1. Introduction
An estimated 570 million farms throughout the world are considered to be small or family operated [
1]. Smallholder farms are characterized by being less than 10 ha in size [
2]; and being family-operated, with limited or no hired labour. In many cases, the smallholders live with poverty, food insecurity, and with limited access to markets and services [
3,
4]. Despite their socioeconomic and environmental limitations, smallholder farmers play an important role in food supply chains and economies at the local, regional and global level, especially in the developing world, e.g., [
1,
2,
3,
4,
5,
6]. Lowder et al. [
1] explain the importance of smallholder farmers, reporting that about 75% of global agricultural land is occupied by smallholders or family farms, which are also responsible for the majority of the world’s agricultural production. Consequently, smallholder farmers have an important influence in the process of land-use/land-cover change and agrobiodiversity conservation [
5].
In the Latin American and Caribbean (LAC) context, recent evidence indicates that the situation and importance of smallholder farmers supporting food production systems, livelihoods of rural and urban households, and local and regional economies, have some important similarities and significant differences compared to the regional and global context [
1,
4,
6,
7]. One major difference between LAC and other regions is the greater agricultural land grabbing resulting in the consolidation of large landholdings in the hands of landlords and agribusiness companies [
1,
7]. The higher land consolidation and increasing land grabbing in LAC [
8,
9] is reducing the possibilities for smallholder access to agricultural land, and usually accelerates the expansion of agricultural frontiers, fragmentation and overexploitation of existing agricultural land and water resources [
10]. The marginalization and poverty of smallholder farmers’ households, also increases inequality and reduced access to farmland and other assets for production, such as access to technology, information, credit and technical support [
10,
11]. In line with the global context, smallholder farmers in LAC play a key role in supporting food production systems and local and regional economies [
12]. Altieri et al. [
13] reported that smallholder farmers in LAC represents a population of about 66 million people, including 40–55 million indigenous people who are responsible for the production of the main staple foods consumed in the region; including maize, beans, and potatoes. A study conducted in six LAC countries by Soto et al. [
6] found that smallholder farming employed between 57% of the agricultural sector and 77% of the rural employment.
In the case of Ecuador, the situation of smallholder farmers appears similar to the general trends in the LAC region. The increasing trend of land consolidation, land grabbing, and unequal distribution of agricultural lands and other assets for production are threatening the maintenance and improvement of smallholders’ livelihoods [
14,
15,
16]. Agricultural land consolidation is also a significant environmental and socioeconomic problem in Ecuador. Approximately 76% of farmers are smallholders (with farms <10 ha), but they occupy only 12% of the agricultural land. In contrast, 6% of farmers have large holdings (>50 ha) and occupy 61% of the land [
15,
17,
18]. Land consolidation and grabbing are associated with the concentration of other productive assets, especially water, which is also concentrated in few and large landholdings [
14,
15,
19,
20]. The accumulation of land and water as primary productive assets is closely related to the increase of marginalization, poverty and malnutrition, which are common problems experienced by Ecuadorian smallholders [
15,
21]. The unequal access to land and water is strongly connected with socioeconomic and cultural discrimination, whereby agricultural land areas with high levels of fragmentation commonly coincide with areas having high poverty levels, and where most indigenous people live. These areas are located mainly in the highlands, which are characterized by steep slopes and harsh environmental conditions [
14,
15,
16].
Smallholder farmers in Ecuador play an important role in local food supply for millions of rural and urban households and livelihoods. Data from the last agricultural national census 2000 [
18] (
Figure A1) and other publications [
6,
12,
19,
21,
22,
23], indicate that most of the staple food consumed in the country is produced by smallholder farmers, giving them a strategic role supporting agrobiodiversity, food security and food sovereignty. Although there is a lack of information detailing the contribution of smallholder farmers to the economy, official data shows that the agriculture sector, which includes smallholdings, contributes 9% to total GDP [
15,
24], 15.4% of the non-petroleum GDP, and directly employs about 70% of rural workers [
15]. Furthermore, the smallholder farming sector employs about 16% of permanent and 40% of non-permanent hired labour in the country [
18]. Considering that smallholder farming mainly uses family labour, these figures represent an important contribution by the smallholder sector to rural employment and livelihoods in Ecuador.
In this context, and taking into account that smallholder farming in the developing world is also a very culturally and ecologically heterogeneous sector [
25], the aim of this paper is to provide a socioeconomic and environmental analysis of how different types of production systems contribute to the sustainability of smallholder livelihoods in the tropical highlands. The analysis compares smallholder farmers’ perceptions of the main biophysical and socioeconomic components of the farming systems that support their livelihoods. A comparison is made within and between two types of smallholder production systems; agroforestry systems (AFS) and conventional agricultural systems (CAS). CAS are commonly found in the Indigenous Territory of Kayambi People (ITKP), while AFS are less practiced but there is an increasing interest of smallfarmer groups and local institutions, on the implementation of this type of farming systems. The main element differentiating AFS from CAS in this study is the proportion of the farm area covered by trees or shrubs (described in detail in
Section 2.2), which influences the biophysic and socioeconomic functioning of the farming system [
26].
The main research question addressed in this study is: How sustainable are smallholder AFS and CAS in the ITKP, Ecuador? This question will be addressed through two sub-questions, which are: (1) What are the main biophysical and socioeconomic characteristics and differences between current AFS and CAS? and (2) Which system provides better opportunities to enhance sustainable smallholder farmers’ household incomes and livelihoods?
This paper presents a simplified multidisciplinary case study and contributes towards an improved understanding of the structure and dynamics that maintain and enhance sustainable livelihoods of smallholder farmers in highlands.
2. Materials and Methods
2.1. Study Area
The research area was located in the Northern Highland Andes of Ecuador as part of the ITKP (
Figure 1). The biophysical and socioeconomic conditions, and problems affecting smallholders in the study area are similar, and in most cases are worse than the conditions and problems of other highland smallholders throughout the country (
Figure 2). The Kayambi’s territory includes approximately 1329 km² [
27], distributed mainly along the rural highlands of three provinces, six cantons, 16 parishes and 168 communities [
28,
29,
30]. The territory covers an altitude range of 2000 (low valleys) to 5790 m (Cayambe Volcano), along the eastern and western volcanic mountain chains and between the inter-Andean valleys. The Inter-Andean valleys are the lower areas between the two mountain chains and are characterized by the flat or low-sloping topography, while the hillsides are highly eroded with high slopes and little flat land [
31]. These geomorphological and topographic features contribute to the formation of a variety of bioclimatic and biotic zones [
32,
33].
The ITKP includes areas under agricultural production interspersed with natural and semi-natural native ecosystem remnants, especially highland grasslands known locally as “Páramo”. The soils in the ITKP are classified as andisols, mollisols and inceptissols, based on volcanic ash and distinguished by their productivity and fertility [
34]. The rainy season usually occurs from September to April with a mean annual rainfall ranging from 250 to 2000 mm [
32,
35]. The rainy season is commonly distributed in two rain periods, with the first occurring from October to November and the second from February to April. An intermediate period—summer—occurs from June to August and is characterized by dryness, strong winds and high solar radiation and temperature [
32]. The temperature varies from dry and temperate in low inter-Andean valleys with average annual temperatures of 12 to 18 °C, to the cold and humid highland grasslands with average annual temperatures of 3 to 6 °C [
36].
The ITKP has a population of 154,437, and according to the last national population census [
37], the mean concentration of self-recognized indigenous population in the territory is approximately 40% (
Table A1 in the
Appendix). The indigenous population is unevenly distributed, exceeding 70% in some areas, and more than 90% in others (
Table A1,
Appendix). The Kayambi’s territory is not an official administrative territory, but rather it can be considered as ancestral territory, managed by the Kayambi people according to their customs and recognized by local, national, international, public and private institutions. These figures reveal the indigenous cultural dominance in the territory, which has a significant influence over the management practices implemented in the traditional farming systems throughout the territory.
The study area was located in the highlands of the ITKP at an altitudinal range of 2500 to 3300 m. Areas such as these have special importance in terms of food security and production, at both the local and national levels. Most of the vegetables and tubers consumed locally and in other regions of the country are produced in these areas. Additionally, dairy farming is becoming one of the most expanded activities. Agricultural management in this area is predominantly with permanent and temporary monoculture crops such as pastures, potatoes, maize, broad beans, Andean lupin and vegetables, but in some places alternative management practices such as crop rotation, agroforestry and agrosilvopastoral systems are also implemented. Most of the crops are produced for home consumption and sale in local markets.
Highlands are transition zones with competition between farmland and highland grassland ecosystems, mainly distributed around Cayambe and Imbabura volcanoes, and in the uplands around Olmedo, Cangahua and Tabacundo villages (
Figure 1). The highland grasslands are considered a key Andean ecosystem due to their fresh water supply and regulation function. Currently the expansion and intensification of the agriculture and livestock farming activities are the main drivers of highland grassland depletion [
39].
The ITKP was selected because the territory fulfilled the main research requirements, which were: the existence of smallholder agroforestry and conventional agricultural farms in highlands, rural livelihoods based mainly on agricultural activities; and importantly, and the willingness of smallholder farmers and indigenous’ organizations to participate in the research. The favourable logistics and access to reach and work in the area (road infrastructure; security level and relatively easy access from the capital Quito) were also important considerations in the selection of the study area. The Kayambi People’s organisation showed a keen interest in the research and facilitated the access to the territory. The organisation also provided local technicians for logistic and cultural support. Before selecting the ITKP as study area, 15 key informant interviews with smallholder farmers and indigenous leaders were conducted in four highland provinces: Imbabura, Pichincha, Cotopaxi and Chimborazo.
2.2. Sampling and Data Collection
A sample of 60 smallholder farms were randomly selected from a total of 633 smallholder farms belonging to the local smallholder farmer organization RESSAK (Network for Food Sovereignty and Solidarity Economy of the Kayambi’s territory). These farms are part of approximately 12,000 smallholder farms in the ITKP [
40]. The process to select the 60 sample farms was conducted by the main author and three local technicians from the Kayambi People’s Organization who identified and chose the farms based on the following criteria: (1) farm size, up to 10 ha [
2]; (2) altitude, between 2500 and 4000 m.a.s.l; and (3) the percentage of farm area covered by trees and/or shrubs. Farms with 10% or more of the area covered by trees and/or shrubs in any spatial arrangement were considered AFS [
41], while farms with less than 10% tree and/or shrub cover were considered CAS.
The AFS and CAS samples were located in upper inter-Andean valleys, foothills and along gorges (
Figure 1). AFS sites were difficult to locate since they are a much less common than CAS (which includes mainly annual or seasonal croplands and permanent pastures), and they are scattered throughout the territory. Therefore it was not possible to use villages as a unit, because individual villages had very few households with AFS. This land use pattern is common for the whole Ecuadorian high Andes, where AFS have almost disappeared as a consequence of the influence of colonization, which also changed the production systems [
42].
To collect the data, 60 household surveys were conducted mostly with individual farmers, but in some cases with farming couples (73% of the farmers surveyed were women, 10% were men and the remaining 17% were couples). Surveys were conducted using semi-structured questionnaires designed to collect primary data about the main biophysical and socioeconomic characteristics of the farming systems (
Table A2 in
Appendix). The 60 surveys were conducted directly by the lead author of this paper from December 2015 to May 2016. The detailed questionnaires took an average of between three to four hours to conduct, and the data were directly entered into the database (
Table A2 in
Appendix). Depending on the farmer’s time availability, one or two visits to the farm were sometimes needed to complete the survey. The survey work started with direct observation of the farmland, in a process led by the farmer who was able to explain the main biophysical and socioeconomic characteristics of their farm in person. This was an important step to get the farmer involved in the survey and to improve the interaction between the farmer and the researcher. Many features related to the farmer’s household and livelihoods were also highlighted at this step of the survey. In addition, a set of photographs were taken to document each farmer’s plot.
The main variables considered in the biophysical component were agrobiodiversity, soil fertility and microclimate conditions inside the farm. Agrobiodiversity was divided into two categories, cultivated biodiversity and associated biodiversity, in order to establish the composition and main characteristics of agrobiodiversity within and between the AFS and CAS. Cultivated biodiversity includes all species, cultivars and breeds introduced and managed by the farmer, which play an important role maintaining food security-sovereignty and enhancing cash income generation. Cultivated biodiversity was analysed in detail through 11 subcategories. In complement, the associated biodiversity category considers the wild plant and animal species commonly found and used in the farming system. The analysis of associated biodiversity was essential to establish its importance for the ecological functionality of the farming system and also to determine its contribution to food security (subsistence) and income generation of smallholders. The method used by the farmers to register and estimate the number of animals and plant species was based on a progressive checklist. The checklist was made as follows: in the first interview the farmer was asked about the species used in the different categories of agrobiodiversity. Every species, cultivars and breeds described by the farmer was registered in the questionnaire matrix (
Table A2 in
Appendix) and it represented the starting checklist. In the subsequent interviews, additions were made to the list when the farmer indicated new species, varieties and breeds.
To establish the soil fertility conditions, the main chemical, physical and biological parameters were measured and evaluated through basic soil laboratory analysis (
Table A3 in
Appendix). The variables for microclimate conditions inside the farm included temperature, humidity and wind velocity (
Table A4 in
Appendix). For the analysis of soil fertility and microclimate conditions, a subsample of 16 farms were chosen randomly from the 60 sample farms and included eight AFS and eight CAS. Only 16 farms were chosen as subsamples due to time and budget limitations. The microclimatic conditions were measured using the Davis Vantage Pro2 micro weather station. The weather station was located strategically in the middle of the farm in order to provide an extensive microclimate measurement. Microclimate measurements were automatically logged every 30 min during a seven day period in each farm.
For the socioeconomic component, the main variables considered were livelihoods, income levels, agrobiodiversity usage, land tenure and irrigation sources (
Table A2 in
Appendix). To categorise and analyse the livelihoods, farmers were asked to describe their main livelihood activities and prioritise them, starting from the activity which generated the highest cash income. The prioritised livelihood activities represented the key data for the identification of the main livelihood categories. Complementary to the livelihood activities analysis, farmers were asked about the contribution of on-farm and off-farm income activities to the household economy. On-farm income activities are related mostly to the commercialisation of farm products and dairy farming, while off-farm income activities are linked to wages obtained from off-farm work, usually related to the construction and fresh cut-flower industries. Based on the basic salary (BS) for Ecuador (1 BS = 375 USD in 2016–2017), incomes were classified according to three levels (high, moderate and low). High income represented more than 1 BS per month, while moderate income was 1 BS, and low income indicates less than 1 BS.
For the analysis on how agrobiodiversity contributes to maintain and enhance the smallholder farmers’ livelihoods and household economies, the species of cultivated and associated biodiversity were classified in two main use categories: commercial and subsistence-functional species. A species was considered commercial when the species, or a derived product, was used mainly in the provision of cash income rather than providing basic household needs (usually food, medicine or fodder). On the other hand, subsistence or functional species were species used by farmers mostly to fulfil basic needs, or species that constitute an intrinsic part of the farming system and support its functionality (usually as pollinators and predator-pest control species). To estimate the ratio of commercial and subsistence-functional species, the farmer was asked about the amount of the production of the species (in %) used for subsistence (family consumption) or commercial purposes. To define if the species belongs to the subsistence, commercial or both categories, the major proportion was considered, i.e., (a) in the ratio 95/05 (95% of the production used for subsistence purposes and 05% for commercial) the species was defined and counted as subsistence species (as in the case of banana passion fruit in
Table A2 in
Appendix); (b) in the ratio 05/95, the species was counted as commercial (avocado case in
Table A2 in
Appendix); (c) in the case of ratio 50/50, the species was counted equals as subsistence and commercial. To calculate how many subsistence or commercial species are used by the farmer, the species was assigned a value = 1 in the cases a and b. In the case c, the species was assigned a value = 0.5 for counting as subsistence species and 0.5 for commercial. This logic was applied in order to conduct the significance test.
To analyse the land tenure between farming systems, three basic land ownership categories were included, formal, informal and mixed. Formal ownership means that the property rights of the land are officially recognized and protected by the state. In the informal ownership category the property rights are not fully recognized and protected by the state but the access and control of the land are recognized by the community and customary laws. Mixed ownership category includes farmers with some of their farmland as formal and informal.
Finally, to categorise the main irrigation sources, the interview included information related to dependency on rainfall (i.e., rain-fed agriculture), types of irrigation systems, and the methods for water harvesting and storage used by the farmer.
2.3. Data Analysis
A comparative analysis approach was applied to analyse the characteristics of the two farming system types. Descriptive statistics (Crosstabs) were used for qualitative variables (livelihood types, land tenure, irrigation sources, income types and levels); and inferential statistical test (Independent-Samples t Test) for quantitative variables (agrobiodiversity and usage; soil fertility parameters and microclimate conditions inside the farms). To analyse the sustainability of the farming systems, key qualitative and quantitative variables were chosen within the biophysical and socioeconomic components of the farming systems. The bulk of the data collected by interviews were based on smallholder farmers’ perceptions and observations, except the microclimate and soil data (which was biophysical). The perceptions were related to the main characteristics that maintain and enhance the sustainability of the farming systems.
4. Discussion
The results of this paper provide important evidence to inform understanding of how the basic biophysical and socioeconomic features of two farming system types (AFS and CAS) could contribute to support sustainable livelihoods of smallholder farmers.
Among the biophysical features included in this study, the higher levels of agrobiodiversity estimated for AFS represent one of the most interesting—although unsurprising—findings. In reviewing the literature, many papers have stressed the intrinsic value of agrobiodiversity to sustain rural livelihoods and maintain important farming system services. According to the literature, agrobiodiversity plays a key role in providing better food access; improved diets; reduced malnutrition (a major problem in the study area); and to support more sustainable food systems [
55,
56,
57,
58]. Complementing this, the greater levels of agrobiodiversity in a system contributes to enhanced delivery of some important regulatory and provisioning ecosystem services such as pest and disease control, pollination, microclimate control, yield stability and efficiency, primary production, provision of habit, and nutrient and water cycling. Considering these benefits, the results of this study support the increasing body of evidence that agrobiodiversity provides better environmental and socioeconomic opportunities to sustain livelihoods of smallholder farmers, especially in the context of global change [
59,
60]. Therefore the higher levels of agrobiodiversity found in AFS represent an important farming system asset to support the natural capital (natural resource base) [
61,
62] of agroforesters’ livelihoods. In addition, the benefits of greater agrobiodiversity levels of AFS are also related to the greater use of subsistence-functional and commercial species, especially in the case of cultivated biodiversity shown by agroforesters (
Table 2). Greater availability and usage of subsistence-functional species support agroforesters’ livelihoods with better opportunities to sustain food security-sovereignty and farming system services (natural capital). Complementing this, the greater use of commercial species by agroforesters (
Table 2) diversifies their economic incomes and provides better support to the financial-economic capital.
Despite the lack of similar studies conducted in the highland region of Ecuador, the agrobiodiversity results of this study are aligned with results of other studies on smallholder farmers carried out in the region. The estimated levels of cultivated agrobiodiversity presented in this study follow a similar tendency found by Oyarzun et al. [
23] in the Central Highlands of Ecuador. These authors reported highly cultivated agrobiodiversity levels in smallholdings, showing a positive relationship between the number of on-farm cultivated species and the number of species and products destined for home consumption. The study indicates that smallholdings with high agrobiodiversity levels tend to consume more on-farm food items than the households living in low agrobiodiversity farms. The results of the main agrobiodiversity usages also coincides with well-established assumptions of other studies [
63,
64] which indicate that smallholder farmers in the Andes of Ecuador dedicate most of their production to subsistence needs.
Although the greater availability and usage of subsistence-functional species found in AFS do not directly indicate their specific contribution to support sustainable livelihoods and farming systems´ functioning, these findings highlight the potential of these species to be developed as ‘Agroforestry Tree Products (AFTP)’ [
58] for sustainable and multifunctional farming systems (especially in the case of indigenous and exotic trees and shrubs). AFTP are new and highly nutritious crops (originated from the domestication of useful trees), which could enhance the production and the socioeconomic and environmental sustainability of smallholder farming systems [
58]. Such an approach could be relevant for the study area and Andean Highlands.
For the socioeconomic features considered in this study (such as livelihood composition, income levels, agrobiodiversity usages, land tenure and irrigation sources), the findings show a greater potential for agroforesters to support sustainability than conventional farmers. The composition of livelihoods prioritised by smallholder farmers based on the activities which generate the main cash incomes denote the livelihood portfolios used by farmers to improve their incomes and reduce socioeconomic and environmental risks. Although the livelihood portfolios of agroforesters and conventional farmers are quite similar, there are remarkable differences among on- and off-farm activities, which could provide interesting inputs for sustainability analysis. The more diverse agroforesters’ livelihoods portfolios represent an important advantage to reduce socioeconomic and environmental vulnerability and risk (such as market fluctuations, disease, natural hazards and climate extremes) especially in the context of global change. In addition, although the levels of dependence on off-farm activities between the livelihoods of agroforesters and conventional farmers are similar, the off-farm portfolios of agroforesters include complementary on-farm activities mainly oriented to improve their cash incomes and support food security. For example: off-farm work + dairy farming; or off-farm work + farm product commercialization + subisistence farming; or off-farm work + dairy farming + subsistence farming (
Figure 4). By contrast, the on-farm activities included in off-farm portfolios of conventional farmers are mostly focused on staple food supply through subsistence farming (
Figure 4). Therefore, the off-farm portfolio composition of agroforesters in this study could be seen as an advantage to enhance sustainable livelihoods since these activities could give extra support to their financial capital component. In general, off-farm portfolios of smallholder farmers are characterised by activities that promote extra cash income [
65,
66]. These are often based on temporary or permanent migration to work as hired labour, which is one of the most common strategies for livelihood diversification [
60,
61,
65,
66]. In this context, the off-farm portfolios of smallholder farmers in this study are also characterised by temporary or permanent migration whereby typically the male household head migrates to other areas to be employed as a low cost worker in the building sector (especially in urban areas) or in the expanding fresh-cut flower industry [
67,
68,
69,
70,
71]. This explains why most of the household heads interviewed in this study were women.
The less dependence of agroforesters’ livelihoods on off-farm activities and off-farm income differs from the findings of other studies which estimate that the majority of smallholdings in Ecuador, with more prevalence in highlands, depend mainly on off-farm activities and incomes [
72] (the case of conventional farmers´ households in this study).
The differences found in land tenure conditions between agroforesters and conventional farmers also provide an interesting angle to discuss the sustainability of the studied farming systems. According to the literature on the topic, the land tenure status may represent one of the most decisive issues influencing other socioeconomic features included in the study. The more secure land tenure situation for most agroforesters in this study, could enhance farmers’ opportunities to invest and increase production [
73], while at the same time contributing to livelihood diversification and enhancing sustainability [
66,
74]. By contrast, the land tenure insecurity indicated by most of the conventional farmers puts property rights at risk due to other potential land claimants or even through eviction [
74]. In addition, insecure land tenure affects the farmers’ assets to provide food sovereignty and security to their households, restricting farmer’s investments in important assets for production such as irrigation systems; farm equipment and infrastructure; credits and financial assistance [
73].
The greater diversification of irrigation sources and the lesser dependency on rain-fed agriculture found in AFS could have positive effects on the productivity of the system, and most likely reduces the vulnerability of these systems to climate variability and change, placing agroforesters in a better position to maintain and enhance their livelihoods than conventional farmers. Therefore, smallholder farmers—with clear property rights—would be more motivated to adopt alternative production approaches and make greater investments in productive assets (such as trees for agroforestry practices; increment on agrobiodiversity, improvements to farm equipment and infrastructure; and implementation of irrigation systems) in order to intensify the agricultural activities which enhance the self-sufficiency of their livelihoods (characterised mainly by economic and food security/sovereignty).
The socioeconomic findings of this study are also in line with those of previous studies, which consider AFS to be one of the land use practices with enormous potential to enhance sustainable livelihoods and promote the adaptation and mitigation of smallholder farmers’ farming systems to climate change and variability [
26,
41,
75,
76,
77].
5. Conclusions
This study provides qualitative and quantitative evidence to suggest that the highland agroforestry farming systems in the ITKP provide more favourable biophysical and socioeconomic conditions than conventional farming systems to maintain and enhance sustainable livelihoods of smallholder farmers.
Among all the factors analysed, the statistically significant difference in agrobiodiversity species between farming systems—with AFS having more agrobiodiversity than CAS—was one of the most important findings. Other interesting findings were the differences found in the numbers of cultivars/breeds and commercial and subsistence/farming system functioning species used by farmers. AFS could be considered as more genetically diversified farming systems than CAS. The greater levels of agrobiodiversity found in AFS, and especially in the case of the cultivated biodiversity (species, cultivars and breeds), indicate that agroforesters have better socioeconomic and environmental assets to sustain their livelihoods and households than conventional farmers.
All the socioeconomic aspects included in this study, especially livelihood composition; on-and off-farm income levels and agrobiodiversity usages, indicate major advantages of AFS to support sustainable smallholder farmers’ household incomes and livelihoods compared to CAS.
Additional studies using quantitative methods could be done to complement the findings of this study. For example: in the case of agrobiodiversity, on-farm inventories during different crop seasons could be done to establish a more precise number of cultivated and wild species used by farmers. In the case of some socioeconomic variables such as agrobiodiversity usages and income levels, it could be interesting to know how the commercialisation of agrobiodiversity economically contribute to improve the incomes levels and if the improvements of income levels and land tenure status contributes to enhancing sustainability through the direct investments on productive assets (such as infrastructure, equipment, technology and capacitation). An analysis of the vulnerability and resilience of different farming system types to climatic variability and change also is needed in order to have a complete appraisal of the sustainability of smallholders’ livelihoods in the global change context. These issues were beyond the aims of current study and could be considered for further research.
The methods and findings of this research could be considered as an important contribution and reference point for the scarce, but increasing body of knowledge comparing traditional agroforestry and conventional agriculture systems in the tropical highlands. Considering the limited knowledge and geographical expansion of agroforestry practices in the study area and Ecuadorian highlands in general, the results of this study could enhance the initiatives which promote trees and agroforestry practices as essential components to improve the livelihoods and sustainability of smallholder farmers, and contribute to the increasing agroecological approach implemented at local, regional and global levels to deal with the global change process. The results of this study suggest that AFS should be promoted in Ecuadorian highlands due to the socioeconomic and environmental advantages to support and enhance sustainable livelihoods.
Finally, more multidisciplinary research is needed in the High Andes in order to understand the characteristics of the different farming systems and the strategies implemented by the farmers to support sustainable livelihoods in the context of local, regional and global change.