4681106-210249001281430-204470Journal of Environmental Education Research and Sustainable Development Volume 2, Issue 3 (1) (2023)00Journal of Environmental Education Research and Sustainable Development Volume 2, Issue 3 (1) (2023)left-161925Research article00Research article36948522801500457879217374800right79246JEERESDJournal Home page: www.jeeresd.online ISSN: 3078-211200JEERESDJournal Home page: www.jeeresd.online ISSN: 3078-2112right81182Genetic erosion and in-situ conservation of peanut (Arachis hypogaea L.) in Cameroon00Genetic erosion and in-situ conservation of peanut (Arachis hypogaea L.) in Cameroonright75625Victor AKOA 1, MEGUEKAM TEKAM Liliane2, NGALLE Hermine3, AKOA Dominique4, AKOA Régine4, BELL Joseph Martin3, NAVEEN Puppala5.1. Victor Akoa Trading Company for Plant Breeding and Genetic Resources, Cameroon2. Higher Teacher Training College of Yaoundé3. Laboratory of Plant Breeding, University of Yaoundé I, Cameroon4. National Advanced School of Posts and Telecommunications5. University of New Mexico00Victor AKOA 1, MEGUEKAM TEKAM Liliane2, NGALLE Hermine3, AKOA Dominique4, AKOA Régine4, BELL Joseph Martin3, NAVEEN Puppala5.1. Victor Akoa Trading Company for Plant Breeding and Genetic Resources, Cameroon2. Higher Teacher Training College of Yaoundé3. Laboratory of Plant Breeding, University of Yaoundé I, Cameroon4. National Advanced School of Posts and Telecommunications5. University of New Mexico21196306985abstract ContextGenetic erosion and in situ conservation are two strategies for resilience in food security. The main objective of this study was to know the interactions between these two concepts into the farmlands facing climate change threats. A survey of 224 peanut’s farmers of 75 localities was represented by two groups; North region (zone 1) with 111 farmers and South region (zone 2) with 113 farmers. 23 variables (questions), were divided in two categories; variables of protection (8 questions) and variables of production (15 questions). 00abstract ContextGenetic erosion and in situ conservation are two strategies for resilience in food security. The main objective of this study was to know the interactions between these two concepts into the farmlands facing climate change threats. A survey of 224 peanut’s farmers of 75 localities was represented by two groups; North region (zone 1) with 111 farmers and South region (zone 2) with 113 farmers. 23 variables (questions), were divided in two categories; variables of protection (8 questions) and variables of production (15 questions). 7499086600ARTICLE INFOKeywords:Peanut, genetic erosion, in situ conservation, food security, resilience, Cramer..00ARTICLE INFOKeywords:Peanut, genetic erosion, in situ conservation, food security, resilience, Cramer..right7620* Corresponding author. Email address: Email : victorakoa@gmail.comPhone : 00237699615877Adress : Yaoundé CamerounDOI : 10.5281/zenodo.18113647Received the 24 Jan 25; revised the 13 march 25; Accepted 03 September 25; published le 01 Jan 26. © 2025 The Authors. Published by EcoClean Environment Company. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/bync-nd/4.0/). 00* Corresponding author. Email address: Email : victorakoa@gmail.comPhone : 00237699615877Adress : Yaoundé CamerounDOI : 10.5281/zenodo.18113647Received the 24 Jan 25; revised the 13 march 25; Accepted 03 September 25; published le 01 Jan 26. © 2025 The Authors. Published by EcoClean Environment Company. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/bync-nd/4.0/). Factorial analysis of components (FAC) was used to construct in situ conservation models for the North and South system of production. The Cramer test, were used to link genetic erosion and in situ conservation. FAC shows that, models of in situ conservation are very specific inside each zone. IntroductionThe Convention on Biodiversity (CBD) (Heinrich, 2002), adds sustainability and resilience (Benton, 2009), facing threats of climate change for food security, Manda et al. (2025). Throughout the ages, men practiced agricultural resilience (Akoa, 2023), and in situ conservation (William, 2022) in farmlands Liu et al. (2021), for many reasons; as nutrition, Nila et al. (2019), clothing, cosmetic, Talebmorad et al. (2021), and medical needs (Zhang, 2019). Peanut (Arachis hypogaea L.) is originated to South America (Hammons, 1994), and in Cameroon, it introduces in 1928 (Hamasselbé, 2006). In situ conservation integrates also storage into high and small farmlands (UNCED, 1992; Maxted et al., 1997ab). The main conservations are the landraces Maxted et al. (2002). Cameroon, has five agro ecological system of food production (DSCE, 2009; figure 1), and for natural conservation which plays and important role in food security. Also, farmers participate actively by selecting peanuts after every harvest, for sowing to the following season Maxted et al. (1997c). Because, peanut plays the third important role, after cocoyam and maize (Hamasselbé, 2008) in Cameroon. And, peanut is very resilient, in land for food security (Nwaga, 2000, Akoa, 2024a), by its good adaptability (Park, 2009; Foncéka, 2010, Akoa, 2024c). The methods of in situ conservation (FAO, 2014; Maxted, 2002) by farmers in spite of the absence of storage factories Maxted et al. (1997b) are specific (Nana, 2021) facing climate change’s threats (Pachauri & Meyer, 2014; FAO, 2010) to fight against food insecurity. Today, this economical method of conservation (Yébi-Mandjek & Seignobos 2010), is confronted to the genetic erosion (FAO, 2009; Essomba, 1990) enhances by climate change threats (GIEC, 2007). Van de Wouw et al. (2009) define genetic erosion as the loss of variation in crops due to the modernization of agriculture. Nevertheless, many new cultivars introduce by genetic erosion are very attractive by big farmlands in this country (Akoa, 2024b), and contribute also at the resilience process, but using others variables for it sustainability (Akoa, 2024c). The main objective of this study, is to know whether in situ conservation and genetic erosion could interacted in food security.Material and methodsII.1. MaterialsII.1.1. SurveyVariables of production: Question 1 (Q1) Do you sell the peanuts you produce? Question 2 (Q2) apart from groundnuts, do you grow anything else? Question 3 (Q3) Do you feed animals with the groundnut’s tops? Question 4 (Q4) Are groundnuts grown twice a year in your home? Question 5 (Q5) Do you eat the peanuts you harvest? Question 6 (Q6) Do you have two rain cycles? Question 7 (Q7) Is your parcel ten years old? Question 8 (Q8) Does this plot belong to you? Question 9 (Q9) Have you received training for this crop? Question 10 (Q10) Are the crops grown in the off-season? Question 11 (Q11) Do you use the same varieties? Question 12 (Q12) Are you satisfied with the returns? Question 13 (Q13) Do you use an herbicide? Question 14 (Q14) Do you enrich your parcels with NPK? Question 15 (Q15) Do you use sulphide as an input? (Essomba et al., 1990; Hamasselbé, 2006; Ibrahim, 2010). Variables of protection: Question 1 (Q1) Are your peanut crops still sick? Question 2 (Q2) Do you have training on peanut diseases? Question 3 (Q3) When your parcels are sick, do you treat them? Question 4 (Q4) Do you practice fallow? Question 5 (Q5) Do you make associations of cultures? Question 6 (Q6) Do you use (bio) pesticides? Question 7 (Q7) Do you use breeding seeds? Question 8 (Q8) Do public authorities help you in the event of yield losses due to disease? (FAO, 2015).II.1.2. Representation of Farmers A sample of 224 peanut farmers in towns and villages, divided as follows: North localities: 30 farmers from towns; 81 farmers from villages; South localities: 50 farmers from towns; 63 farmers from villages using the map of agro ecological (figure 1). During 2021-2023. Fig.1. Agro ecological area of Cameroon (DSCE, 2009)II.2. METHODSII.2.1. Choice of towns and villages In the first hand, the first approach was knowledge about peanut (cultivation and utilization). The second approach was in situ conservation methods. The third approach was the period of 4 years for production of peanut. All these approaches were according Agricultural Research Institute for Development (ARID) and the technical sheet of Hamasselbé et al. (2003). In the second hand, the designation of farmland as town was assessed at 10 -500 m2, and village greater than 500 m2 contrarily to FAO methodology of (Khalil et al., 2017; Akhere & Ndzifon, 2020). II.2.2. Codification of FarmersFarmers into North and South region codified as: INVLE1. I: Inhabitant (farmer), N: North, VLE 1: City’s Farmer number 1. ISVLE 7; I: Inhabitant, S: South, VLE7: City’s Farmer number 7 or; ISVAG 42: I: Individual; S: South, VAG; village’s Farmer number 42) Hamasselbé et al. (2003). Zone 1 is North zone grouping three regions: Adamawa, north and far north. Zone 2 is South zone grouping seven regions: Center, East, West, Littoral, South, South-West, North West (NPCCA, 2015).II.2.3. Data analysisFactorial analyzes of components (fac) Pressac & Mell, 2017 was used to construct all models of in situ conservation in the North and South also for the global system of production. Cramer (1946) value (1) test scale, was used to compare level of genetic erosion and in situ conservation intensity V=Φ²/min⁡(k-1, r-1)  Φ²:coefficient phi;K:number of raw;r:number of lignesGenetic erosion and genetic erosion of Cramer scale ranging from 1 to 6, for each value obtained. Most the V value is closed to 1, most the risk of genetic erosion is lower, and high is in situ conversation. Inversely, more the V value is closed to 0, most the risk of genetic erosion is high and in situ conservation is weak. Summarily, peanut’s conservation is inversely proportional to genetic erosion (table I). Software R program, version 4.2.3 (R Core Team 2023).Table I: Cramer’s value adaptation scale to peanut genetic erosion and conservation Cramer’s test (V)InterpretationScale Genetic erosion characteristicIntensity of conservationbetween 0 et 0.05Absence of liaison6Very highNon existantbetween 0.05 et 0.1very weak5HighLittle existingbetween 0.1 et 0.2Weak4Quite highExistingbetween 0.2 et 0.4moderate 3ExistingQuite highbetween 0.4 et 0.8High2Little existingHighbetween 0.8 et 1Collineaire1Non existantVery highIII. Results and discussionIII.1. ResultsIII.1.1. Models for in situ conservation of peanut III.1.1.1. Models for North and South townsThe farmers from north and south cities are represented at 61.69% in the fac. The different colors represent the levels of representations with respect to the square cosine (cos2) of the variables of the farmers and of the modalities of the questions. Farmers from north towns, INCT18 and INCT7 are correlated to the in-situ conservation model of peanuts of variable Q15 by the use of sulfur. The farmers from south cities, ISCT39 and ISCT33 are correlated to in-situ conservation model of peanuts for the variable Q6, linked to the two cycles of the rainy seasons. The farmers from the south city ISCT23 are correlated to the in-situ conservation model of peanuts by variables Q4 and Q10 related to the practice of peanut cultivation twice a year and in the off-season. Variable Q14 which represents the enrichment in NPK does not characterize the farmers of the cities of the South and is an extreme variable and little correlated to the individuals of the cities of the south ISCT32 and ISCT27 which, on the other hand, are not very correlated to the related conservation model (figure2). Fig.2. Model for in situ conservation for peanut in North and South townsIII.1.1.2. Models for North and South villages The farmers of the north and South villages are represented at 61.61% in the fac. The different colors represent the levels of representations with respect to the square cosine (cos2) of the variables of the farmers and of the modalities of the questions. The farmers from south villages ISVAG15, ISVAG55, ISVAG25 are correlated to the in-situ conservation model of peanuts for variables Q4 and Q6 relating to the double cultivation of groundnuts following the two rainy seasons. Variable Q10, is linked to off-season agriculture is an uncommon practice among individuals in south villages (figure 3). Fig.3. Model for in situ conservation for North and South villagesIII.1.1.3. General model of in-situ conservation for zone1The farmers from the north zone including the farmers from towns and villages are represented at 85.84% in the fac. The different colors represent the levels of representations with respect to the square cosine (cos2) of the variables of the farmers and of the modalities of the questions. The models of in situ conservation of groundnuts which characterize this north zone are the variables Q1, Q8, Q14, Q15, respectively relating to the marketing of groundnuts, the ownership of arable land, the enrichment in NPK, and the use of sulfur. The farmers from north towns, INCT26 and INCT28 have the same model of in situ conservation as the farmers from villages, INVAG (49, 36, 58, and 71 (figure 4). Fig.4. General model of in-situ conservation for zone1III.1.1.4. General model of in-situ conservation for zone2The farmers from towns and villages in the south zone are represented at 33.35% in the fac. The different colors represent the levels of representations with respect to the square cosine (cos2) of the variables of the farmers and of the modalities of the questions. The in-situ conservation models for peanuts from farmers in this south zone are the variables Q3, Q10, Q12, Q13, and Q14. These variables of in-situ conservation in the south refer respectively to livestock feed, off-season agriculture, yield satisfaction, herbicide use, and NPK. In situ conservation models for peanuts Q14 and Q13 diverge from conservation variables in the south (figure, 5). Fig.5. General model of in-situ conservation for zone2III.1.1.5. General system of in situ conservation for 224 farmersThree general patterns of production in groundnut cultivation are represented in dimensions 1 and 2 at 45.26%. The south region contains a single, but hybrid cropping pattern combining town and village techniques, while the north region contains two pure cropping patterns, one for towns and one for villages (figure 6). Fig.6. General system of in situ conservation for 224 farmersIII.1.2. Models of variables for in situ conservationIII.1.2.1. Model of variables for production in zone 1 and 2The peanut production model variables for zones 1 and 2 is represented at 55.62% in the fac. The different colors represent the levels of representation with respect to the cosine squared (cos2) of the variables of the farmers and the modalities of the questions. In situ conservation models of the south region are negatively correlated to variables Q3, Q7, Q8, Q9, Q11, Q12, Q13, Q14, Q15 which represent the in-situ conservation variables of the north, but in situ conservation of the peanut is done by the conservation models of the variables Q1, Q2, Q4, Q5, Q6, Q10 (figure 7). Fig. 7. Model of variables for production in zone 1 and 2III.1.2.2. Model of variables for protection in zone 1 and 2The variables which characterize best the north region for protection are question 2 (Q2) do you have any training on peanut diseases? Question 3 (Q3) when your plots are diseased do you treat them? Question 6 (Q6) do you use pesticides? Question 8 (Q8) Does the government help you in case of yield losses due to disease? These variables are strongly correlated. The variables which characterize best the south region for protection are the variables related to questions 4 and 5 respectively: Question 4 (Q4) do you practice fallow? Question 5 (Q5) do you do crop associations? (Figure 8).Fig.8. Model of variables for protection in zone 1 and 2III.1.2.4. General variables of production for 224 farmers The north region is strongly correlated to the variables Q7, Q8, Q9, Q13, Q14, Q21, Q3, and negatively correlated to the variables Q17, Q6, Q4, Q10, which represents the characteristic variables of the south region (figure 9). Fig. 9. General variables of production for 224 farmersIII.1.3. Intensity of peanut conservationIII.1.3.1. North and south citiesThe 100% of the intensities of the connections of the towns of the south and the north are reached in dimension 14. The connection is almost average between the farmers of the towns of the north and the south and the variables, in the first dimension (0.43) and almost zero in dimension 13 (0.01), the first two dimensions have a value of 61.69%. Cramer's test gives a value of 0.445 (2) which corresponds to a little existence of genetic erosion and high level of in situ conservation of peanut (table II).Table II. Dimension of Cramer values in north and south towns Eigen value% of variancecumulative % of variancedim 10.4348.2848.28dim 20.1213.4161.69dim 30.077.7169.40dim 40.066.4575.85dim 50.055.3681.21dim 60.044.5785.78dim 70.033.5189.29dim 80.022.5391.82dim 90.022.3994.21dim 100.021.8196.02dim 110.011.6497.66dim 120.011.1798.82dim 130.010.7599.58dim 140.000.42100.00V of Cramer0.445 (2) Dim = dimensionIII.1.3.2. North and south villagesThe 100% of the intensities of the links of the villages of the south and the north are reached in dimension 13. The dependence between the conservation variables and the individuals of the villages of the north and the south is weak in the first dimension (0.25) and is almost independent (0.01) at the 11th dimension. The first two dimensions have a cumulative value of 61.60%. Cramer's test gives a value of 0.3 (3), this value corresponds to an existence of genetic erosion and a quite high level of peanut conservation (table III).Table III. Dimension of fac values of north and south villages Eigen value% of variancecumulative % of variancedim 10.2541.5041.50dim 20.1220.1161.60dim 30.069.9171.51dim 40.057.7679.27dim 50.034.5483.81dim 60.023.8787.68dim 70.023.3691.04dim 80.023.2694.29dim 90.011.9596.24dim 100.011.7497.98dim 110.011.4199.39dim 120.000.3999.78dim 130.000.22100.00V of Cramer0.3 (3)III.1.3.3. Intensity of peanut conservation in zone1The 100% of the intensities of the links in the north zone are reached at dimension 7. The links between the variables and the individuals of zone 1 are independent (0.09) at the first dimension and almost zero at the third dimension and (0.01). The first dimension has a cumulative value of 71.20%. Cramer's test gives a value of 0.06 (5), this value corresponds to a high genetic erosion and a little existing level of peanut conservation (table IV).Table IV. Dimension of fac values of zone1 Eigen value% of variancecumulative % of variancedim 10.0971.2071.20dim 20.0214.6485.85dim 30.015.4391.28dim 40.003.0794.35dim 50.002.6396.98dim 60.001.7898.76Dim70.001.24100.00V of Cramer 0.06 (5)III.1.3.4. Intensity of conservation in zone 2The 100% of the intensities of the connections in the south zone are reached at dimension 13. The connections between the individuals of the south and the conservation variables in dimension 1 are weak (0.20) and almost zero at the 3rd dimension (0.02). The first dimension has a cumulative value of 18.73%. Cramer's test gives a value of 0.545 (2), which corresponds to a little existence of genetic erosion and a high level of peanut conservation (table V). Table V. Specific values of the conservation of the inhabitants of zone 2 Eigen value% of variancecumulative % of variancedim 10.2018.7318.73dim 20.1614.6233.35dim 30.1614.3347.68dim 40.1211.3959.07dim 50.1110.3569.42dim 60.076.8076.22dim 70.065.6781.89dim 80.054.3986.28dim 90.043.6789.95dim 100.043.3993.34dim 110.032.5595.89dim 120.032.4098.29dim 130.021.71100.00V of Cramer 0.545 (2)III.1.3.5. Intensity of conservation for 224 farmers 100% of the intensities of the bonds in zone 1 and 2 are reached at dimension 14. The intensity of the bonds between the farmers and conservation variables on the general level vary between 0.34 and 0.01 from the first to the 14th dimension. The first dimension has a cumulative value of 43.46%. Cramer's test gives a value of 0.385(3). This value corresponds to an existence of genetic erosion and a quite high level of peanut conservation (table VI).Table VI. Specific values of the conservation of the inhabitants of zone 1 and 2 Eigen value% of variancecumulative % of variancedim 10.3443.4643.46dim 20.0912.1655.62dim 30.0810.1665.77dim 40.067.5273.29dim 50.045.5178.81dim 60.034.2183.02dim 70.034.0087.01dim 80.022.9689.98dim 90.022.8292.79dim 100.022.1194.90dim 110.011.7996.69dim 120.011.44698.15dim 130.011.1299.27dim 140.010.73100.00V of Cramer0.385 (3)Table VII. Summary of assessmentsNorth and South villages also zone 2 are the same scale intensity (2) and same characteristics of genetic erosion and in situ conservation intensity. Zone 1 has a little existing in situ conservation and high genetic erosion.SitesCramer’s valueScale intensityCharacteristic of genetic erosion In situ conservation intensityNorth and South towns0.33Existing Quite highNorth and South villages0.4452Little existingHighZone 10.065HighLittle existingZone 20.5452Little existingHighZone 1 and 20.3853Existing Quite highIII.2. DiscussionsProtection and production model and global system of productionThe representation of the fac contradicts the results of Khalil et al. (2017) basing on the standard work of the FAO which demonstrates that there would be an uniformity of production by area of less than 2 ha, while figure 2 demonstrates a variability of farmers. This variability of farmlands could be explained by the fact that it is a supply capacity at different time periods of seedlings’ demand both in markets and households. Supply and demand can thus be in balance to explain price stability in the markets and remain within the purchasing power threshold of populations. And according to (Aryal, 2021), these results in the small farmlands in urban areas are for fighting against food shortages. In large areas, 61.61% (figure 3) average of farmlands correlate to some variables of production in south villages. The best representation would be strongly correlated to Q10 variable which represents an off-season crop. Thus, it is the off-season which mainly characterizes the production of the big farmers into the south. This could be explained by the fact that, irrigation methods would not be developed to support off-season agriculture. These results confirm the work of (Akhere & Ndzifon, 2020) on the production strategies of farmers in Bamenda in times of drought. The cultures of the south zone take place both in the growing season and in the off-season, certainly by the use of swamps. This allows a continuous supply of this agricultural speculation in the south markets, in the absence of supply from the groundnut basin from the north. This could be explained by the fact that the issues and structures present in the two peanut production system areas don’t meet the same objectives. Indeed, zone 1 or north zone is considered as the national peanut basin and the availability of seedling is more encouraged than in zone 2. The presence of non-governmental organizations and research institutions are more important and benefit more from the funds of research for the satisfaction of demand and even of technological innovation. These results are confirmed by (Yébi-Mandjek & Seignobos, 2010) and also by Hamasselbé et al. (2003) on intensive farming in the Sudano-Sahelian zone of north Cameroon. Similarly, the mixed model of conservation (figure 9) confirms this result.Among these 224 peanut producers, there are two main peanut systems (figure 6). The system in the south region, which has a strong representation of certain farmlands, has a certain heterogeneity by combining a big-area of farmlands (ISVAG 30). This could be explained by the fact that the agricultural system that he would practice would be similar to the small farmers. The second conservation system with three variants namely a homogeneous agricultural system of towns and villages and a mixed agriculture. These results contradict the works of Essomba et al. (1990), who present peanut production with four systems.In situ conservation intensity and genetic erosionThe Cramer's test gives a value of 0.445 (2), which corresponds to a little existence of genetic erosion and a high level of conservation of peanut in north and south cities. Cramer's test gives a value of 0.3 (3). This value could be explained by an existence of genetic erosion and a quite high level of peanut conservation in north and south villages. Because in towns, the conservation of seeds is very ease, and the intensity reflects the level of attachment that small farmers have with the family seedling from previous harvests. Thus, small farmers (towns) produce for self-consumption due to low household demand. These results corroborate the work of (Hamasselbé, 2008) on the revaluation of groundnut production threatened with genetic erosion in agricultural competition; as well as those obtained by the same author (Hamasselbé, 2006) on the place of groundnut consumption in the north Cameroon, faced with an increase in demand for food security. The genetic erosion of villages (0.3) for Cramer test gives 3 and therefore exists, but peanut conservation is quite high. This could be explained by the fact that confidence in the new seedling cannot be a guarantee of sufficient productivity. Because in developed countries there would be losses in yields following a genetic erosion of around 30% due to uncontrolled pathogens (Dong & Pamela, 2019), and on the other hand, the search for biological uniformity in yields and resistance to diseases could not be tested in large areas, who do not have research structures for carrying out trials Betdogo et al. (2015). Nevertheless, big farmers still test new seedlings, with the aim of improving yields; while small farmers don’t take this risk, and keep the seedlings from previous crops. The big farmers are informated about research’s results and also oriented productions to commercialization, while the small farmers are oriented to self-consumption, and therefore only seek their subsistence. These two kings of in situ conservation by both big and small farmers corroborate the work of (Nana, 2021) on biodiversity conservation in Central Africa, when he speaks of mixed conservation. IV. ConclusionIn situ conservation intensity and genetic erosion interactions exist in farmlands. This strategy could be used in peanuts production system, facing climate change threats. in situ conservation is very diversified and it is inversely proportional to genetic erosion. Two approaches for measuring in situ conservation was made by utilizing factorial analysis components (FAC) and Cramer’s value adaptation scale test. In sum, Cramer test value of 0.385 characterizes the presence of genetic erosion, and a quite high level (3) of in situ conservation. All pillars of food security are presented, but it is duo to the utilization of chemicals products for sustaining production into the main basin of peanuts. Facing climate change threats, the practice of genetic erosion to sustain food security inside the farmlands is another solution. Also, genetic erosion and in situ conservation of peanut are the two resilient approaches against food insecurity. Declaration of interests: The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.Available of data and materials: The datas are available at University of Yaounde I, Cameroon Laboratory of genetic and plant breeding. Tel. +237 699615877Compliance with ethical standardsConflict of interest: The authors declare that they have no conflict of interestEthical approval: This article does not contain any study with human participants or animals performed by any of the authors.Acknowledgments: We thank the encouragements for the University of New Mexico and AMOUGOU NDI ACHILLE University of Yaounde I.Author contributions: AKOA DOMINIQUE helps for data analysis and corrections. AKOA REGINE helps for English language and corrections. OBILOMA ARMAND helps for data collection and registration. 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