Open access peer-reviewed chapter

# Plant Diversity, Ecological Services, and Carbon Stock Assessment in Cocoa Agroforestry Plantations of Forest and Savannah Transitions in Cameroon

By Patrick Bustrel Choungo Nguekeng, René Bernadin Jiofack, Lucie Temgoua, Irène Franceline Mbouwe, Armelle Verdiane Tchanou and Zacharie Tchoundjeu

Submitted: September 6th 2017Reviewed: April 9th 2018Published: November 14th 2018

DOI: 10.5772/intechopen.77093

## Abstract

This study was carried out in cocoa-based agroforestry systems in Mbam and Inoubou department, Center Region, Cameroon. The study aimed at assessing the plant species diversity, ecological services, and carbon sequestration potentials of diverse trees associated in cocoa agroforestry systems. Twenty-seven sampling plots of 100 × 20 m were established in cocoa agroforestry systems in three villages. Our results registered the occurrence of 238 plant species grouped into 16 families in the sampled area. Sterculiaceae, Burseraceae, and Moraceae were the three dominant families. The species richness and diversity that were assessed using the Shannon index were 0.62, 0.66, and 0.68, respectively, while using the Simpson index, they were 1.421, 1.409, and 0.349, respectively, for Mouko, Rionong, and Nyamsong 3. Carbon stock sink was also estimated at 92.03, 55.18, and 46.83 tC/ha. Our results indicate a high flora diversity in cocoa-based agroforests especially with respect to fruit trees where Tetracarpidium conophorum is introduced. The total amount of CO2/ha per village plots is estimated at 337.46, 202.32, and 171.71 tCO2/ha. Then, the ecological services that should be paid according to 10 US$per ton of carbon are evaluated at 3374.6, 2023.2, and 1717.1 US$ to the owner of the selected farms.

### Keywords

• carbon sequestration
• REDD+
• agroforestry systems
• climate change
• mitigation

## 1. Introduction

The concept of REDD+ is always limited to emissions due to deforestation and the increase of carbon sink in land use systems. In order to contribute to the fight against climate change issues in Cameroon, we should develop suitable proposals which target the Clean Development Mechanism (CDM) [1]. The particularity of these projects is to reduce the emission of CO2.

Agroforestry can be defined as a collective name for land use systems and technologies where woody perennials (trees, shrubs, palms, bamboo, etc.) are deliberately used on the same land management units as agricultural crops [2]. Agroforestry can provide benefits as (i) linking poor households to markets for high-value fruits, (ii) balancing improved productivity with the sustainable management of natural resources, and (iii) maintaining or enhancing the supply of environmental services in agriculture and landscapes for water, soil health, carbon sequestration, and biodiversity conservation [3, 4]. In our land use systems, there are non-timber forest products (NTFPs). They are considered with higher potentialities as medicinal and economic values which contribute to break the chain of poverty in rural areas [5, 6]. T. conophorum (Photograph 1) is a local vine from the Euphorbiaceae family which is also called African walnut, cashew nut, conophor seeds, or conophor nuts [7, 8, 9]. This species has several properties such as cholesterol-lowering and triglyceride-lowering properties which have been reported [10]. The nutritional properties of seeds have also been fully demonstrated [11, 12, 13].

During some inventories, it was estimated that tropical forests can store more than 200 t C/ha in trees [14]. Carbon management in agroforestry systems is a new global concern to mitigate the increased concentration of greenhouse gases in the atmosphere in Congo Basin countries. Reforestation cover and finding low-cost methods to sequester carbon in land use systems are emerging tools. As trees grow and their biomass increases, they absorb carbon from the atmosphere and store in the plant tissues and roots. We need to contribute to the Reduction of Emissions derived from Deforestation and Degradation (REDD+). Carbon stock sink varies following the type of trees, and it has been demonstrated that diameter at breast height (DBH) and height are important factors in carbon stock sink variation [15]. Several studies were carried out on the biomass and carbon stock assessment in all ecosystems all over the world [16, 17, 18, 19, 20]. These aspects have been partially studied, and there is only a limited amount of work which upholds the notion of the potential of diversity and associated species with Tetracarpidium conophorum in agroforestry systems which can contribute to mitigate effects of climate change and improve livelihood options of local farmers. At this time when natural ecosystems are disappearing at an alarming rate, it is clearly necessary today to outline the carbon sequestration potential of agroforestry systems, so that their compensatory role in the mitigation process of climate change be made known in Cameroon.

## 2. Materials and methods

### 2.1. Study area

The study was carried out in the Mbam and Inoubou department in Cameroon (Figure 1) which appears to be a transitional area covered by forest and savannah. The main cultivation of species there is cocoa plantation. This area is located between 4′39 and 4′49 north and then 11′4 and 11′19 east. Altitude varies from 600 to 900 m [21]. We choose this site because it is located near Yaounde, which includes several markets around where the conophor nuts can be found. Secondly, it is classified among the main area in terms of productivity of T. conophorum fruit in Cameroon [13]. There are many vegetal formations that belong to Sterculiaceae (Pterygota macrocarpa, Sterculia tragacantha, Cola gigantea, Cola altissima, Cola cordifolia, Triplochiton scleroxylon, Mansonia altissima, etc.) and Ulmaceae (Celtis zenkeri, Celtis tessmannii) [22].

### 2.2. Data collection

#### 2.2.1. Floristic inventories

Floristic inventories were performed in cocoa-based agroforestry plantations where the liana (T. conophorum) is introduced for several purposes. Data were collected in nine sample plots of 2000 m2 in each sample village. Trees with a DBH > 5 cm were also assessed with the aim of evaluating the typology of cocoa agroforests associated with liana cultivation. In each plot, species were identified with the use of identification tool keys using various books [23, 24, 25] and various volumes of flora of Cameroon. Figure 2 illustrates the experimental design of inventories carried out in the various cocoa agroforestry sample plots where we record the presence of T. conophorum.

#### 2.2.2. Aboveground biomass (AGB)

AGB was performed using the methodology described by measuring carbon stock manual [26]. This method illustrated by Figure 3 consists in delimiting a main plot (2000 m2) where all trees with a dbh ≥ 30 cm have been recorded. Another subplot of 40 × 5 m was designed in order to assess trees (30 < dbh < 5 cm). In the subplot 40 × 5 m, other plots of 1 × 1 m were designed in order to collect litter and herbs of understory.

### 2.3. Data analysis

#### 2.3.1. Floristic inventories

According to the following formula, we calculated structural parameters and determined the dominant species importance value index (IVI).

• Frequency was estimated for each species with the formula F = (number of plot containing × species/total number of plot) × 100.

• Abundance was estimated for each species using the formula A = (ni/N) × 100, where “ni” is the number of individuals of species i and “N” is the total of the flora.

• The diversity was calculated using the Shannon index to compare the data of various sample sites in terms of diversity of plant species. ISH = −Σ pi log2 (pi), where “pi” is the frequency of species i (ni/N), “ni” is the number of individuals of species i, and “N” is the number of individuals of all species.

• IVI = frequency + abundance + dominance [27].

Diversity parameters were also calculated according to the following formula:

• Shannon index (H′) measures uncertainty about species belonging to a randomly selected individual in the sample. It is expressed according to the proportions of each species: The formula is H′ = −Σ = pi log2 (pi) with “pi” proportion of the species “i”.

• Simpson index (D’) is a measure of dominance and expresses the probability that two individuals drawn at random from an infinite population belong to the same species. It is expressed from the “pi” frequencies of species where D’ = Σpi2. The value 0 of this index indicated a maximum diversity, while value 1 represents the minimum diversity.

#### 2.3.2. Aboveground biomass (AGB)

The methodology used in this study was described in the document [1, 28] in cocoa agroforestry systems. Biomass was estimated using allometric model. We used allometric model of Chave [29] to evaluate carbon stock sink sequestration by each tree species. The formula is AGB = Exp (−2.977 + LN (DBH2Hρ)) where “ρ” is the wood density and “DBH” is the diameter at breast height. We, respectively, use the density of all those trees which correspond to each plant species according to wood density database of the Food and Agricultural Organization (FAO). The total carbon stock sink in the selected trees was estimated by summing the values at the level of timbers, herbs, and litters.

### 4.3. Environmental services and carbon sinks

For this work, the estimated percentage of carbon stock sink sequestrated per locality varies as 92.03, 55.18, and 46.83 tC/ha, respectively, to Mouko, Rionong, and Nyamsong 3. Those values represent less than one-fourths of the biomass estimated in some selected agroforestry systems around natural forest stands in the Dja biosphere reserve in the East province of Cameroon. We can say that density and number of species can greatly impact the quantity of carbon sink in some land uses systems (LUS). Diversification is an important tool which contributes to mitigate effects of climate change and climate modifications [39, 34]. Considering the fact that each plant/tree specie can store a specific quantity of carbon through leaves and roots, it is therefore recommended to plant more species in our LUS in order to gather more carbon. Our results obtained on the carbon sink potential are important like the others conducted in cocoa agroforestry systems around the world. Results obtained in our study are superior in Mouko village (92.03 tC/ha), while different from the results found in [40] where the authors revealed an amount of 68.12 tC/ha at Kédia and 76.99 tC/ha at Ediolomo. These results demonstrated that carbon stock sink in cocoa-based agroforestry plantations is higher when there is more fruiting species and other useful tree species for the local producer. It can be explained by the fact that carbon sink depends on several parameters such as the quality and quantity of species which are introduced for diversification or shade purposes. Following this, a study was conducted on carbon stocks [34], and it reveals a higher amount of carbon sink (197.5 tC/ha) in the cocoa agroforests of Bokito in the same geographical area with the sampled localities. This amount of carbon is higher because during the creation of cocoa farms and local producers/farmers introduce several species (fruiting species and medicinal, etc.) in order to provide many services in the farm and then conserve more land for land restoration and protection. The presence of several species in our LUS increases the total quantity of CO2, which appears to be very high, thus explaining an important ecological and ecosystem service provided by those cocoa agroforests to local farmers and land owners.

## 5. Conclusion

This study was carried out in order to assess plant diversity and carbon stock assessment by some selected cocoa-based agroforests in the Mbam and Inoubou department of Cameroon. Then, the interest in this work was to show that some tree species introduced in cocoa-based agroforests can store an important quantity of carbon which will contribute to fight, reduce climate change modifications, and diversify farmer’s income during the year in order to improve livelihood options. We also estimate ecological services which can be derived from the utilization of those land use systems depending on the trees which have been integrated or associated according to farmer’s preferences and needs. We have shown that percentage of fruiting species within the villages was very high, and this demonstrates that cocoa-based agroforestry plantations sometimes need associated trees in order to provide shade for cocoa development. Moreover, we can recommend that cocoa agroforestry systems can also play an important key role in biodiversity conservation. Also, different species were found to be more or less as reported by other studies using the same methodologies, and we can note that characterization allows us to demonstrate the various family species of trees associated with cocoa agroforestry systems in the Mbam and Inoubou department.

## Acknowledgments

The Congo Basin Grant Program (CBGP) has supported this research through a fellowship awarded to M. Patrick Bustrel Choungo through the Conservation Action Research Network (CARN). The authors of this paper will like to thank IDEA WILD Foundation for research materials support and also all farmers of the Department of Mbam and Inoubou who helped us to realize this study and allow us to work in their cocoa-based agroforests. We will finally give thanks to all the farmers who have accepted to answer our questionnaire sheets during this study and anonymous reviewers for their comments in order to improve the quality of the manuscript.

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© 2018 The Author(s). Licensee IntechOpen. This chapter is distributed under the terms of the Creative Commons Attribution 3.0 License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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Patrick Bustrel Choungo Nguekeng, René Bernadin Jiofack, Lucie Temgoua, Irène Franceline Mbouwe, Armelle Verdiane Tchanou and Zacharie Tchoundjeu (November 14th 2018). Plant Diversity, Ecological Services, and Carbon Stock Assessment in Cocoa Agroforestry Plantations of Forest and Savannah Transitions in Cameroon, Forest Biomass and Carbon, Gopal Shukla and Sumit Chakravarty, IntechOpen, DOI: 10.5772/intechopen.77093. Available from:

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