1. Introduction
Bhutan represents a fragile mountainous ecosystem and is a least developed country. The economy of the country is one of the world’s smallest and continues to depend substantially on the Renewable Natural Resources (RNR) sector that comprises Forest, Agriculture and Livestock. The RNR sector accounts for about 15.7% of the total GDP [
1]. The livelihood of over 69% of the population is dependent on the RNR sector. The country is located in the southern slopes of Eastern Himalayas between latitudes 26°42′ N and 28°14′ N, and longitudes 88°44′ E and 92°07′ E. The country has a total geographical area of 38,394 km
2 of which about 70.46% is under forest cover with only 2.93% of the total area available for cultivation [
2]. Rice, maize, wheat, barley, buckwheat and millets are major staple cereals cultivated by farmers. Bhutanese farmers are largely small holders, marginal and practice a self-sustaining, integrated and subsistence agricultural production system. The average land holding is three acres on which farmers grow a variety of crops under different farming practices and rear livestock to meet their household food security. Despite small farm size, farmers grow many types of crops and varieties where farm level agro-biodiversity is the corner stone for sustainable subsistence agriculture. In Bhutan where subsistence farming is still dominant, agro-biodiversity plays a pivotal role for sustainable agricultural development, food security and poverty alleviation [
3]. Bellon [
4] has noted that agro-biodiversity is the basis of food security both in subsistence and technologically advanced agriculture production systems. The Bhutanese agricultural production can be classified as a classic “small holder system” because it associates with most of the characteristic of a small holder. A small holder is characterized by small farm size less of than 10 hectares; most of the farming is undertaken using family labor; the major portion of the produce is used for household consumption with small surplus for sale that provide them the cash income [
5,
6].
Due to the significant influence of the high Himalayas, the Bhutanese agriculture is entirely dependent on the monsoon and prevailing weather conditions where even small variations in the onset and retreat of the monsoon could have considerable impacts on crop production [
7]. The increasing frequency of extreme and adverse weather events that are considered as the signals of climate change include the floods from glacial lake outburst, flash floods, insurgence of new pest and disease such as the rice blast of paddy in 1995 and Gray Leaf Spot (GLS) in maize in 1997 indicate that climate change will have a major impact on the Bhutanese farmers [
8]. Climate change has been proven to have a pervasive influence on food security and livelihoods of the small holder farmers worldwide [
6,
9,
10]. According to the Sector Adaptation Plan of Action (SAPA) [
11] of the Ministry and Agriculture and Forest (MoAF) for climate change, Bhutan is projected to experience a peak warming of about 3.5 °C by the 2050s with the overall significant increase in precipitation but with an appreciable change in the spatial pattern of winter and summer monsoon precipitation. Given this backdrop, the Bhutanese agriculture sector and the farming communities are likely to be most vulnerable.
Bhutan’s strategic location as a landlocked country, poor accessibility with mostly rugged mountainous terrain in the high Himalayas and, its relative isolation from other parts of the world until 1960 has made it rely on agro-biodiversity for its domestic food production. In contrast to its geographical size, it has a rich and unique domestic diversity of species and varieties which has been enhanced through natural and human selection and, subsequent conservation by the farmers. The local crops are considered to possess tremendous genetic diversity and are well adapted to the specific requirements of the areas where they are grown. It is estimated that there are about 350 landraces of rice, 47 of maize, 24 of Wheat and 30 of Barley in the country [
12]. Generally, agro-biodiversity in the Bhutanese context is understood as the cultivation of different types of crops, their landraces and varieties for direct consumption as food and normally includes cereals, oilseeds, legumes, roots and tuber crops, all types of vegetables and fruits [
3]. The National Biodiversity Center (NBC) is the nodal agency of the country, which is mandated to develop programs for the sustainable conservation, development and utilization of the agro-biodiversity resources for food security and poverty alleviation. The conservation and use of agro-biodiversity is fundamental for making the agricultural ecosystems sustainable, productive, and resilient and can contribute to better nutrition and livelihoods of poor farmers throughout the world [
13]. Thus, agro-biodiversity has been recognized as one of the potential means of adaptation to climate change mainly through the development and use of biotic and abiotic tolerant varieties, strengthening the traditional seed system and enhancing the on-farm diversity as potential insurance to climate change [
3,
7,
11]. Jarvis
et al. [
14] have established that agro-diversity is maintained by farmers as an insurance to meet future environmental changes and socio-economic needs.
As one of the key strategy for the formulation of the Strategic Action Plan (SAP) for conservation of cereals in the country, the NBC commissioned a rapid baseline research to understand the community perspectives on the on-farm diversity, status and trends of the six major cereals considered in this study. This study attempted to understand why farmers conserve and maintain agro-biodiversity, the extent of agro-ecological richness, average species richness and the estimated loss of traditional varieties and threats to the loss of on-farm agro-biodiversity.
2. Materials and Methods
This study was undertaken as one of the key process for the formulation of SAP for conservation of cereals. A nationwide community vulnerability assessment study was carried out in 2013 covering the five main agro-ecological zones of the country. This research was undertaken through collaboration between the NBC, the Regional Research and Development Centers (RDC), Dzongkhag (district) and Geog (Sub-district), agriculture extension staff and farmers. The objectives of this study were to understand why farmers conserve and maintain agro-biodiversity, the extent of agro-ecological richness, average species richness and the estimated loss of traditional varieties and threats to the loss of on-farm crop species diversity in the country.
2.1. Study Sites
This survey covered a total of nine
Dzongkhags (districts) out of the total 20
Dzongkhags and 20 of the total 205
Geogs (Sub-districts). The districts and sub-districts were randomly selected to represent the five dominant agro-ecological zones (
Table 1). The elevations of the study sites ranged from 200 masl to 2500 masl covering four different types of agro-ecological zones namely the humid subtropical, the dry subtropical, warm temperate and the cool temperate. The dominant production environment in the dry-subtropical and cool temperate agro-ecology was the rainfed dryland farming where crop production entirely depends on monsoon rains. In the warm temperate, humid and wet-subtropical agro-ecological zone, terraced rice paddies which are irrigated and those that depend on rainfed streams for source of irrigation were the prevalent land use practice. The key features of the study sites are summarized in
Table 1.
2.2. Data Collection Methodology
In order to start the survey, a core team comprising of biodiversity officers, researchers and policy makers was formed. This team designed a comprehensive survey questionnaire to assess the status, extent and trends of cereals diversity and farmers understanding and perceptions on climate change and, its potential impact on cereals diversity. After the finalization of the questionnaire, the sites were randomly selected to represent the different agro-ecological zones from where the data for this study was gathered. The target crops in this study were rice (
Oryza sativa L), maize (
Zea mays), wheat (
Triticum asetivum), barley (
Hordeum vulgare), buckwheat (
Fagopyrum esculentum); millets namely finger millet (
Eleusine coracana), foxtail millet (
Setaria italaca) and common millet (
Panicum miliaceum) that constitute the predominant cereals cultivated by the farmers. Information was collected from 404 respondents (
Table 1).
Table 1.
Detail of the study sites and respondents.
Table 1.
Detail of the study sites and respondents.
Agro-ecology/Altitude Range masl | Dzongkhags | Geogs | No. of Informants | Total |
---|
Male | Female |
---|
Cool Temperate 2600–3600 | Haa | Isu | 8 | 12 | 20 |
Katsho | 7 | 13 | 20 |
Warm Temperate 1800–2600 | Paro | Tsento | 7 | 13 | 20 |
Dopshari | 8 | 12 | 20 |
Punakha | Shelngana | 10 | 6 | 16 |
Toewang | 9 | 15 | 24 |
Dagana | Drujegang | 13 | 7 | 20 |
Goshi | 18 | 2 | 20 |
Dry Subtropical 2013;1800 | Mongar | Chali | 13 | 11 | 24 |
Kengkhar | 12 | 9 | 21 |
Trashiyangtse | Khamdang | 4 | 12 | 16 |
Toetsho | 16 | 9 | 25 |
Pemagatshel | Khar | 7 | 9 | 16 |
Yurung | 1 | 15 | 16 |
Humid-Subtropical 600–1200 | Samtse | Norgaygang | 18 | 4 | 22 |
Pemaling | 15 | 6 | 21 |
Samtse | 14 | 6 | 20 |
Wet-Subtropical 150–600 | Sarpang | Gelephu | 16 | 3 | 19 |
Jigmechholing | 21 | 2 | 23 |
Shompangkha | 20 | 1 | 21 |
Total | 9 | 20 | 237 | 167 | 404 |
During the survey, the survey team collected the data based on the information entirely recalled by the farmers. The surveyors visited the farmers and interviewed them to gather information on the crops, varieties grown and lost, cereals displaced and farmer’s perceptions on climate changes. The information on crop varieties is exclusively based on those mentioned by the farmers. The names of the varieties reported by the respondents included those being cultivated now or those that used to be cultivated before 20 years and that they had heard of from the village elders. Information was collected for traditional and improved varieties. Improved varieties in this study refers to those crop varieties that have been introduced from different sources from outside the country and evaluated and adapted to local conditions through adaptive research including those varieties that have been developed through hybridization with local varieties. The improved varieties are formally released for cultivation to the farmers by the Technology Release Committee (TRC) of the Ministry of Agriculture and Forest which is coordinated by the Council for RNR Research of Bhutan (CORRB). The improved varieties are in most cases high yielding compared to the traditional varieties. They also confirm to the three basic characteristics of being distinct, uniform and stable.
The respondents were randomly selected to represent a Geog. The survey targeted respondents with age group of 40 years and above in order to get a better perspective on the status and trends of cereals and traditional crop varieties cultivated 20 years ago. The survey also gathered farmer’s awareness on the importance of farm level diversity of these cereals, practices and capacity to manage cereals diversity and different challenges faced in maintaining the cereals diversity.
2.3. Data Analysis
The survey data was first compiled using MS Excel and then relevant tables were generated using MS Access. To understand the role of the cereals diversity and the reasons why farmers cultivate different crops and varieties we computed the percentage of respondents assigning different reasons for maintaining agro-biodiversity. The reasons that the highest percentage of respondents assigned was considered the most important factor for maintaining the on-farm agro-biodiversity.
We determined the current status of on-farm agro-biodiversity for individual crop by listing the number of varieties that the surveyed farmers are currently cultivating in their farms (
Table 2). In estimating the number of varieties grown for each crop we only used the respondents growing the crops. Individual variety named by the respondents for each crop was used as the basic diversity unit. Wherever we came across with varieties with different local names in the same locality we further probed the farmers and asked them to describe and agree if the variety in question were similar or different. We removed the varieties with similar names to avoid duplicates. Jarvis
et al. [
14] and Kiwuka
et al. [
15] have used variety as a basic diversity and when issue of the same variety being reported with different names occurred they used the farmer’s knowledge and description to agree whether a variety in question was actually different. In this study, we also used farmer’s knowledge and description as the basis to distinguish whether a variety was similar or different when varieties with different names were reported from the same location.
Table 2.
Number of improved and traditional varieties cultivated by the interviewed farmers in the study sites.
Table 2.
Number of improved and traditional varieties cultivated by the interviewed farmers in the study sites.
Crop | Improved Variety | Traditional Variety | Total Varieties Cultivated |
---|
Rice | 15 | 84 | 99 |
Maize | 5 | 34 | 39 |
Wheat | 6 | 19 | 25 |
Barley | 0 | 14 | 14 |
Buckwheat | 1 | 13 | 14 |
Millet | 0 | 30 | 30 |
Total (n = 219) | 25 | 194 | 219 |
To estimate the level of current on-farm diversity we took into account number of traditional and improved varieties which are currently grown by the respondents in their farm and listed during the survey. Similarly, we asked the respondents to list of varieties for each crop cultivated 20 years ago (1993) but not found in the respondents farm now (2013). We used the chronological difference between numbers of varieties cultivated now and the number of varieties that used to be cultivated 20 years ago to estimate the percentage of varieties lost for each crop (
Table 3). Fowler and Mooney [
16] have also used number of varieties in a time series gap of 80 years (1903 and 1983) to estimate the percentage loss of diversity for different vegetables as one of the basis to establish the loss of genetic diversity. Thrupp [
17] has used the same basis in his review to indicate the loss of traditional crop varieties over time.
Table 3.
Status of traditional varieties of cereals cultivated 20 years ago and now.
Table 3.
Status of traditional varieties of cereals cultivated 20 years ago and now.
Crop | 20 Years Ago (1993) | Now (2013) | Loss % |
---|
Rice | 126 | 86 | 31.75 |
Maize | 45 | 34 | 24.44 |
Wheat | 31 | 19 | 38.71 |
Barley | 14 | 8 | 42.86 |
Buckwheat | 15 | 13 | 13.33 |
Millet | 35 | 30 | 14.29 |
Total | 266 | 190 | 28.57 |
Richness is one notion of diversity that refers to the number of different kinds of individuals regardless of their frequencies [
14]. In this study we have attempted to assess the average species richness for each agro-ecological zone and for six important staple crops (
Table 4). We first estimated the average richness per agro-ecological zone and per species, as the average number of varieties of the six staple crops cultivated by farmers in the six different agro-ecological zones. We used all the respondents interviewed in each site to estimate the agro-ecological richness for each crop under consideration (
Table 4). We computed the average species richness by taking the mean of the species richness from different agro-ecological zones to compare the richness between the six different crops covered in this study.
Table 4.
Average agro-ecological and species richness for six main staples, 2013.
Table 4.
Average agro-ecological and species richness for six main staples, 2013.
Average Agro-ecological and Species Richness for Six Main Staple Cereals |
---|
Agro-ecological Zones (AEZ) | Rice | Maize | Wheat | Barley | Buckwheat | Millet | Average Agro-ecological Richness |
---|
Cool Temperate (2600–3600 masl) | 0.13 | 1.65 | 3.16 | 1.37 | 2.20 | 1.09 | 1.60 |
Warm Temperate (1800–2600 masl) | 3.70 | 1.31 | 0.73 | 0.09 | 0.70 | 0.50 | 1.17 |
Dry Sub-tropical (1200–1800 masl) | 4.63 | 5.63 | 0.73 | 0.91 | 0.90 | 0.78 | 2.26 |
Humid Sub-tropical (600–1200 masl) | 3.19 | 2.23 | 0.16 | 0.11 | 0.92 | 1.94 | 1.42 |
Wet Sub-tropical (150–600 masl) | 1.50 | 2.48 | 0.31 | 0.03 | 1.26 | 1.67 | 1.21 |
Average species richness | 2.63 | 2.66 | 1.02 | 0.50 | 1.20 | 1.19 | 1.53 |
We used the number of respondents (counts) to estimate the percentage of respondents as a simple measure to assess farmers’ level of awareness on climate change, their perceptions of climate change and its impact on agro-biodiversity and household food security. Risks and threats to cereals diversity posed by climate change and farmer’s current coping strategies for adaptation to climate change were recorded. The threats mentioned by the respondents were listed for each crop. The frequency of threats mentioned was cumulated and ranked to arrive at the seven most widespread threats to cereal diversity (
Figure 1). To know which traditional crops were being displaced, we directly asked the farmers for information and synthesized the information and tabulated by
Dzongkhags and by agro-ecology (
Table 5).
Figure 1.
Frequency of different threats to cereals diversity reported by farmers.
Figure 1.
Frequency of different threats to cereals diversity reported by farmers.
Table 5.
Information on cereals displaced and crops displacing them in study site.
Table 5.
Information on cereals displaced and crops displacing them in study site.
Dzongkhags | Agro-ecology | Crops Displaced | New Crops |
---|
Haa | Cool Temperate 2600–3600 | Barley, Buckwheat, Wheat, Millet | Potato, Apple, Vegetable, Pasture |
Paro | Warm Temperate 1800–2600 | Wheat, Barley, Buckwheat | Potato |
Dagana | Warm Temperate 1800–2600 | Maize | Citrus |
Trashiyangtse | Dry Subtropical 1200–1800 | Wheat, Buckwheat | Potato, Vegetables |
Samtse | Humid-Subtropical 600–1200 | Rice, Maize, Wheat, Barley, Buckwheat, Millet | Ginger, Cardamom, Arecanut, Citrus, Vegetables |
Sarpang | Wet-Subtropical 150–600 | Rice, Maize, Wheat, Barley, Buckwheat, Millet | Arecanut, Cardamom, Litchi, Vegetables, Citrus, Pasture, Fodder |
4. Conclusions
This study brings into light the perceptions of the farmers on the status and significance of on-farm varietal diversity of six staple crops and climate change based on their experiences. It is apparent that household food security and livelihood of the subsistence Bhutanese farmers largely hinges on the on-farm agro-biodiversity which provides with crops and varieties that have specific adaptation for the diverse risk prone farming environments spread across five different agro-ecological zones.
This study also shows that subsistence Bhutanese farmers still continue to cultivate different types of staple crops and their varieties in their farms maintaining a rich on-farm agro-biodiversity across different agro-ecological zones. The average agro-ecological richness estimated in this study indicates a wider agro-ecological heterogeneity which determines the types and extent of crops cultivated. Some agro-ecological zones like the dry-subtropical agro-ecological zone grow more crops and their varieties as compared to other agro-ecological zones. The average species richness further indicates that some species like barley is more dominant in the cool temperate agro-ecological zone where as in the dry-subtropical zones all the six crops are cultivated. From the six staple cereals included in this study wheat, barley and buckwheat are more predominant in the cool temperate agro-ecological zone whereas millet is more widely cultivated in the humid and wet subtropical agro-ecological zones. The average species richness estimated for wheat, barley, buckwheat and millets was much lower compared to rice and maize. The lower species richness reveals that households grow much fewer varieties of these crops and these crops are dominant only in a selected agro-ecological zone. Maize and rice had much higher species richness as these two crops are undoubtedly the most popular staple grown across all agro-ecological zones in the country. The findings from this study establish that on-farm conservation programs for the six different staple cereals needs to be more specific and concentrated considering the agro-ecological heterogeneity. The on-farm agro-biodiversity conservation program has to focus on individual crops that have low average species richness and high percentage of loss of traditional varieties.
Climate change is a reality at the household level and farmers perceive climate change including all associated climatic factors as the most impending threat to the loss of on-farm agro-biodiversity. The impact of climate change could directly offset the traditional seed systems in several forms and on farm agro-biodiversity that is vital for household food security. There is abundant existing scientific evidence that agro-biodiversity is fundamental to maintain food production and adaption to climate change for small subsistence farmers. The national research and development programs should start giving more attention towards selection, seed production and dissemination of locally adapted traditional varieties or using the local genes in the future crop breeding programs. The six staple cereals under consideration in this study being displaced by plantation crops rather than the perception that local varieties are being displaced by high yielding improved varieties need more in-depth analysis and attention.
The exploitation of the benefits of agro-biodiversity has been rightly recognized in the National Adaptation Programme of Action (NAPA) and the Sector Adaptation Plan of Action (SAPA) of the MoAF as one of the coping strategies for climate change. To harness the existing potential of agro-biodiversity for adaption to climate change, more dynamic on-farm agro-biodiversity conservation, development and utilization programs that enhance household food security and resilience to climate change will be very important. Farmer’s current coping strategies at the household level needs to be strengthened for adaptation to climate change through the provision of information on potential adverse extremes, enhancing farm level diversity through participatory variety selection and diversification of food crops by improving and strengthening the traditional seeds system.