African Journal of
Agricultural Research

  • Abbreviation: Afr. J. Agric. Res.
  • Language: English
  • ISSN: 1991-637X
  • DOI: 10.5897/AJAR
  • Start Year: 2006
  • Published Articles: 6860

Full Length Research Paper

Contribution of soil macro-fauna diversity and abundance to soil fertility enhancement in cocoa-based (Theobroma cacao) agroforestry systems in the Littoral Region of Cameroon: An appraisal of cocoa farmers’ local knowledge

Azembouh Roshinus Tsufac
  • Azembouh Roshinus Tsufac
  • Department of Forestry, Faculty of Agronomy and Agricultural Sciences, University of Dschang, P. O. Box 222, Dschang, Cameroon.
  • Google Scholar
Bernard Palmer Kfuban Yerima
  • Bernard Palmer Kfuban Yerima
  • Department of Soil Sciences, Faculty of Agronomy and Agricultural Sciences, University of Dschang, P. O. Box 222, Dschang, Cameroon.
  • Google Scholar
Roger Kogge Enang
  • Roger Kogge Enang
  • Department of Soil Sciences, Faculty of Agronomy and Agricultural Sciences, University of Dschang, P. O. Box 222, Dschang, Cameroon.
  • Google Scholar
Nyong Princely Awazi
  • Nyong Princely Awazi
  • Department of Forestry, Faculty of Agronomy and Agricultural Sciences, University of Dschang, P. O. Box 222, Dschang, Cameroon.
  • Google Scholar


  •  Received: 10 December 2020
  •  Accepted: 26 January 2021
  •  Published: 28 February 2021

 ABSTRACT

Soil macro-fauna diversity and abundance greatly influence soil fertility. However, little has been done to confirm this hypothesis in cocoa-based agroforestry systems. It was in this light that this research work was undertaken in order to fill the knowledge gap. Through the use of a mixed research method for data collection and appropriate data analysis procedures, findings showed that diverse soil macro-fauna were identified by cocoa farmers in cocoa-based agroforestry systems with the main being earth worms (100%), ants (100%), termites (70%), millipedes (50%), centipedes (50%), and snails (60%). Most cocoa farmers perceived that soil macro-fauna diversity in cocoa-based agroforestry systems was high (58.3%) and very high (17%) respectively. Earth worms, ants, millipedes, centipedes, spiders, harvestmen and scorpions were perceived by most cocoa farmers (44%, 38.3%, 43.3%, 41.3%, 55.6%, 53.3% and 48% respectively) to have a high level of abundance in cocoa-based agroforestry systems. A statistically significant direct non-causal and causal relationship (p<0.05) existed between soil macro-fauna diversity and soil fertility enhancement in cocoa-based agroforestry systems, implying that the higher the diversity, the higher the level of soil fertility and the lower the diversity, the lower the level of soil fertility enhancement. Concerning soil macro-fauna abundance, a statistically significant direct non-causal and causal relationship (p<0.05) existed between soil macro-fauna abundance (i.e. for earth worms, ants, termites, beetles, crickets, woodlice, snails and slugs) and soil fertility enhancement in cocoa-based agroforestry systems, implying that the greater the abundance of these soil macro-fauna, the greater the fertility of the soil. It is recommended that measures be taken to ensure soil macro-fauna diversity and abundance in order to enhance the fertility of the soil in cocoa-based agroforestry systems.

Key words: Cocoa, cocoa farmers, agroforestry, cocoa-based agroforestry systems, soil macro-fauna, macro-fauna, soil fertility, Cameroon.


 INTRODUCTION

Agroforestry systems  are  climate-smart, environmentally friendly, agro-ecological and sustainable farming systems wherein trees/shrubs are integrated in crop and pasturelands in order to obtain socio-economic and environmental/ecosystem benefits (Jose, 2012; Amare et al., 2018; Leakey, 2019; Quandt et al., 2018; Awazi et al., 2020; Awazi and Avana, 2020). Agroforestry systems are broadly classified into three major groups, that is, agrosilvicultural, silvopastoral and agrosilvopastoral (Awazi et al., 2019). These three main categories are characterized by practices like home gardens, trees on croplands, home gardens with livestock, life fences, windbreaks, coffee-based agroforestry, cocoa-based agroforestry, rubber-based agroforestry, trees on grazing lands, aquaforestry, entomoforestry and many others (Tsufac et al., 2019; Awazi et al., 2020). Although the term “systems” is often used interchangeably with the term “practices”, systems generally refer to the three broad categories, while practices refer to the sub-categories.

Agroforestry systems provide different ecological services one of which is soil fertility enhancement (Nair, 2011; Asaah et al., 2011; Noordwijk et al., 2019; Tsufac et al., 2019). This is done through nutrient cycling between the above-ground and below-ground components of the system (Cardinael et al., 2020). The above-ground components are trees/shrubs as well as crops while the below-ground components are tree roots and soil organisms. The close interaction of these two components contributes towards soil fertility enhancement in the agroforestry system (Jose, 2009, 2012; Leakey, 2017; Amare et al., 2018).

In Cameroon, cocoa-based agroforestry systems constitute one of the main types of agroforestry systems (Sonwa et al., 2007; Laird et al., 2007; Jagoret et al., 2011, 2014; Tankou, 2015). It is a system where mostly smallholder farmers integrate and/or maintain trees/shrubs in cocoa farms to act as shade for the cocoa plant. Both local and exotic tree species are integrated in the system, and farmers make sure that the trees integrated have multiple uses, thus the term “multipurpose trees” in agroforestry systems (Sonwa et al., 2007). The trees act as shade, wood, building materials, biofertilizers, fodder, windbreaks, food, medicines and many other uses (Tankou, 2015).

Cocoa production in Cameroon which is dominated by smallholder farmers as mentioned earlier, is cultivated under the cocoa-based agroforestry system (Jagoret et al., 2012). It contributes enormously to the Gross Domestic Product (GDP) of the country (Nfinn, 2005; Mukete et al., 2018). However, most of the smallholder farmers engaged in the cocoa production, reap very little benefits from their hard work because the price of cocoa is dictated by middlemen who seek to make as much commission   as   possible   from   their   middleman   role  (Tankou, 2015; Mukete et al., 2018). This situation has made many farmers to abandon their cocoa farms and take to other alternative activities such as market gardening, food crop cultivation and even bike riding (Tankou, 2015).

With soil fertility in cocoa-based agroforestry systems declining and cocoa farmers’ inability to purchase fertilizers to replenish the lost fertility, it becomes imperative to promote organic farming methods. For this to be feasible, the soil needs to be treated with care so as not to destroy soil organisms in general and soil macro-organisms in particular which are the engineers working every day to ensure that the soil remains naturally fertile. Thus, looking at the grim picture of soil infertility across cocoa-based agroforestry systems in Cameroon in general and littoral region of Cameroon in particular, this study sought to assess the contribution of soil macro-fauna diversity and abundance to soil fertility enhancement in cocoa-based agroforestry systems. More precisely, the study sought to:  (1) identify soil macro-fauna in cocoa-based agroforestry systems; (2) assess the degree of soil macro-fauna diversity in cocoa-based agroforestry systems; (3) examine the level of soil macro-fauna abundance in cocoa-based agroforestry systems; and (4) assess the relationship between soil macro-fauna diversity and abundance and soil fertility in cocoa-based agroforestry systems.


 MATERIALS AND METHODS

Description of the study area

The study was carried out in the administrative district of Melong, found in the Mungo division, Littoral region of Cameroon.  It lies between longitude 9°17’ to 10°52’ E and latitude 4°22’ to 6°20’ N.  The study area falls within the Western Highlands of Cameroon, a major agro-ecological and relief region in Cameroon. The Western Highlands covers four administrative regions in Cameroon (part of the littoral, part of the south west, and the entire west and north-west regions) and has a surface area of roughly 50,000 km2. A vast majority of the population (over 80%) is engaged in agricultural activities and livestock rearing. Due to the predominance of agricultural activities, the Western Highlands of Cameroon (Mungo division in general and Melong sub-division in particular) is considered one of the major breadbaskets of Cameroon and the Central African sub-region (Tankou et al., 2017). The climate of the Melong sub-division is humid tropical and the vegetation type is degraded forest interspersed with patches of savannah grassland. The soils are mostly ferralitic, volcanic, as well as andosols.

Melong administrative district was created in 1962 by Decree No. 62/17 of 26/12/1962 (Plan Communal de Developpement - PCD Melong, 2012). It covers an area of 497 km2 and has a population of about 102,000 persons living in both rural and urban settings (Plan Communal de Developpement - PCD Melong, 2012). The municipality of Melong shares boundaries with the municipality of Santchou to the north; the  municipality of Nguti  to  the  north-west; the municipality of Bangem to the west; the municipality of Nkongsamba to the south-west; the municipality of Baré to the south-east; the Nkam River and the municipality of Kékem to the east.

Data collection procedure

To achieve the goals of this study, secondary and primary data were collected. For primary data a plethora of sampling techniques were used.

Sampling procedure

The multi-phase sampling procedure was used as reported in previous studies undertaken by some authors in Cameroon (Awazi and Tchamba, 2018; Awazi et al., 2019, 2020). At the first phase, the study area (Mungo division in general and Melong sub-division in particular) was purposively chosen owing to the predominance of cocoa-based (Theobroma cacao) agroforestry systems in the area. At the second stage, focus group discussions and key informant interviews were conducted with cocoa farmers and resource persons, respectively in order to obtain relevant information on macro-fauna diversity/abundance and its role in soil fertility enhancement in cocoa-based agroforestry systems in the study area. The focus group discussants were mainly farmers who had great indigenous knowledge about the cocoa-based agroforestry system. Cocoa farmers selected to participate in focus group discussions were done with the help of agricultural/environmental extension agents who had a better mastery of the study area. The key informants who were resource persons living in the different villages in the municipality of Melong included agricultural and environmental extension agents, chiefs, quarter heads, heads of cocoa farming groups, sub-divisional delegates in the ministries of agriculture and rural development; forestry and wildlife; environment, nature protection and sustainable development. At the third phase, household surveys were conducted with farmers involved in cocoa-based agroforestry systems. This was done with the help of agricultural extension agents working on the field. The tool used to conduct the household survey was semi-structured questionnaires. The questionnaires were structured to get information on the types of soil macro-fauna in cocoa-based agroforestry systems; the degree of soil macro-fauna diversity in cocoa-based agroforestry systems; the level of soil macro-fauna abundance in cocoa-based agroforestry systems; and the relationship between soil macro-fauna diversity and abundance and soil fertility in cocoa-based agroforestry systems. The fourth and last stages involved direct field surveys on the farm plots of cocoa farmers. In these phases, both soil macro-fauna diversity/ abundance and soil fertility parameters were measured. This was done through inventories of soil macro-fauna and collection of soil samples for laboratory testing.

Secondary data

To realize the objectives of this work, secondary data was collected from the following sources:

(1) The Regional, Divisional and Sub-Divisional Delegations of Agriculture and Rural Development; Forestry and Wildlife, Environment and Nature Protection; and Economy and Regional Planning, and Municipal councils found in the Mungo division in general and Melong sub-division in particular;

(2) Libraries in the Faculty of Agronomy and Agricultural Sciences of the University of Dschang;

(3) Scientific publications or articles, books and book chapters  both online and offline;

(4) Different websites on the internet.

Secondary data enabled the verification and comparison of the contribution of soil macro-fauna to soil fertility in cocoa-based agroforestry systems in Melong administrative district to that of other areas in Cameroon, Africa and the world.

Primary data collection

Primary data was collected through household surveys, direct field surveys as well as direct field observations.

Household surveys: Household surveys were conducted with farmers practicing cocoa-based agroforestry systems in order to ascertain their perceptions pertaining to the contribution of soil macro-fauna to soil fertility improvement. Semi-structured questionnaires were administered to 300 cocoa-based agroforestry practitioners. The questionnaires were structured to capture information with respect to the types of soil macro-fauna in cocoa-based agroforestry systems; the degree of soil macro-fauna diversity in cocoa-based agroforestry systems; the level of soil macro-fauna abundance in cocoa-based agroforestry systems; and the relationship between soil macro-fauna diversity and abundance and soil fertility in cocoa-based agroforestry systems. The selection of these farmers was done with the aid of agricultural/environmental extension officials working on the field in the study area. The household survey of 300 farmers was complemented with focus group discussions, and key informant interviews in order to ascertain the truthfulness of farmers’ perceptions.

Data analysis

Microsoft Excel 2007 and SPSS 17.0 software packages were used for descriptive and analytical statistical analysis. The main descriptive statistics were charts, graphs, tables as well as percentage indices, while analytical statistics included Spearman’s correlation coefficient, Chi-square test statistic, and logistic regression analysis. The analytical statistics were used based on the normality of the data obtained as well as the type of variables, that is, qualitative or quantitative. Analytical statistics indicated the causal and non-causal relationship existing between soil macro-fauna diversity/abundance and soil fertility status in the cocoa-based agroforestry systems in Melong Municipality, littoral region of Cameroon.


 RESULTS

Identified soil macro-fauna in cocoa-based agroforestry systems

Diverse soil macro-fauna were identified by cocoa farmers in cocoa-based agroforestry systems in the Littoral region of Cameroon (Table 1).

Table 1 shows that earth worms (100%), ants (100%), termites (70%), millipedes (50%), centipedes (50%), and snails (60%) were identified by cocoa farmers as the main soil macro-fauna in cocoa-based agroforestry systems. As per cocoa farmers’ perceptions, beetles, harvestmen, scorpions and slugs were the least identified soil macro-fauna in cocoa-based agroforestry systems.

Cocoa  farmers’  perceptions  of  different   soil   macro- fauna in cocoa-based agroforestry systems differed significantly (c2 = 127.4, p<0.05).

Degree of soil macro-fauna diversity in cocoa-based agroforestry systems

Cocoa farmers perceived the level of soil macro-fauna diversity in cocoa-based agroforestry systems differently (Table 2).

From Table 2, it is noticed that most cocoa farmers perceived that soil macro-fauna diversity in cocoa-based agroforestry systems was high (58.3%) and very high (17%), respectively, with few cocoa farmers (6.7%) perceiving that soil macro-fauna diversity in cocoa-based agroforestry systems was very low.

Cocoa farmers’ perceptions of the level of soil macro-fauna diversity in cocoa-based agroforestry systems differed significantly (c2 = 75.8, p<0.05).

Level of soil macro-fauna abundance in cocoa-based agroforestry systems

Cocoa farmers perceived the level of soil macro-fauna abundance   in   cocoa-based   agroforestry   systems   in a diverse fashion (Table 3).

As shown in Table 3, earth worms, ants, millipedes, centipedes, spiders, harvestmen and scorpions were perceived by most cocoa farmers (44, 38.3, 43.3, 41.3, 55.6, 53.3 and 48%, respectively) to have a high level of abundance in cocoa-based agroforestry systems. Crickets, woodlice, snails and slugs were perceived by most farmers (58.3, 62.5, 53.3 and 55.6%, respectively) to have an average abundance in cocoa-based agroforestry systems. Termites and beetles were perceived by most cocoa farmers (58.6 and 48.6%, respectively) to have a low abundance in cocoa-based agroforestry systems.

As shown in Table 3, a statistically significant difference (c2 > 40, p<0.05) existed between farmers’ perceptions of abundance of soil macro-fauna in cocoa-based agroforestry systems.

Influence of soil macro-fauna diversity on soil fertility in cocoa-based agroforestry systems

Spearman rank correlation and logistic regression analyses showed the existence of a direct non-causal and causal relationship between soil macro-fauna diversity and  soil  fertility  enhancement  in  cocoa-based agroforestry systems (Table 4).

As shown in Table 4, a statistically significant (p<0.05) direct non-causal and causal relationship was found to exist between different levels of soil macro-fauna diversity (very high soil macro-fauna diversity, high soil macro-fauna diversity, average soil macro-fauna diversity, low soil macro-fauna diversity, and very low soil macro-fauna diversity) and soil fertility enhancement in cocoa-based agroforestry systems.

Influence of soil macro-fauna abundance on soil fertility in cocoa-based agroforestry systems

Spearman rank correlation and logistic regression analyses revealed the existence of a direct non-causal and causal relationship between soil macro-fauna abundance and soil fertility enhancement in cocoa-based agroforestry systems (Table 5).

As shown in Table 5, there was a statistically significant (p<0.05) difference between the abundance of some soil macro-fauna (earth worms, ants, termites, beetles, crickets, woodlice, snails and slugs) and soil fertility enhancement in cocoa-based agroforestry systems. Although, there was a direct non-causal and causal relationship between the abundance of some soil macro-fauna (millipedes, centipedes, harvestmen, spiders and scorpions) and soil fertility improvement in cocoa-based agroforestry systems; there was no statistical significance (p>0.05).


 DISCUSSION

Soil macro-fauna identified by cocoa farmers in cocoa-based agroforestry systems

Diverse soil macro-fauna were identified by cocoa farmers in cocoa-based agroforestry systems in the Littoral region of Cameroon. Earth worms, ants,  termites, millipedes, centipedes, and snails were the major soil macro-fauna identified by cocoa farmers in their cocoa-based agroforestry systems. Beetles, harvestmen, scorpions and slugs were the least identified soil macro-fauna in cocoa-based agroforestry systems. Cocoa farmers’ perceptions of different soil macro-fauna in cocoa-based agroforestry systems differed significantly. Differences in cocoa farmers’ perceptions of the different soil macro-fauna could be attributed to differences in age, farm experience, educational level, farm size and many others. Cocoa farmers’ identification of earth worms, ants, termites, millipedes, centipedes, and snails as major soil macro-fauna in cocoa-based agroforestry systems could be attributed to the easily identifiable nature of these soil macro-fauna when compared to others such as harvestmen and scorpions which are very much elusive. Mostly, biophysical studies have been carried out to identify soil macro-fauna in agricultural systems (Harvey et al., 2006; Moco et al., 2009, 2010; Huerta et al., 2009; Rahman et al., 2012; Deheuvels et al., 2014; Suarez et al., 2018; Mortimer et al., 2018; Suarez et al., 2019; Villanueva-Lopez et al., 2019; Prayogo et al., 2019; Dahlsjo et al., 2020). However, very limited research has been done on farmers’ indigenous knowledge of soil macro-fauna diversity and abundance and their contribution to soil fertility enhancement in cocoa-based agroforestry systems. This study is therefore timely and fills a knowledge vacuum.

Degree of soil macro-fauna diversity and abundance in cocoa-based agroforestry systems

Cocoa farmers perceived  the  level  of  soil  macro-fauna diversity in cocoa-based agroforestry systems differently. Most cocoa farmers perceived that soil macro-fauna diversity in cocoa-based agroforestry systems was high, with few cocoa farmers perceiving that soil macro-fauna diversity in cocoa-based agroforestry systems was very low. Cocoa farmers’ perceptions of the level of soil macro-fauna diversity in cocoa-based agroforestry systems differed significantly. Biophysical studies have shown that soil macro-fauna diversity is high in different organic/agro-ecological farming systems (Rousseau et al., 2014; Jagoret et al., 2014; Vanhove et al., 2016; Wartenberg et al., 2017; Tongkaemkaew et al., 2018; Suarez et al., 2018; Oliveira et al., 2018; Suarez et al., 2019; Marsden et al., 2020). This could be attributed to the presence of trees and the limited use of toxic agro-chemicals which are harmful to soil macro-fauna.

Cocoa farmers perceived the level of soil macro-fauna abundance in cocoa-based agroforestry systems in a diverse fashion. Earth worms, ants, millipedes, centipedes, spiders, harvestmen and scorpions were perceived by most cocoa farmers to have a high level of abundance in cocoa-based agroforestry systems. Crickets, woodlice, snails and slugs were perceived by most farmers to have an average abundance in cocoa-based agroforestry systems. Termites and beetles were perceived by most cocoa farmers to have a low abundance in cocoa-based agroforestry systems. A statistically significant difference existed between farmers’ perceptions of abundance of soil macro-fauna in cocoa-based agroforestry systems. Cocoa farmers’ perceptions of the abundance of earth worms, ants, millipedes, centipedes, spiders, harvestmen and scorpions could be attributed to the fact that these soil macro-fauna  are  frequently  seen  by the farmers during their daily farming activities. Meanwhile, soil macro-fauna such as crickets, woodlice, snails, slugs, termites and beetles, which were perceived by cocoa farmers to have average to low abundance, could be attributed to the fact that these soil macro-fauna are not frequently seen by the farmers during their daily activities on the farm. Significant differences in cocoa farmers’ perceptions of the abundance of soil macro-fauna could be attributed to farm experience, age, farm size, and educational level. Mainly biophysical studies have been undertaken to assess soil macro-fauna abundance in different agricultural systems (agroforestry inclusive). Most of these studies (Jose, 2009; Oke and Odebiyi, Nair, 2011; Jose, 2012; Asare et al., 2014; Carsan et al., 2014; Rousseau et al., 2014; Dumont et al., 2014; Mortimer et al., 2018; Niether et al., 2019; Wartenberg et al., 2020), have found varying degrees of abundance of soil macro-fauna in different agricultural systems. This study by focusing on cocoa-based agroforestry systems and making use of cocoa farmers’ local knowledge breaks away from the norm, which accounts for its originality.

Influence of soil macro-fauna diversity and abundance on soil fertility in cocoa-based agroforestry systems

Correlation and regression analyses showed the existence of a direct non-causal and causal relationship between soil macro-fauna diversity and soil fertility enhancement in cocoa-based agroforestry systems. A statistically significant direct non-causal and causal relationship was found to exist between different levels of soil macro-fauna diversity (very high soil macro-fauna diversity, high soil macro-fauna diversity, average soil macro-fauna diversity, low soil macro-fauna diversity, and very low soil macro-fauna diversity) and soil fertility enhancement in cocoa-based agroforestry systems. Thus, the higher the level of soil macro-fauna diversity in the cocoa-based agroforestry system, the higher the level of soil fertility; and the lower the level of soil macro-fauna diversity in the cocoa-based agroforestry system, the lower the level of soil fertility. As shown by most biophysical studies (Rousseau et al., 2014; Jagoret et al., 2014; Vanhove et al., 2016; Wartenberg et al., 2017; Tongkaemkaew et al., 2018; Suarez et al., 2018; Suarez et al., 2019; Marsden et al., 2020), soil macro-fauna diversity contributes enormously towards enhancing soil fertility in different agricultural systems owing to engineering role (aid in the decomposition of dead organic matter) played by soil macro-fauna. By laying emphasis on the cocoa-based agroforestry system and making use of cocoa farmers’ local knowledge, this study brings forth some originality.

A statistically significant direct relationship existed between the abundance of some soil macro-fauna (earth worms, ants, termites, beetles, crickets, woodlice, snails and slugs) and soil fertility enhancement  in  cocoa-based agroforestry systems. Although, there was a direct non-causal and causal relationship between the abundance of some soil macro-fauna (millipedes, centipedes, harvestmen, spiders and scorpions) and soil fertility improvement in cocoa-based agroforestry systems, there was no statistical significance. These findings imply that, as the abundance of earth worms, ants, termites, beetles, crickets, woodlice, snails and slugs increases in cocoa-based agroforestry systems, their contribution to soil fertility also increases. The relative abundance of millipedes, centipedes, harvestmen, spiders and scorpions also contributed towards increasing soil fertility in cocoa-based agroforestry systems (although not very significantly). Studies (mostly biophysical) have shown that the abundance of soil fauna in general and soil macro-fauna in particular, in different agricultural systems contribute towards enhancing soil fertility (Jose, 2009, 2012; Oke and Odebiyi, 2007; Nair, 2011; Asare et al., 2014; Carsan et al., 2014; Rousseau et al., 2014; Dumont et al., 2014; Mortimer et al., 2018; Niether et al., 2019; Wartenberg et al., 2020). This could be attributed to the role played by these soil macro-fauna as decomposers of dead organic matter. With focus on cocoa-based agroforestry systems and cocoa farmers’ local knowledge, this study has produced some novel findings.


 CONCLUSION

The findings of this study have proven that soil fertility is greatly influenced by soil macro-fauna diversity and abundance in cocoa-based agroforestry systems. From these findings, different soil macro-fauna were identified by cocoa farmers in cocoa-based agroforestry systems with the main being earth worms, ants, termites, millipedes, centipedes, and snails. Most cocoa farmers perceived that soil macro-fauna diversity in cocoa-based agroforestry systems was high and very high respectively, with few cocoa farmers perceiving that soil macro-fauna diversity in cocoa-based agroforestry systems was very low. Earth worms, ants, millipedes, centipedes, spiders, harvestmen and scorpions were perceived by most cocoa farmers to have a high level of abundance in cocoa-based agroforestry systems. Crickets, woodlice, snails and slugs were perceived by most farmers to have an average abundance in cocoa-based agroforestry systems. Termites and beetles were perceived by most cocoa farmers to have a low abundance in cocoa-based agroforestry systems. Correlation and regression analyses showed the existence of a statistically significant direct non-causal and causal relationship between soil macro-fauna diversity and soil fertility enhancement in cocoa-based agroforestry systems, implying that the higher the diversity, the higher the level of soil fertility and the lower the diversity, the lower the level of soil fertility.

Concerning  soil   macro-fauna  abundance,  correlation  and regression analyses revealed the existence of a statistically significant direct non-causal and causal relationship between soil macro-fauna abundance (that is, for earth worms, ants, termites, beetles, crickets, woodlice, snails and slugs) and soil fertility enhancement in cocoa-based agroforestry systems, implying that the greater the abundance of these soil macro-fauna, the greater the fertility of the soil. It is therefore recommended that measures be taken to ensure soil macro-fauna diversity and abundance in order to enhance the fertility of the soil in cocoa-based agroforestry systems.


 POLICY RECOMMENDATIONS

Four policy recommendations arise from the findings of this study.

First, most cocoa farmers perceived that soil macro-fauna diversity in cocoa-based agroforestry systems was high, with few cocoa farmers perceiving that soil macro-fauna diversity in cocoa-based agroforestry systems was very low. Thus, policies geared towards the sustainability of cocoa-based agroforestry systems should look into this and seek for ways to maintain this for as long as possible.

Secondly, earth worms, ants, millipedes, centipedes, spiders, harvestmen and scorpions were perceived by most cocoa farmers to have a high level of abundance in cocoa-based agroforestry systems. Crickets, woodlice, snails and slugs were perceived by most farmers to have an average abundance in cocoa-based agroforestry systems. Termites and beetles were perceived by most cocoa farmers to have a low abundance in cocoa-based agroforestry systems. Policy makers should take a keen look at this to see which soil macro-organisms deserve much care less they go extinct.

Correlation and regression analyses showed the existence of a statistically significant direct non-causal and causal relationship between soil macro-fauna diversity and soil fertility enhancement in cocoa-based agroforestry systems, implying that the higher the diversity, the higher the level of soil fertility and the lower the diversity, the lower the level of soil fertility. Policy makers should craft policies that seek to ensure more diversity of these soil macro-fauna in cocoa-based agroforestry systems which could be through measures that ban the use of harmful agro-chemicals.

Concerning soil macro-fauna abundance, correlation and regression analyses revealed the existence of a statistically significant direct non-causal and causal relationship between the level of soil macro-fauna abundance (that is, for earth worms, ants, termites, beetles, crickets, woodlice, snails and slugs) and soil fertility enhancement in cocoa-based agroforestry systems, implying that the greater the abundance of these soil macro-fauna, the greater the fertility of the soil.

Policy makers should seek to ensure the abundance  of these soil macro-fauna in cocoa-based agroforestry systems through actions like the banning of harmful agro-chemical use on farms.


 CONFLICT OF INTERESTS

The authors have not declared any conflict of interests.



 REFERENCES

Amare D, Wondie M, Mekuria W, Darr D (2018). Agroforestry of smallholder farmers in Ethiopia: Practices and benefits. Small-scale Forestry18 (1):39-56.
Crossref

 

Asaah EK, Tchoundjeu Z, Leakey RRB, Takousting B, Njong J, Edang I (2011). Trees, agroforestry and multifunctional agriculture in Cameroon. International Journal of Agricultural Sustainability 9(1):110-119.
Crossref

 

Asare R, Afari-Sefa V, Osei-Owusu Y, Pabi O (2014). Cocoa agroforestry for increasing forest connectivity in a fragmented landscape in Ghana. Agroforestry Systems 88:1143-1156.
Crossref

 

Awazi NP, Avana TML (2020). Agroforestry as a sustainable means to farmer-grazier conflict mitigation in Cameroon. Agroforestry Systems 94(6):2147-2165. 
Crossref

 

Awazi NP, Tchamba NM (2019). Enhancing agricultural sustainability and productivity under changing climate conditions through improved agroforestry practices in smallholder farming systems in sub-Saharan Africa. African Journal of Agricultural Research 14(7):379-388.
Crossref

 

Awazi NP, Tchamba NM, Avana TML (2019). Climate change resiliency choices of small-scale farmers in Cameroon: determinants and policy implications. Journal of Environmental Management 250:109560.
Crossref

 

Awazi NP, Tchamba NM, Temgoua LF (2020). Enhancement of resilience to climate variability and change through agroforestry practices in smallholder farming systems in Cameroon. Agroforestry Systems 94:687-705. 
Crossref

 

Awazi NP, Tchamba NM (2018). Determinants of small-scale farmers' adaptation decision to climate variability and change in the north-west region of Cameroon. African Journal of Agricultural Research 13(12):534-543.
Crossref

 

Cardinael R, Mao Z, Chenu C, Hinsinaer P (2020). Belowground functioning of agroforestry systems recent advances and perspectives. Plant and Soil 453:1-13.
Crossref

 

Carsan S, Stroebel A, Dawson I, Kindt R, Mbow C, Mowo J, Jamnadass R (2014).Can agroforestry option values improve the functioning of drivers of agricultural intensification in Africa? Current Opinion in Environmental Sustainability 6:35-4.
Crossref

 

Dahlsjo CAL, Stiblik P, Jaklova J, Zidek M, Huaycama WJ, Lojka B, Houska J (2020).The local impact of macro-fauna and land use intensity on soil nutrient concentration and exchangeability in lowland. Biotropica 52(2):242-251.
Crossref

 

Deheuvels O, Rousseau GX, Quiroga GS, Franco MD, Cerda R, Mendoza SJV, Somarriba E (2014). Biodiversity is affected by changes in management intensity of cocoa-based. Agroforestry Systems 88:1081-1099.
Crossref

 

Dumont ES, Gnahoua G-M, Ohouo L, Sinclair FL, Vaast P (2014). Farmers in Cote d'Ivoire value integrating tree diversity in cocoa for the provision of ecosystem services. Agroforestry systems 88:1047-1066.
Crossref

 

Harvey CA, Gonzalez J, Somarriba E (2006). Dung beetle and terrestrial mammal diversity in forests, indigenous agroforestry systems and plantain monocultures in Talamanca, Costa Rica. Biodiversity and Conservation 15:555-585.
Crossref

 

Huerta E, Kampichler C, Geissen V, Ochoa-Gaona S, de Jong B, Hernandez-Daumas S (2009).Towards an ecological index for tropical soil quality based on soil macro-fauna. Pesquisa Agropecuaria Brasileira 44:1056-1062.
Crossref

 

Jagoret P, Kwesseu J, Messie C, Michel-Dounias I, Malezieux E (2014). Farmers' assessment of the use value of agro-biodiversity in multispecies systems An application to cocoa agroforests in Central Cameroon. Agroforestry Systems 88:983-1000.
Crossref

 

Jagoret P, Michel-Dounais I, Malezieux E (2011). Long term dynamics of cocoa agroforests: a case study in central Cameroon Agroforestry Systems 81:267-278.
Crossref

 

Jagoret P, Michel-Dounias I, Snoeck D, Ngnogue HT, Malezieux E (2012). Afforestation of savannah with cocoa agroforestry systems: a small-farmer innovation in central Cameroon. Agroforestry Systems 86:493-504.
Crossref

 

Jagoret P, Snoeck D, Bouambi E, Ngnogue HT, Nyasse S, Saj S (2018) Rehabilitation practices that shape cocoa agroforestry systems in Central Cameroon:key management strategies for long term exploitation. Agroforestry Systems 92:1185-1199.
Crossref

 

Jose S (2009).Agroforestry for ecosystem services and environmental benefits: an overview. Agroforestry Systems 76:1-10.
Crossref

 

Jose S (2012)Agroforestry for conserving and enhancing biodiversity. Agroforestry Systems 85:1- 8.
Crossref

 

Laird SA, Awung GL, Lysinge RJ (2007).Cocoa farms in the mount Cameroon region: biological and cultural diversity in local livelihoods Biodiversity Conservation16:2401-2427.
Crossref

 

Leakey RRB (2017).Socially Modified Organisms in Multifunctional Agriculture - Addressing the Needs of Smallholder Farmers in Africa. Archives of Crop Science 1(1):20-29.
Crossref

 

Leakey RRB (2019). A holistic approach to sustainable agriculture: trees, science and global society In: Mosquera-Losada, MR and Prabhu, R (eds), Agroforestry for sustainable agriculture, Burleigh Dodds Science Publishing, Cambridge, UK, 2019,(ISBN:978(1)78676 220 7).

 

Marsden C, Martin-Chave A, Cortet J, Hedde M, Capowiez Y (2020). How agroforestry systems influence soil fauna and their functions-a review. Plant and Soil 453:29-44.
Crossref

 

Moco MKS, da Gama-Rodrigues EF, da Gama-Rodrigues AC, Machado RCR, Baligar VC.(2009). Soil and litter fauna of cacao agroforestry systems in Bahia, Brazil. Agroforestry Systems 76:127-138.
Crossref

 

Moco MKS, Gama-Rodrigues EF, Gama-Rodrigues AC, Machado RCR, Baligar VC (2010). Relationships between invertebrate communities, litter quality and soil attributes under different cacao agroforestry systems in the south of Bahia, Brazil. Applied Soil Ecology 46:347- 354.
Crossref

 

Mortimer R, Saj S, David C (2018). Supporting and regulating ecosystem services in cocoa agroforestry systems. Agroforestry Systems 92:1639-1657.
Crossref

 

Mukete N, Li Z, Mukete B, Bobyeg P (2018).Cocoa production in Cameroon: A socio-economic and technical efficiency perspective. International Journal of Agricultural Economics 3(1):1-8.
Crossref

 

Nair PKR (2011). Agroforestry systems and environmental quality: introduction. Journal of environmental quality 40(3):784-790.
Crossref

 

Nfinn T (2005). Cocoa production in Cameroon. AFTA Conference Proceedings 5 pages.

 

Niether W, Schneidewind MF, Schneider M, Armengot L (2019). Below and above ground production in cocoa monocultures and Agroforestry systems. Science of the Total Environment 657:558-567.
Crossref

 

Noordwijk VM, Duguma L, Dewi S, Leimona B, Catacutan D, Lusiana B, Oborn I, Hairiah K, Minang P, Ekadinata A, Martini E, Degrande A,

 

Prabhu R (2019). Agroforestry into its fifth decade: local responses to global challenges and goals in the Anthropocene in book: Sustainable Development through Trees on Farms: Agroforestry in its Fifth Decade (pp.347-368) Publisher: World Agroforestry (ICRAF), Bogor, Indonesia

View

 

Oke DO, Odebiyi KA (2007). Traditional cocoa-based agroforestry and forest species conservation in Ondo State, Nigeria. Agricultural Ecosystem Environment 122:305-311.
Crossref

 

Oliveira PHG, Gama-Rodrigues AC, Gama- Rodrigues EF, Sales Multiple Virtual Storage (2018). Litter and soil-related variation in the functional group abundances in cocoa agroforests using structural equation modeling Ecological Indicators 84:254-262.

Crossref

 

Plan Communal de Developpement-PCD Melong (2012). Melong Council Development Plan. Working Document 154 p.

 

Prayogo C, Sholehuddin N, Hassan EZ, Putra S, Rachmawati R (2019). Soil macro-fauna diversity and structure under different management of pine-coffee agroforestry system. Journal of Degraded and Mining Lands Management 6(3):1727.
Crossref

 

Quandt A, Neufeldt H, McCabe JT (2018). Building livelihood resilience: what role does agroforestry play? Climate for Development in Africa.
Crossref

 

Rahman PM, Varma RV, Sileshi GW (2012). Abundance and diversity of soil invertebrates in annual crops, agroforestry and forest ecosystems in the Nilgiri biosphere reserve of Western Ghats, India. Agroforestry Systems 85:165-177.
Crossref

 

Rousseau GX, Deheuvels O, Arias IR, Somarriba E (2012).Indicating soil quality in cocoa-based agroforestry systems and old growth forests: the potential of soil macro-fauna assemblage. Ecological Indicators 23:535-543.
Crossref

 

Rousseau L, Fonte SJ, Tellez O, Van der Hoek R, Lavelle P (2014). Soil macro-fauna as indicators of soil quality and land use impacts in smallholder agro-ecosystems of western Nicaragua. Ecological Indicators 27:71- 82.
Crossref

 

Sonwa DJ, Nkongmeneck AB, Weise SF, Tchatat M, Adesina AA, Janssens MJ (2007). Diversity of plants in cocoa agroforests in the humid forest zone of southern Cameroon. Biodiversity and Conservation 16:2385- 2400.
Crossref

 

Suarez LR, Audor LCU, Salazar JCS (2019). Formation of macroaggregates and organic carbon in cocoa agroforestry systems. Floresta e Ambiente 26(3):2019.
Crossref

 

Suarez LR, Josa YTP, Samboni EJA, Cifuentes EHDB, Salazar JCS (2018). Soil macro-fauna under different land uses in the Colombian Amazon. Pesquisa Agropecuaria Brasileira 53:1383-1391.
Crossref

 

Tankou CM (2015).The Cameroon cocoa story The "Supply Change - Make Supermarkets fair" project sponsored by the European Union.

 

Tankou CM, de Snoo GR, Persoon G, de longh HH (2017). Evaluation of smallholder farming systems in the Western Highlands of Cameroon. IOSR Journal of Engineering 7(1):1-11.
Crossref

 

Tongkaemkaew U, Sukkul J, Sumkhan N, Panklang P, Brauman A, Ismail R (2018). Litter, litter decomposition, soil macro-fauna, and nutrient contents in rubber monoculture and rubber-based agroforestry plantations. Forest and Society 2:138-149.
Crossref

 

Tsufac AR, Yerima BPK, Awazi NP (2019). Assessing the role of agroforestry in soil fertility improvement in Mbelenka-Lebialem, Southwest Cameroon. International Journal of Global Sustainability 3(1):115-135.
Crossref

 

Vanhove W, Vanhoudt N, Van Damme P (2016). Effect of shade tree planting and soil management on rehabilitation success of a 22 year old degraded cocoa. (Theobroma cacao L) plantation. Agriculture Ecosystems and Environment 219:14-25.
Crossref

 

Villanueva-Lopez G, Lara-Perez LA, Oros-Ortega I, Ramirez-Barajas PJ, Casanova-Lugo F, Ramos-Reyes R, Aryal DR (2019). Diversity of soil macro-arthropods correlates to the richness of plant species in traditional agroforestry systems in the humid tropics of Mexico Agriculture, Ecosystems and Environment 286:106658.
Crossref

 

Wartenberg AC, Blaser WJ, Gattinger A, Roshetko JM, Van Noordwijk M, Six J (2017). Does shade tree diversity increase soil fertility in cocoa plantations?. Agriculture, Ecosystems and Environment 248:190-199.
Crossref

 

Wartenberg AC, Blaser WJ, Gattinger A, Roshetko JM, Van Noordwijk M, Six J (2020). Soil fertility and Theobroma cacao growth and productivity under commonly intercropped shade-tree species in Sulawesi, Indonesia. Plant and Soil 453:87-104.
Crossref

 




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