundation for integrating agriculture and livestock farming in sedendary areas of northern Cameroon. Family farms in west and central Africa. Paris, France, p. 331-343.
[22] Abdou, M. R., Nazoumou, Y., Favreau, G. et Issoufou, O. B. (2022). Land occupation and dynamics and the rise of the water tablein the lower Dallol valley, Maouri European Scientific Journal, vol., 18 (14).
[23] Raunet M. (2003). Some morpho-pedological keys for Northern Cameroon for the use of agronomists. CIRAD, Montpellier, 24p.
[24] Traversa, A., Orazio, V. and Senesi N. (2008). Properties of dissolved organic matter in forest soils: Influence of different plant covering. Forest Ecology and Management, 256 p.
[25] Sébastien, C., David, K. and Pierre, L. (2008). Soil amendements or liming of meadows, 2008. Sheep and goat sector n°26- 4ème quarter 2008.
[26] Diatta, M. T. (2016). Clay raw materials from Senegal: Characteristics and applications to mass-produced ceramic products. Doctorat thesi, University of Limoges/France. 158p.
[27] Nguetnkam, J. P., Kamga, R., Villiéras, F., Ekodeck, G. E. and Yvon, J. (2008). Differential weathering of granite in tropical zones: example of two sequences studied in Cameroon (Central Africa). Geosciences report. 340, 451-461.
[28] Tsozué, D. and Yongue-Fouateu R. (2017). Tropical chemical weathering of a garnet rich micaschist in the rainforest zone of Cameroon. Eurasian J Soil Sci, 6 (1), 1-19.
[29] Tsozué, D. and Ndjigui, P. D. (2017). Geochemical Features of the Weathered Materials Developed on Gabbro in a Semi-Arid Zone, Northern Cameroon. Geosciences 7, 16: 1-17.
[30] Kouyate, A. B., Ibrahim, A., Serme, I. and Dembélé, S. G. (2020). Sorghum responses to the application of different forms of natural phosphaate from Tilemsi. Combined with soluble fertilizers in low-input production system in Mali. Int. J. Biol. Chem. Sci. 14 (9): 3285-3296.
[31] Aliou, B. K. and Serme, I. (2021). Evaluation of the effectiveness of natural phosphate (PNT) under different tillage practices in the sahelian zone of Mali. International Journal of Innovation and Applied Studies (34) 845-857.
[32] Issiné, A., Kao-mbassi, Y. K. J., Doloum, G., (2024). Physicochemical Characteristics and Soil Suitability for Semi-Irrigated Rice Cultivation in The Tandjile Province of Chad, Int. J. Appl. Sci. Biotechnol. Vol 12(4): 180-186.
[33] Erktan, A., Coq, S., Blanchart, E., Chevallier, T., Trap, J. Bernard, L., Nahmani, J., Hartmann, C., Hedde, M., Ganault, P., Barot, S. and Cortet, J. (2022). Biodiversity and physical structure of soils ; a spatial view of soil functioning- soil study and management, 153-167.
[34] Noble, A. D. (2004). Ruaysoongern S., Penning de Vries F. W. T., Hartmann C. et Webb M. J., Enhancing the agronomic productivity of degraded soils in Northeast Thailand through clay-based interventions. In: Water and Agriculture, eds., V. Seng, E. Craswel, S Fukai and K. Fischer. ACIAR proceedings, 116: 147-160.
[35] Issiné, A. (2023). Genêsis, classification and soil suitability ofMayo-Lemié in South-West Chad; Doctor of Philosophy thesis in Eatth Scince, 167p.
Cite This Article
  • APA Style

    Agoubli, I., Teguinet, B., Touroumgaye, G., Tombor, A. N. (2025). Characteristics and Suitability of Mayo-Lemie Soils for Corn Production. Agriculture, Forestry and Fisheries, 14(6), 232-239. https://doi.org/10.11648/j.aff.20251406.12

    Copy | Download

    ACS Style

    Agoubli, I.; Teguinet, B.; Touroumgaye, G.; Tombor, A. N. Characteristics and Suitability of Mayo-Lemie Soils for Corn Production. Agric. For. Fish. 2025, 14(6), 232-239. doi: 10.11648/j.aff.20251406.12

    Copy | Download

    AMA Style

    Agoubli I, Teguinet B, Touroumgaye G, Tombor AN. Characteristics and Suitability of Mayo-Lemie Soils for Corn Production. Agric For Fish. 2025;14(6):232-239. doi: 10.11648/j.aff.20251406.12

    Copy | Download

  • @article{10.11648/j.aff.20251406.12,
      author = {Issine Agoubli and Biaksoubo Teguinet and Goalbaye Touroumgaye and Allanaissem Ngonka Tombor},
      title = {Characteristics and Suitability of Mayo-Lemie Soils for Corn Production},
      journal = {Agriculture, Forestry and Fisheries},
      volume = {14},
      number = {6},
      pages = {232-239},
      doi = {10.11648/j.aff.20251406.12},
      url = {https://doi.org/10.11648/j.aff.20251406.12},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.aff.20251406.12},
      abstract = {A study conducted in the Mayo-Lemié region of southwestern Chad aimed to determine the physicochemical characteristics and suitability of a soil for maize cultivation. A soil profile was established and described in the field, and soil samples were then collected from the different horizons. These samples were oven-dried for two weeks, crushed, labeled, and sent to the laboratory for routine analysis. The results of the analyses showed that all the samples analyzed ranged from slightly acidic to acidic with pH between 5.1 and 6.5; similarly, all exchangeable cations were poorly represented. The sum of exchangeable cation decreases with depth, as do the values of other nutrients. The results of the laboratory analyses were compared white the climatic data of the study area for evaluation according to the FAO. The climate assessment shows that the climate is very suitable for maize cultivation with an adjusted climate index of 88.03. It also appears from this study that the land unit concerned is marginally suitable for maize production with a parametric value of 31.82. The sandy texture remains the main limitation. To improve the situation, crop rotation is necessary, stubble should be returned to the fields after harvest, and mineral and organic fertilizers should be applied to improve the physical and chemical characteristics of the soil in order to increase yields.},
     year = {2025}
    }
    

    Copy | Download

  • TY  - JOUR
    T1  - Characteristics and Suitability of Mayo-Lemie Soils for Corn Production
    AU  - Issine Agoubli
    AU  - Biaksoubo Teguinet
    AU  - Goalbaye Touroumgaye
    AU  - Allanaissem Ngonka Tombor
    Y1  - 2025/12/17
    PY  - 2025
    N1  - https://doi.org/10.11648/j.aff.20251406.12
    DO  - 10.11648/j.aff.20251406.12
    T2  - Agriculture, Forestry and Fisheries
    JF  - Agriculture, Forestry and Fisheries
    JO  - Agriculture, Forestry and Fisheries
    SP  - 232
    EP  - 239
    PB  - Science Publishing Group
    SN  - 2328-5648
    UR  - https://doi.org/10.11648/j.aff.20251406.12
    AB  - A study conducted in the Mayo-Lemié region of southwestern Chad aimed to determine the physicochemical characteristics and suitability of a soil for maize cultivation. A soil profile was established and described in the field, and soil samples were then collected from the different horizons. These samples were oven-dried for two weeks, crushed, labeled, and sent to the laboratory for routine analysis. The results of the analyses showed that all the samples analyzed ranged from slightly acidic to acidic with pH between 5.1 and 6.5; similarly, all exchangeable cations were poorly represented. The sum of exchangeable cation decreases with depth, as do the values of other nutrients. The results of the laboratory analyses were compared white the climatic data of the study area for evaluation according to the FAO. The climate assessment shows that the climate is very suitable for maize cultivation with an adjusted climate index of 88.03. It also appears from this study that the land unit concerned is marginally suitable for maize production with a parametric value of 31.82. The sandy texture remains the main limitation. To improve the situation, crop rotation is necessary, stubble should be returned to the fields after harvest, and mineral and organic fertilizers should be applied to improve the physical and chemical characteristics of the soil in order to increase yields.
    VL  - 14
    IS  - 6
    ER  - 

    Copy | Download

Author Information
  • Department of Agricultural Sciences, University of Sarh, Sarh, Chad

  • National Higher Institute of Agronomic Sciences and Agri-Food Technologies of Laï, Laï, Chad

  • Department of Agricultural Sciences, University of Sarh, Sarh, Chad

  • Direction of Agricultural Statistics, Ministry of Agriculture, Ndjamena, Chad