Next Article in Journal
Access to Affordable Houses for the Low-Income Urban Dwellers in Kigali: Analysis Based on Sale Prices
Next Article in Special Issue
A Visual Typology of Abandonment in Rural America: From End-of-Life to Treading Water, Recycling, Renaissance, and Revival
Previous Article in Journal
Peatland Governance: The Problem of Depicting in Sustainability Governance, Regulatory Law, and Economic Instruments
Previous Article in Special Issue
Economic Comparison between Pasture-Based Beef Production and Afforestation of Abandoned Land in Swedish Forest Districts
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

A Synopsis of Farmland Abandonment and Its Driving Factors in Nepal

1
Institute of Mountain Hazards and Environment, Chinese Academy of Sciences, Chengdu 610041, China
2
University of Chinese Academy of Sciences (UCAS), Beijing 100049, China
3
Wanzhou Key Regional Ecology and Environment Monitoring Station of Three Gorges Project Ecological Environmental Monitoring System, Wanzhou 404020, China
4
National Society for Earthquake Technology-Nepal, Kathmandu Lalitpur, P.O. Box 13667, Nepal
5
Central Department of Geography, Tribhuvan University, University Campus, Kirtipur, P.O. Box 44613, Nepal
*
Author to whom correspondence should be addressed.
Submission received: 4 February 2020 / Revised: 13 March 2020 / Accepted: 13 March 2020 / Published: 16 March 2020
(This article belongs to the Special Issue Agricultural Land Abandonment: Patterns, Drivers and Consequences)

Abstract

:
Farmland abandonment is considered as an important phenomenon for changing eco-environmental and sociocultural landscapes of mountainous rural landscape. Many studies have analyzed farmland abandonment, its driving factors, geophysical processes and consequences at landscape: however, very few have focused on mountainous developing countries such as in Nepal, which is a rapidly urbanizing country suffering from serious farmland abandonment. Therefore, our study was an attempt to (i) assess the spatiotemporal extent of farmland abandonment in Nepal, (ii) explore driving factors of farmland abandonment, and (iii) discuss on the eco-environmental and sociocultural consequences in Nepal. We reviewed various literature, documents, and national reports to obtain a dataset pertaining to the overall status of farmland use and changes along with political and socioeconomic changes, economic development processes, and policy and governance in Nepal. Our results showed that farmland abandonment is widespread; however, it is more prevalent in the hilly and mountainous regions of Nepal. A total of 9,706,000 ha, accounting for 23.9% of the total cultivated farmland in Nepal, was abandoned during the period of 2001 to 2010. The driving factors included population growth, scattered distribution of settlements, urbanization, socio-economic development, poor access to physical services, and poor implementation of agriculture development policies. Furthermore, the increasing extent of natural disasters, malaria eradication, land reform and resettlement programs, the complex system of land ownership, land fragmentation, political instabilities, and the intensification of trading in agricultural products also acted as drivers of farmland abandonment in Nepal. Farmland abandonment generates negative effects on rural societies eco-environmentally and sociologically. Abandoned plots were subjected to different forms of geomorphic damage (e.g. landslide, debris flows, gully formation, sinkhole development etc.). Farmland landscape fragmented into a group of smaller interspersed patches. Such patches were opened for grassland. Furthermore, farmland abandonment also has effects on the local population and the whole society in terms of the production of goods (e.g., foods, feed, fiber), as well as services provided by the multi-functionality (e.g. sociocultural practices, values and norms) of the agricultural landscape. Therefore, this study plays an important role in planning and implementing eco-environmental management and social development processes in Nepal.

1. Introduction

Farmland abandonment is considered an important phenomenon in the eco-environmental and sociocultural landscape change process [1,2,3]. Since 19th century, farmland abandonment is primarily occurred in European or in developed and industrialized countries [4,5,6], particularly in Western Europe [7,8,9], former Soviet Union [4], Southeast Asia [10], United States of America [11], Australia [12], Japan [13] and the Mediterranean regions [14,15,16]. However, many south Asian developing countries such as Nepal, India, Pakistan and Bangladesh, have also been subjected to farmland abandonment in the recent years [17,18,19,20]. According to historical database, the global farmland abandonment area was estimated at approximately 385–472 million square kilometer, accounting for 8–10% of the total cultivated land of the world in 2008 [21]. Some scholars view farmland abandonment as an opportunity for reversing the long term declines of forest, provision of ecosystem services, and habitat enhancement that re-naturalization of landscape provides [22,23,24,25], while others regard farmland abandonment as a threat to rural biodiversity that can cause serious environmental security, such as natural hazards and habitat loss [26,27]. Regardless of the environmental impacts, farmland can lead to socio-economic effects, especially in terms of weakened farmers livelihoods, goods production (e.g. food, fiber etc.) [28], and socio-cultural practices (e.g. indigenous practices, norms and value) in rural communities [29,30]. In the case of Nepal, most Nepalese scholars insist that increasing farmland abandonment tend to have negative impacts both on the environment and socio-economic condition, especially on mountainous closure, agricultural production, poverty alleviation and food security [31,32,33]. In response, Ministry of Agriculture and Livestock Development, Nepal government updated national agriculture-forest policy to control farmland abandonment, which began being enforced in 2019 [34]. This was necessary in order to promote agricultural production that remains in harmony with the environment without compromising rural development, food security, alleviate poverty and biodiversity conservation thereby leading to the healthy development of agriculture.
Farmland abandonment is manifold, reciprocal, complex, and operates at different spatiotemporal scales [35]. Empirical studies have elucidated that the industrialization process and the end of World War II were the main causes of farmland abandonment in the 19th century [36]. Currently, the driving factors are eco-environmental and socioeconomic, including the climate, topography, soil conditions, urbanization, and physical infrastructure development [37]. In particular, the rough terrain associated with steep slopes, poor soil conditions, harsh climates, and long commuting distance from settlements makes the use of machinery more difficult or prevents the adoption of market-oriented farming practices, resulting in a low-intensity farming system [38]. A socioeconomic status expressed by low farm viability and stability, family characteristics with high rates of non-agricultural employment, and a shortage of agricultural labor leads farmers to give up their cultivated farmland [39]. Market expansion and urbanization create diverse non-farm jobs, driving rural outmigration towards cities [40]. Land use policies, taxation, and ownership systems can decelerate the process of land abandonment by encouraging modern agricultural practices that enhance the market value of superior quality productions [41]. Similarly, a breakdown of prevailing social cohesion due to the division of the society into different political groups, ongoing feuds throughout national politics, and frequent institutional changes also led to farmland abandonment [42]. This diverse causes is reflected not only in the spatial location of abandonment but also in the regional variations in the characteristics of socioeconomic development and land use practices [43,44]. Such information supports regional planners and policymakers to implement effective countermeasures, such as controlling possible environmental impacts of farmland abandonment or preventing its expansion by issuing new laws and regulations [45].
Nepal is a mountainous developing country located along the southern slopes of the Himalayan mountain range. More than two-thirds country’s population resides in the rural area and most of them on agricultural activities. Subsistence form of agriculture is common in Nepal. Rural area and agro-activities are interrelated; like two parts of the coin. The contribution of agriculture to Gross Domestic Product (GDP) is also remarkable, however; farm activities is declining, in regard to the increasing problem of farmland abandonment over the decades [46,47]. In fact, the agricultural sector cannot attract young people; the trend of migration from rural to urban is significantly increasing. The poverty is exceedingly marked in rural Nepal. However, there is a conspicuous lack of research focusing on a quantitative and qualitative assessment of the processes involved, the driving factors, and the consequences of to farmland abandonment in this country [48,49,50,51]. Further, future management directions of these abandoned areas have also been outside the scope of any research work conducted to date [52].
With this background, our study attempted to: (i) provide an idea of the spatiotemporal extent of farmland abandonment, (ii) explore the driving factors thereof, and (iii) discuss the eco-environmental and sociocultural consequences of this phenomenon in Nepal. To accomplish these objectives, we first reviewed the long and well documented land use history in Nepal and the various shock events including changes in political settings, land ownership, and political insurgency over the past few decades. Subsequently, we explored the co-occurring drivers of changes in the broad prototypes of land use and management. Land use encompassed all socioeconomic activities that controlled or altered the flows of energy on a given piece of land, and land management was defined by the combined legal, fiscal, and political or other institutional arrangements (e.g., land reforms, protection schemes, and subsidies) that affected land use, as well as the inputs of land, labor, and capital. The comprehensiveness of the present study is unique, and it is therefore expected to serve as the baseline and as a guide for future research and the implementation of eco-environmental management and management of social processes in Nepal.

2. A Theoretical Framework of Farmland Abandonment

Farmland abandonment is simply defined as the cessation of agricultural activities on a given land surface [53,54]. Farmland abandonment involves both eco-environmental components of the earth system and gradual socioeconomic process of local and global systems [4,55], thus leading to undesirable changes in the agricultural landscape, biodiversity [56,57], ecosystem services [58], and sociocultural landscape [59]. A broad number of studies have identified a set of components that commonly act to transfer land and cause farmland abandonment [17,21,60,61]. These are referred to in the following categories: (i) environmental components such as soil quality, slope, elevation, fertility, soil depth, seasonal climate, etc. that constrain agricultural production; (ii) the socioeconomic situation, such as the farm size, household labor, age of farmers, productivity levels, market facility, farm investment, farm industrialization, trades, etc., which expresses the lack of economic and demographic viability and stability; (iii) the regional or nearby surrounding context, such as the distance to markets, road networks, major settlements, forests, etc., which measures the level of access to infrastructure, services, and markets; (iv) policy instruments, urbanization, population distribution, and migration; and (4) the management practices of soil and water resources leading to land degradation, soil erosion, overexploitation of groundwater resources causing water scarcity, and the salinization of croplands. The terms “drivers”, “driving forces”, “(spatial) determinants”, and “factors”, and verbs such as “causing”, “influencing”, or “affecting”, are used extensively in explaining farmland abandonment. Causes often appear in simple combination with other variables that have a high likelihood of explaining an outcome [62]. In social and earth systems, the use of “causes” is insufficient to describe a “contributory” or “combinatory” outcome [63]. Thus, the words “driver” and “driving force” have been widely used in many recent analyses explaining farmland abandonment [64]. These are appropriate and specific to the factors of environmental or social change processes being forced by socio-ecological or land system processes [65].
As shown in Figure 1, several factors play a role in farmland abandonment at the regional and national levels [36,64,65]. The proximity to infrastructure, such as schools and hospitals, and the related accessibility of opportunities, activities, or assets, such as retailers and input suppliers, are proximate drivers, which are either human-induced or originate based on the local conditions. Biophysical and social drivers, such as the topographical and geomorphic processes, weather and climate variations, demographic changes, and their effects on geo-environmental and natural ecosystems, such as biodiversity, water sources, surface runoff, and solar radiation [40,66,67,68,69] underpin farmland use and changes [18,21,70]. Similarly, complexes of technological, political, institutional, and urbanization factors act as the underlying drivers of abandonment that operate indirectly from a remote distance and/or act at the regional or even global scale [71,72].
Larger holdings can benefit from lower production costs and are more competitive for farm practices (the use of machinery or a better input use efficiency). They are more frequently associated with innovation and are usually more competitive and viable in economic terms [73]. Small farmers are more likely to have difficulty accessing credit and the other institutional services required to increase their competitiveness. This prevents the reconstruction of viable farming units through land consolidation [74]. Training and information exchange enables farmers to adapt to changing economic circumstances and to guarantee the integration of the different functions of agriculture at the farm level [8].
Land tenure and the price of land play a supplementary role, as they express the property rights or the demand for land [75]. A weak land market usually translates as low transaction prices (selling or renting), however, is a good proxy for a higher risk of land abandonment [76]. This plays a role in the regional and national context, as well according to laws and local usage, which vary between regions [77]. In such conditions, the transition phase faces difficulties regarding land ownership (registration), insufficiently defined property rights, and the lack of operation land sales markets [75].

3. Material and Methods

3.1. Study Area

This study on the problems of farmland abandonment covered the entire part of Nepal. Nepal is a landlocked country located between the world’s two most populous countries, namely China to the north and India to the south, east, and west (see Figure 2). The country covers a territory of 147,181 km2 and is stretched between the 26°22′–30°27′N latitudes and 80°04′–88°12′E longitudes. It appears roughly rectangular in shape, with the length from east to west about 1024 km and the width ranging from 130 to 192 km. The elevation of country increases dramatically from about 60 mean average sea level (masl) in the southern plains to the world’s highest peak of Mt. Everest at 8848 masl. Such relief in the country is divided into three broad eco-environmental regions, namely (i) the High Mountains, constituting the mighty Himalayas in the north; (ii) the Middle Mountains (Pahad), which includes the intervening hills, intra-montane valleys, and the frontal range (called Siwalik); and (iii) Tarai, the southern belt of plains land, which is the northern extension of the Indo-Gangetic plain. The High Mountains, Middle Mountains, and the Tarai regions are home, respectively, to 7%, 46%, and 47% of Nepal’s population [51]. Agriculture is the major livelihood source of households: approximately 66% of people are directly engaged in farming [78]. Administratively, Nepal is divided into 7 provinces, 77 districts, 6 metropolitan cities, 11 sub-metropolitan cities, 276 urban municipalities (Nagar Palika), and 460 rural municipalities (Gaun Palika).
The country experiences a seasonal summer monsoon rainfall with cloudy skies from June to early October. Nearly 80% of the annual precipitation in the country falls between June and September. In general, the amount of monsoon rains declines from the southeast to the northwest. The success of farming is almost fully dependent on the timely arrival of the summer monsoon. At the same time, landslides, floods, and debris flows, with subsequent losses of human lives, farmlands, and infrastructure, occur largely during the monsoon months. Conversely, severe drought and famine often result when prolonged breaks in rainfall occur during the summer monsoon period. Agriculture is affected by the occurrence of dry spells (for the duration of 2–10 weeks per year), delayed onset of the monsoon, or early cessation of the monsoon. Drought occurs very frequently and is recorded once every three years in the region [79].

3.2. Sources of Data and Methods for Analysis

We reviewed various literature, documents, and reports to obtain a dataset pertaining to the overall status of the spatial and non-spatial farmland use and changes along with political and socioeconomic changes, economic development processes, and policy and governance in Nepal. In particular, three statistical surveys were reviewed: the population census published by the central bureau of statistics (CBS); agricultural statistics of Nepal published by the Ministry of Agriculture and Livestock (MoAL), the Government of Nepal; and the Economic Bulletin published by the Nepal Rastra bank. The population census collected information on the demographic and economic characteristics of farmers and their farmland environmental characteristics. An initial quality check of the available CBS data revealed ambiguities in the 1961/62 data. Consequently, data from the period of 1961/62–2010/11 were selected for this study, and the rate of changes during this period was calculated.
The agricultural statistics were annual surveys collected for almost all farms (or almost the entire utilized agricultural area) during the agricultural census. Additionally, the economic bulletin of Nepal provides a record of all agricultural holdings above a minimum size of two ropani (1 ropani is equal to 508.74 sq m). The record is updated annually and the agricultural activities in each parcel are collected using the technique of a sample survey which is conducted every four months. Various published and unpublished scientific research documents obtained from websites (Google Scholar, Web of Science (WOS), Google search, Research Gate, and specific journal sites—Elsevier, Springer, Science Direct, and Nature), governmental offices, and academic and research institutions, such as the Central Library of Tribhuvan University (TU), Nepal; the Central Bureau of Statistics (CBS), Government of Nepal; the Central Department of Geography (TU); the National Society for Earthquake Technology-Nepal (NSET); the International Centre for Integrated Mountain Development (ICIMOD); the International Union for Conservation of Nature (IUCN); the Department of Forest and Research Division, Government of Nepal; the Department of Soil Conservation and Watershed Management, Government of Nepal; and the Survey Department, Government of Nepal were reviewed. The details of the datasets are listed in Table 1.
Simple statistical methods were used to process and analyze the farmland statuses and their dynamics, including abandonment. First, all spatial and statistical datasets were collected and processed with the help of ArcGIS 10.5 and Microsoft Excel tools. Second, we produced a sample narrative to illustrate the changes of structure of farmland use. This sample summarized the land management in Nepal over the selected years and was divided into subsections, including the technological, institutional, and economic forces involved in the land use changes over the years, The national level narratives were then analyzed on two levels based on a qualitative comparative analysis: (i) a driver-centered analysis, focusing on the trends in land use changes, and (ii) a regime-centered analysis, identifying groupings of similar land management transitions. For the driver-centered analysis, a list of all drivers mentioned in the narratives was created. All narratives were then re-examined and the occurrence of drivers by country was noted. Land management regimes were then identified by combining information on these sets of drivers with a qualitative heuristic text analysis of the narratives, where all narratives were read and the direct or indirect mentioning of periods with any land management were noted. The review of the literature helped to explore numerous narratives for understanding the historical changes in land systems in Nepal. The detailed methodology of information synthesis used for this study is depicted in Figure 3.

4. Results

4.1. The Spatiotemporal Distribution of Abondoned Farmland in Nepal

Numerous studies conducted in the mountainous districts of Nepal have reported that the concentration of farmland abandonment is noteworthy [46,47]. According to Khanal et al., farmland abandonment initially became notable in the high slopes of the mountain areas, particularly in regions that were remote from villages [19]. Abandonment was associated with difficulties in the use of modern agricultural machines on steep slopes and even on small patches that were relatively distant from villages as well as with low yielding capacity [80]. Farmers have been forced to use alternative strategies for increasing their food supply [81]. Whereas, farmers are often confronted with the scarcity of non-farm employment opportunities in the mountain regions [82,83]. Such low crop yields and the limited opportunities available for using the new machinery cannot support the ever-increasing population pressure, which exceed the farmland abandonment in many areas. Moreover, traditional land management systems (e.g., Parma) and irrigation canal management practices have virtually vanished now [84]. Therefore, farmland abandonment is high in the mountainous region of Nepal (see Figure 4).
In earlier parts of the studied period, the volume of land under agricultural cultivation in Nepal and the rate of abandonment appeared to be much less. The main episode of farmland abandonment was first recorded in 1971/72, indicating a 1.86% abandonment of total cultivated farmland. The period was attributed due to the natural growth of the human population and migration (primarily between the 1960s and 1970s). Since the 1970s, the population in the mountainous areas of Nepal has migrated extensively to the lowland plain areas of Nepal, reducing the pressure on cultivated farmlands. Thus, most mountainous farmland coverage changed into forest or shrub land over this period [85]. During the time periods of 1981/82, 1991/92 and 2001/02, increases were seen in the extent of total land cultivated in the proportion of 49.0%, 20.5%, and 36.8%, respectively. Table 2 shows the temporal variation of cultivated area and farmland abandonment in Nepal.
The principal period of industrialization and population migration occurred in the middle of the 1960s and 1970s, although a decrease in the population in agricultural areas was already evident in the beginning of the century, particularly in the middle mountain districts. In 2001/02, the extent of cultivated farmland was recorded at 59.27%, which is the highest rate of cultivated farmland recorded in Nepal to date. During this time, agriculture was the highest priority as economic growth was totally dependent on the extent of crop production. Fertile lands in the Terai region and hardworking peasants in the mountain region provided great supplies of raw materials for industry. Moreover, irrigation facilities increased from approximately 6200 hectares in 1956 to nearly 583,000 hectares by 1990 [86]. However, a slowdown—an abandonment of 23.9%—was reported in 2010/11 in comparison to the results of the previous census. Cultivated farmland was abandoned by 970, 63,000 hectares in 2010/11. Some authors also noted a decline in the area of farmland terraces, which have been rapidly invaded by shrubs and trees in the recent years [87].
Data source: Agriculture Census of Nepal (1961–2010), Central Bureau of Statistics (CBS) 2014, and Economic Indicators of Nepal 2015–2017, Nepal Rastra Bank (note: negative values indicate a rate of abandonment in association with the previous year of total cultivated farmland. There is no record of abandonment during the period of 1981–2001).

4.2. Driving Factors of Farmland Abandonment

A review of the pertinent literature demonstrated that there are four main types of driving factors in Nepal. These are (i) the biophysical characteristics of farmland (e.g., high elevation, steep slope, and aspect), (ii) demographic factors (e.g., population growth and urbanization), (iii) economic and technological factors (a low level of production or the prices of mode of production), and (iv) institutional factors (i.e., land reforms and other policies enforced by organizations at various levels). Within the group of drivers, land reforms were the most frequently mentioned, followed by malaria eradication, resettlement, and land management policies. The details of each driving factor are given below.

4.2.1. Population Growth, Migration, and Urbanization

Population growth and migration towards urban areas are the major driving factors for farmland abandonment in Nepal. In the last five decades, the population of the country increased from 10.22 million to 26.49 million, and the density shot up from 131 person/ km2 to 180 person/ km2 [88,89] (see Figure 5). The migration of population from remote and mountain villages into large- and middle-sized cities located at lower elevations increased dramatically [51]. On average, four persons per 1000 in the population migrated, crossing regional boundaries, and six persons crossed the district boundaries every year. Mountainous and hilly regions constituted the main area for the origin of internal migrants and experienced a net loss of population [90]. Certain districts from the hills lost up to 50% of their populations [91]. The urban populations, in the meantime, increased rather energetically from 3% of the total population to 17% [92]. These demographic shifts led to the process of deactivation and re-peasantization as well as structural changes in household labor [85]. In particular, these structural changes in the demographic conditions (i) provided diverse livelihood strategies, leading to the negligence of subsistence farming [93,94] and (ii) eroded the local support for the continuation farmland activities [95]. Furthermore, the long-term population migration from rural areas caused psychological stresses that intensified the depression and anxiety for the remaining farmers continuing farm activities [96].

4.2.2. Settlement Patterns and Accessibility

Settlement patterns and the accessibility of physical services are also considered driving forces for farmland abandonment. In Nepal, elevation and slope were two basic factors that affected the distribution, scale, and form of rural settlements [97]. Settlements are oriented towards low altitudes and to low slopes and are significantly close to rivers and towns; thus, they formed a special pattern of being dense on the plains, and sparse in the mountainous region. In addition, administrative headquarters, major market towns, roads, basic facilities such as schools and health centers, religious monuments, and other amenities are generally located in major population clusters [98]. Thus, people who live in scattered communities or away from the major settlements, are unable to access basic facilities such as health services, schools, roads, transport, markets, and communication [99].
As there are high costs associated with its deployment, something that is beyond the capacity of local communities, poor access to basic infrastructure appeared in almost all the mountainous settlements [45]. Consequently, this impacted farmland usage in the mountain region, and the roles of regional migration, mobility, and diffusions [100]. Moreover, livelihoods far away from the centers of power and decision-making contributed to the households being socially, economically, and politically isolated [101], and shifting from the mainstreams of cultivators. This was particularly true and prominently conspicuous for communities with farming-based livelihoods in the mountainous regions of Nepal [33].

4.2.3. Socioeconomic Development

Socio-economic development has been another important driving factor for farmland abandonment in Nepal. In the past, human poverty was high, with a human development index of 0.463 [102]. The level of literacy was also only 2% [103]. In addition, systems of civil service, national accounting, records of public welfare, or social, economic, and demographic indicators, such as schools and hospitals, were very sluggish and regionally biased [104]. However, the construction of an improvement in educational and engineering infrastructure, including roads, airports, and hydropower stations throughout the country increased intensively after 1950. For instance, there was a total of only 376 km of road highways in Nepal in 1955, and all were in the north–south direction. By 2014, the road network had extended to all directions, and the highway mileage reached 24,000 km (http://dor.gov.np/road_statistics.php). Further, construction of large hydropower stations has been a significant feature of recent decades [105].
Similarly, there was a marked improvement in human development indicators (HDI) in Nepal as compared to previous years [106]. The latest Nepal Living Standard Survey (NLSS) 2003/04 conducted by the Central Bureau of Statistics revealed that Nepal’s poverty level had declined to 30.85% in 2003–2004 compared to the 41.75% reported in the previous NLSS survey of 1995–1996 [107]. Such development projects enhanced the access to education, health, communication, electricity, transportation, etc. resulting in an increased availability of electric power for use in agricultural irrigation and other usage [50]. These projects also empowered farmers and income projects, especially microcredit schemes, led to their families experiencing better survival [108]. This improvement in livelihoods, the gradual growth of livelihood alternatives such as trade and tourism, and the limitations posed by low-income yielding, traditionally operated farmlands caused a significant decrease in the cultivation of farmland terraces uphill [31].

4.2.4. Natural Disasters

Nepal is a disaster prone country—it faces a multitude of natural disasters, which cause an exceptional number of casualties and amount of property loss [109,110,111]. Historical accounts show that devastating earthquakes occurred in Nepal in 1255, 1810, 1833, 1866, 1934, 1980, 1988, and 2011. The Great Bihar–Nepal Earthquake of 15 January 1934, measuring 8.4 on the Richter scale, shook Kathmandu with intensities of IX and X on the Modified Mercally Intensity (MMI) Scale, raising the ground of more than half of the existing buildings. It claimed >8500 lives in Nepal. Similarly, the 1988 Udaypur Earthquake, with a magnitude of 6.6 on the Richter scale and a maximum intensity of VIII MMI, affected 24 districts of central and eastern Nepal, claiming 744 lives and seriously injuring 6566 persons. Although this was a medium-sized event, it inflicted a significant number of injuries and huge damage to approximately 30,000 residential houses in east Nepal.
Indirect and secondary effects of these extreme events on the local and national economy must be considered, including reduced family income, declines in the production of business and industrial enterprise, inflation, unemployment, increased income disparities, and declines in the national income. Likewise, the devastating flood of 1993 claimed about 1160 lives and affected 70,000 people in the central regions of Nepal. The Kulekhani hydroelectric plant, Bagmati barrage, several bridges and irrigation canals, and check dams were severely damaged [110]. A severe flood on 18 August 2008 in the Koshi River basin directly damaged 17,275 hectares of croplands, affecting 16 village development committees in the Sunsari district [112].
All of this led ultimately to a significant abandonment of farmlands hitherto cultivated on upper hill slope terraces and put tremendous pressure on land resources, leading to abandonment after numerous disaster events. In particular, floods, landslides, and debris flows have been found to be responsible for the reduction of farmland areas due to undercutting and erosion adding to the hardships of farming activities [113]. Frequent river diversions and bank breaches during heavy flooding along the riverbed farmlands as well as in flat-terrain farmlands are another reason for abandonment. Soil erosion, river bank-cutting, and sediments deposited on croplands have often led to the idling for years of cultivated lands [112,114]. Destruction of infrastructure such as buildings, roads, and agricultural irrigation infrastructure has resulted in a significant number of migrants from settlements uphill to the emerging road-side markets on river banks of the affected mountain districts [115].

4.2.5. Land Ownership, Distribution, and Fragmentation

Land ownership and fragmentation is a worrying problem for farmland abandonment in Nepal. A regional analysis of land distribution indicated that one third of the total households owned more than half of the total agricultural farmland in Nepal [78]. Approximately 1.5% of these households held more than five hectares of land, which represents 14% of the total farming area of Nepal. Two thirds of the total land holdings had less than one hectare of land, and they accounted for only 30% of the total farm area of Nepal. Increasingly, the current land holding systems are becoming highly fragmented. The majority of farmers are smallholders, with an average holding of 0.79 hectares [78]. Approximately 8% of households had more than two hectares of land, fragmented into an average of six parcels (CBS, 2011a). See Table 3 for detail land ownership and fragmentation in Nepal.
This reduces the efficiency of agricultural production as well as discouraging the use of cropland [116]. In particular, agricultural producers encounter difficulties in accessing the necessary machinery, obtaining agricultural credit, receiving extension advice, and purchasing inputs [45]. Farmers are not incentivized to seek larger parcels due to the limited available resources with which to cultivate crops [101]. In addition, small farm sizes and their distribution raises the costs of production, as producers cannot use large machinery and lose time traveling between dispersed parcels. Farmers are hindered from adopting productivity-enhancing technologies in the farmlands of small parcels, resulting in abandonment in despair at the constraints of modernization [117].

4.2.6. The Intensification of Agriculture and the Increasing Trade in Agricultural Products

The intensification of cultivation has also been observed as a driver of cultivated farmland abandonment in Nepal. Studies have indicated that there has been increasing access to technical inputs (irrigation and road) and credit in recent years [118]. The production of highly valuable crops, such as cardamom, ginger, potatoes, fruits, tea, coffee, milk, vegetables, and spices was generally introduced near market centers and district administrative headquarters [52,81]. Farmers have started adopting inter-culture practices of growing two or more crops [119], such as maize with beans and/or potato, and the double cropping of staple crops, such as rice and wheat or corn (maize) in one single cultivated field. The most visible impacts seen on the agriculture system have been that staple foods and vegetables such as cabbage, cauliflower, tomato, radish, etc. are imported from the Tarai to the mountains; and crops such as Akabare chili, ginger, fruits (orange, lemons), potatoes, tea, large cardamom, etc. are imported from the mountain regions [52]. This has allowed farmers to discontinue cultivating certain crops that had production constraints. Moreover, importation of subsistence staples such as cereal crops has reduced their local production due to their replacement by high-value cash crops, leading to a substantial reduction of the scattered cultivated areas in the mountain slopes [47].

4.2.7. Malaria Eradication and Land Reform Program

The malaria eradication program has also acted as a driver of farmland abandonment in Nepal. Particularly after the advent of the malaria eradication program in 1956, the Nepalese government recognized the lowland areas as a source of tax revenue, food production, and supplies throughout the country. Tenancy rights were protected under the anti-peasantry land tenure system. Jagir (lands assigned to the state functionaries in lieu of salaries or allowances), Birta (land obtained or possessed in such a way that the land is wholly exempt from the State Land Tax), and the Zamindari (landholders of demarcated areas, responsible for collecting revenue for the monarchy) system were abolished and the responsibility and authority for collection of revenue was shifted to the district revenue officers [120]. Meanwhile, several projects for economic development and planned resettlement programs were introduced in parallel [90]. This motivated many mountain farmers to move towards lowland plain areas, abandoning cultivation in their ancestral farmlands.
According to the statistics, in 1971 the annual migrant population to the Terai was 399,925 people. However, this increased to 686,178 people in 1981, and grew to 1,085,862 people in 2001 [45,49,120]. These enormous population surges into the Terai, regional urbanization, and reduction in household sizes contributed to the increased demand for new houses [121]. This initial migration resulted in the conversion of forests or rangelands to agriculture, and later led to the development of many small city centers with expansive urban sprawls, all of which have resulted in the continuing conversion of mountainous agricultural farmland into forest and grassland [122].

4.2.8. Political Instabilities and Implications

Continued political instability is another major driver of farmland abandonment in Nepal. From the 1950s to recent times, the political environment in Nepal has been defined by highly fragmented, unstable, and zero-sum decision-making practices in the government [123]. Rather than trying to build the country’s economy and disperse its benefits more equitably, political leaders and the ruling elite seemed to be interested in making money for themselves and rewarding their supporters and family members. Corruption has risen at all levels, together with growing inter- and intra-party conflict [124]. Governments have failed to deliver jobs and the necessities of life to disadvantaged groups, particularly in the rural and remote areas, and significantly increased the inequality between the elite and non-elite. Poverty, inequality, anger, and frustration have grown, particularly among the youth in rural and remote areas [49].
Furthermore, the emergence of the Maoists in 1996 created a politico-economic crisis and halted opportunities for socioeconomic development. This development augured a barrier for the socioeconomic growth of in the country [125]. Insurgency led to a political transition, which was followed by further instability in governance along with a huge mobilization of the population towards cities or out of countries. This motivated many landowners to migrate to cities or urban areas mostly in the low-height plain areas [98,121]. Furthermore, the bureaucracy and public administration were constrained by patronage and corruption, low capacity, little coordination or policy coherence, low accountability, and a questionable bureaucratic culture [124].
The private sector was held back by low investment in farm activities and sociocultural development. Consequently, the inadequacy of planned programs for agricultural development, ad hoc land utilization, and conflict management policies as well as the laxity of enforcement of land degradation control measures took over, causing an increase in farmland abandonment in Nepal. Moreover, the performance of the Nepalese economy remained less than satisfactory, owing to unfavorable weather conditions and political tensions, People’s expectations rose—particularly among the disadvantaged youth—and thus farmland abandonment continued over the years.

4.2.9. Poor Implementation of Agricultural Development Policies and Their Impact

The Nepalese government put several acts and policies aimed at sustainable land use and the conservation of existing farmland resources. For instance, the Agriculture Perspective Plan (1994/95–2017/18), Plant Protection Act 2048, Pesticides Act 2049 and Regulation 2050, Food Act 2023, Consumers’ Right Act 2054, and Environment Protection Act 2053 were all considered to constitute a guiding strategy toward the agricultural development in the country [126,127] However, these plans, acts, and guidelines were not successful, and led to a consistent decline in food production and soil fertility [45]. In particular, there has always been a lack of coordination at intra-governmental levels, as well as between the state, private sector, and development partners. Agricultural associations have been unable to identify sectors where collective action would have the highest payoff, and “herd behavior” in the private sector undermines industry-wide competitiveness [128]. These trends have a direct relationship to the abandonment of cultivated farmlands.

4.3. The Eco-Environmental and Social Consequences of Farmland Abandonment

Farmland abandonment most often generates negative effects on rural societies eco-environmentally and sociologically. Studies conducting plot-level analysis of 149.6 ha terraces near the village of Sikles in the Nepal Himalaya showed that nearly 10% of all Khet land had been extensively damaged by landslides and floods. Nearly 41% of all abandoned plots were subjected to different forms of geomorphic damage. As geomorphic processes (e.g., landslides, debris flows) continued to expand, the farmland landscape fragmented into a group of smaller interspersed patches as cropland [19]. Such patches were opened for grassland, which decreased the numbers and abundance of birds and woody plant species [129].
Farmers began to extend their cropland, which led to the further encroachment of the forest and marginal lands [130]. Soil erosion was attributed to greater runoff concentration. In comparison of erosion in an abandoned field to that in a prior cultivated field; the presence of rills and the expansion of deep gullies with very active head-cuts was intensive in the abandoned field [131]. In particular, steep hydraulic gradients between terraces encouraged sub-superficial erosion at the terrace edge, and were sensitive to contraction and swelling with respect to gully formation [114]. A failure to maintain network ditches tended to produce reorganization of the drainage system through the incision of new channels across terraces and re-establishment of the natural drainage network [132]. Finally, terrace abandonment enhanced the piping in terraced fields, which was previously destroyed by annual livestock trampling [133].
Farmland abandonment also has effects on the local population and the whole society in terms of the production of goods (e.g., foods, feed, fiber, and biomass production), as well as other services provided by the multi-functionality (e.g., sociocultural practices and norms) of the agricultural landscape. As more and more households abandon their farmland, the rural populations cannot continue their social and cultural norms and practices [134]. The organizational and institutional mechanisms for the management of farmland, the drinking water supply system, irrigation canal management, and forest resources, such as Parma (indigenous land management system, have disappeared or become less practiced [82]. Some of the practices used to encourage environmental protection as well as the protection, regeneration, and management of local resources are now not employed effectively [135]. Farmland abandonment has also been linked to the modification or degradation of the rural landscapes and the loss of a unique identity, including the traditional features, culture, and characteristics of the mountains of Nepal [136].

5. Discussions

National- and international-level projects and organizations, such as the Land Resource Mapping Project (LRMP) and Integrated Center for Mountain Development (ICIMOD) have undertaken agricultural land use studies at the national scale in Nepal [137], whereas, the IGBP DIS-Cover [138], UMD land cover [139], and GlobeLand30 [140], have been undertaken surveys regarding the dynamics of farmland changes, on a global scale. These projects have produced agricultural land cover maps on various scales based on remote-sensing technologies. However, the exact extent of farmland abandonment in Nepal is not known precisely in quantitative terms, as there is no system of formal inventory for such lands. Maps of land abandonment and figures on the amount of abandoned farmland at the district or provincial scale have not been produced thus far [87]. This partly is because abandoned farmland does not appear as a statistical category in the agricultural census process. Additionally, there is no formal definition of abandoned farmland, which makes its accounting in the census problematic in Nepal. Thus, the exploration of indications and evidences of changes, declines, or increases in land coverage by agricultural activities, and the analysis thereof, was the main objective of this study.
The results demonstrated that there are many factors driving the creation and further increase of farmland abandonment in Nepal. Some of the driving factors (e.g., human population growth, migration, and urbanization) are of natural processes, while others are due to the socioeconomic conditions (poor accessibility, scattered settlements, poverty, and the lack of basic physical services) and were generated by a lack of appropriate policies. These factors are expected to exacerbate if left unattended and uncontrolled. Moreover, the implementation of any comprehensive conservation strategies, including improvement in land use, settlement, agricultural planning and development, forest and biodiversity conservation and restoration, hazard and disaster risk management, sustainable use of land resources, etc., in the long run, cannot be implemented successfully without understanding and addressing the issues of farmland abandonment in the mountainous regions of Nepal. Therefore, a much wider discourse on the topic is acutely necessary, especially if one considers that there is no formal inventory of abandoned farmlands or any systematic study of the underlying dynamics both quantitatively and qualitatively in Nepal.
Farmland abandonment is considered a major phenomenon that has transformed the eco-environmental and sociocultural landscape [5,17,30,141,142]. However, Nepal’s farming is unique and the labor-intensiveness involved makes our case different than other mountainous countries of the world [143]. Sloped terrains that are mostly more than 20% gradient are divided into narrow and graduated steps (typically 2–3 m wide and 10–20 m long across the slopes) for farmlands [137]. Farmers adopted the terracing system to control surface runoff, minimize soil losses, and stabilize the farmland slopes. The agricultural terraces were carved out and most slopes are supported with the aid of buttresses. Terrace risers, beds, and waterways are repaired regularly before the sowing/transplanting of crops and during weeding. Every year, farm households spend at least 16 days on the maintenance of terraces [134]. Therefore, when such terraces are abandoned, the supporting structures fail, leading to accelerated slips that generate a series of geomorphological hazard disasters, such as landslides and debris flows, in the mountainous landscape of Nepal.
An abandonment of farmland does not lead to plant succession, as geomorphic damage is intensified prior to succession, although the amount of geomorphic damage in fields abandoned earlier is greater than that in plots abandoned recently [19]. The stage of dense shrub cover may be delayed by several decades or may even not occur [144]. A fall in infiltration and poor nutrient conditions are some of the most important factors constraining the evolution of plant cover. Livestock trampling enhances the formation of gullies, connecting different terraces between hill slopes and channels [118], which also hinders the growth of woody species and delays plant succession. However, it is interesting to note that if grazing is controlled, the abandoned farmland remains free of thorny shrubs for only a few years: (i) the invasion of herbaceous plants and shrubs occurs during the first years of abandonment, (ii) woody shrubs spread between 2 to 5 years after abandonment, (iii) the retraction of woody shrubs and a new expansion of herbaceous plants occurs between 5 and 10 years, and (iv) the entry of young trees occurs after more than 10 years of abandonment. The succeeded woodlands, although of a limited extent on Nepal’s mountain landscape, support diverse plant, large mammal, and bird species [145] that ultimately influence the mountain biodiversity, tourism, and economic productivity [146].
Moreover, farmers have been practicing diverse sociocultural systems (e.g., Parma) for the management of irrigation canals, drinking water supply services, and farmland terraces [82]. The systems are practiced at the community level with local rules and regulations regarding the use and management. There was a strong social cohesion among the members of each household; thus, it is also feasible to use the available labor force in the village for the maintenance of terraces and irrigation canals, as well as the control of gullies, landslides, and floods on cultivated fields, through community-guided management systems, without paying cash for labor services. Thus, if the land abandoning practices continue, the mountainous rural landscape and its associated eco-environmental, social, and cultural norms and value will be lost gradually. In addition, the new eco-environment and social landscape that is formed may not continue the erstwhile existing tradition, culture, and customs, and may not be as hospitable as the previous society with its rich historical traditions.

6. Conclusions

Based on the secondary data from 1961–2017 from the Central Bureau of Statistics (CBS), the Ministry of Agriculture and Development (MoAD), and the Nepal Rastra Bank, and from the perspective of farmland use and changes in Nepal, this study demonstrated the quantitative value of farmland abandonment and its impact on the eco-environmental and social landscape of Nepal. This study (i) assessed the spatiotemporal distribution of abandoned farmland, (ii) explored the driving factors of farmland abandonment, and (iii) discussed the social and eco-environmental consequences of farmland abandonment. Thus, this study enhanced our understanding of the relationship between the topographic, socioeconomic, physical infrastructure developments, development policies, and farmland use and abandonment in Nepal.
The results of this study provided empirical evidence that policy-makers should work to solve the problems of food and eco-environmental security and that the processes therein could contribute to initiatives including the “land bank” of Nepal. Such knowledge on the spatiotemporal distribution and causes of farmland abandonment could yield different explanations and preferences for interventions, which could be used as input to find a common ground for landscape management, and serve as a starting point for a more spatially targeted and nuanced management approach.
Nepal is one of the world’s highest mountainous countries, and this review on the process of farmland abandonment demonstrated a variety of interrelated adverse consequences (e.g., the loss of agricultural farmland, triggering of natural hazards, changes in the socio-cultural landscape, and the loss of a unique identity) in the mountainous landscape of Nepal. Therefore, the study invites researchers and policy-makers to think about the future of mountain farmlands and societies where a huge number of mountain people are migrating away to enhance their household economic and livelihood security, or are seeking to participate in non-farm activities.
Regarding this, we suggest that focus be placed on (i) enhancing the access to markets and government incentives for farmers to cultivate high-profit commercial crops on abandoned farmland and (ii) developing risk-mitigation strategies through agro-advisory systems and information technology infrastructure to make market, climate, and crop management information accessible to farmers. Incentives could be provided for the new farming community in Nepal, which may increase agricultural productivity. Awareness campaigns could be undertaken to ensure that high quality agricultural inputs, such as certified seeds, fertilizers, and pesticides, are available at reasonable market prices.
Finally, there were some deficiencies in this study that may be addressed in future studies: (i) This study discussed overall eco-environmental and socio-cultural consequences; however, it is necessary to carry out site-specific investigations on this issue, and to gain a deeper understanding of the consequences in Nepal. (ii) The factors of topographic, socioeconomic, and other demographics are increasingly evident for farmland abandonment in Nepal. Due to limitations of the data, this study did not discuss these relationships. Moreover, the relationships may be dynamic. Thus, future research could use this concept to analyze the relationships in greater detail.

Author Contributions

Conceptualization, S.C.; methodology, S.C.; software, S.C., K.Y., Q.L., Y.L., and M.L., validation, S.C.; formal analysis, S.C.; investigation, S.C.; resources, Y.W., and P.X.; data curation, S.C.; writing—original draft preparation, S.C.; writing review and editing, Y.W., A.M.D., N.R.K., P.X., and B.F.; visualization, K.Y., Q.L., Y.L., and M.L.; project administration, Y.K., P.X., and B.F.; funding acquisition, Y.K., P.X., and B.F. All authors have read and agreed to the published version of the manuscript.

Funding

This research was supported by the 135 strategic program of the Institute of Mountain Hazards and Environment, Chinese Academy of Science, grant number SDS-135-1703; International talent program of the Chinese Academy of the Sciences, grant number 2019 VCA 0026); and the Chinese Academy of Sciences-the World Academy of Sciences (CAS-TWAS) Presidents Fellowship program for international PhD study.

Acknowledgments

We are extremely grateful to the Central Department of Geography (CDG) and the National Society for Earthquake Technology (NSET) for sharing their valuable datasets and for their review of the manuscript. The authors were grateful for the constructive comments from the editor and anonymous reviewers.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Ramankutty, N.; Mehrabi, Z.; Waha, K.; Jarvis, L.; Kremen, C.; Herrero, M.; Rieseberg, L.H. Trends in global agricultural land use: Implications for environmental health and food security. Annu. Rev. Plant Biol. 2018, 69, 789–815. [Google Scholar] [CrossRef] [Green Version]
  2. Qin, Y.; Yan, H.; Liu, J.; Dong, J.; Chen, J.; Xiao, X. Impacts of ecological restoration projects on agricultural productivity in China. J. Geogr. Sci. 2013, 23, 404–416. [Google Scholar] [CrossRef]
  3. Zhang, L.; Lu, D.; Li, Q.; Lu, S. Impacts of socioeconomic factors on cropland transition and its adaptation in Beijing, China. Environ. Earth Sci. 2018, 77, 575. [Google Scholar] [CrossRef]
  4. Pointereau, P.; Coulon, F.; Girard, P.; Lambotte, M.; Stuczynski, T.; Sánchez Ortega, V.; Del Rio, A. Analysis of the Driving Forces behind Farmland Abandonment and the Extent and Location of Agricultural Areas That are Actually Abandoned or Are in Risk to be Abandoned; JRC Scientific and Technical Report; European Commission Joint Research Centre, Institute for Environment an Sustainability, 2007. [Google Scholar]
  5. Queiroz, C.; Beilin, R.; Folke, C.; Lindborg, R. Farmland abandonment: Threat or opportunity for biodiversity conservation? A global review. Front. Ecol. Environ. 2014, 12, 288–296. [Google Scholar] [CrossRef]
  6. Renwick, A.; Jansson, T.; Verburg, P.H.; Revoredo-Giha, C.; Britz, W.; Gocht, A.; McCracken, D. Policy reform and agricultural land abandonment in the EU. Land Use Policy 2013, 30, 446–457. [Google Scholar] [CrossRef]
  7. Cerda, A.; Rodrigo-Comino, J.; Novara, A.; Brevik, E.C.; Vaez, A.R.; Pulido, M.; Gimenez-Morera, A.; Keesstra, S.D. Long-term impact of rainfed agricultural land abandonment on soil erosion in the Western Mediterranean basin. Prog. Phys. Geogr. 2018, 1, 18. [Google Scholar] [CrossRef]
  8. Baldock, D.; Beaufoy, G.; Brouwer, F.; Godeschalk, F. Farming at the Margins: Abandonment or Redeployment Of Agricultural Land in Europe; Institute for European Environmental Policy (IEEP): London, UK; Agricultural Economics Research Institute (LEI-DLO): The Hague, The Netherlands, 1996. [Google Scholar]
  9. Brouwer, F.; Baldock, D.; Godeschalk, F.; Beaufoy, G. Marginalisation of agricultural land in Europe. In Proceedings of the Livestock Systems in European Rural Development, Nafplio, Greece, 23–25 January 1997. [Google Scholar]
  10. Wang, B.; Zhang, G.H.; Shi, Y.Y.; Zhang, X.C.; Ren, Z.P.; Zhu, L.J. Effect of natural restoration time of abandoned farmland on soil detachment by overland flow in the Loess Plateau of China. Earth Surf. Process. Landf. 2013, 38, 1725–1734. [Google Scholar] [CrossRef]
  11. Ramankutty, N.; Heller, E.; Rhemtulla, J. Prevailing myths about agricultural abandonment and forest regrowth in the United States. Ann. Assoc. Am. Geogr. 2010, 100, 502–512. [Google Scholar] [CrossRef]
  12. Sochacki, S.J.; Harper, R.J.; Smettem, K.R. Bio-mitigation of carbon following afforestation of abandoned salinized farmland. GCB Bioenergy 2012, 4, 193–201. [Google Scholar] [CrossRef]
  13. Ito, J.; Nishikori, M.; Toyoshi, M.; Feuer, H.N. The contribution of land exchange institutions and markets in countering farmland abandonment in Japan. Land Use Policy 2016, 57, 582–593. [Google Scholar] [CrossRef]
  14. Cots-Folch, R.; Martínez-Casasnovas, J.A.; Ramos, M.C. Land terracing for new vineyard plantations in the north-eastern Spanish Mediterranean region: Landscape effects of the EU Council Regulation policy for vineyards’ restructuring. Agric. Ecosyst. Environ. 2006, 115, 88–96. [Google Scholar] [CrossRef]
  15. Labaune, C.; Magnin, F. Pastoral management vs. land abandonment in Mediterranean uplands: Impact on land snail communities. Glob. Ecol. Biogeogr. 2002, 11, 237–245. [Google Scholar] [CrossRef]
  16. Arnaez, J.; Lasanta, T.; Errea, M.; Ortigosa, L. Land abandonment, landscape evolution, and soil erosion in a Spanish Mediterranean mountain region: The case of Camero Viejo. Land Degrad. Dev. 2011, 22, 537–550. [Google Scholar] [CrossRef]
  17. Benayas, J.R.; Martins, A.; Nicolau, J.M.; Schulz, J.J. Abandonment of agricultural land: An overview of drivers and consequences. CAB Rev. Perspect. Agric. Vet. Sci. Nutr. Nat. Resour. 2007, 2, 1–14. [Google Scholar] [CrossRef] [Green Version]
  18. Gellrich, M.; Baur, P.; Koch, B.; Zimmermann, N.E. Agricultural land abandonment and natural forest re-growth in the Swiss mountains: A spatially explicit economic analysis. Agric. Ecosyst. Environ. 2007, 118, 93–108. [Google Scholar] [CrossRef]
  19. Khanal, N.; Watanabe, T. Abandonment of Agricultural Land and Its Consequences: A Case Study in the Sikles Area, Gandaki Basin, Nepal Himalaya. Mt. Res. Dev. 2006, 26, 32–40. [Google Scholar] [CrossRef] [Green Version]
  20. Jing’an, S.; Zhang, S.; Xiubin, L. Farmland marginalization in the mountainous areas: Characteristics, influencing factors and policy implications. J. Geogr. Sci. 2015, 25, 701–722. [Google Scholar]
  21. Campbell, J.E.; Lobell, D.B.; Genova, R.C.; Field, C.B. The global potential of bioenergy on abandoned agriculture lands. Environ. Sci. Technol. 2008, 42, 5791–5794. [Google Scholar] [CrossRef]
  22. Gashaw, T.; Tulu, T.; Argaw, M.; Worqlul, A.W.; Tolessa, T.; Kindu, M. Estimating the impacts of land use/land cover changes on Ecosystem Service Values: The case of the Andassa watershed in the Upper Blue Nile basin of Ethiopia. Ecosyst. Serv. 2018, 31, 219–228. [Google Scholar] [CrossRef]
  23. Perpiña Castillo, C.; Coll Aliaga, E.; Lavalle, C.; Martínez Llario, J.C. An Assessment and Spatial Modelling of Agricultural Land Abandonment in Spain (2015–2030). Sustainability 2020, 12, 560. [Google Scholar] [CrossRef] [Green Version]
  24. Tolessa, T.; Senbeta, F.; Kidane, M. The impact of land use/land cover change on ecosystem services in the central highlands of Ethiopia. Ecosyst. Serv. 2017, 23, 47–54. [Google Scholar] [CrossRef]
  25. Xie, Z.; Game, E.T.; Hobbs, R.J.; Pannell, D.J.; Phinn, S.R.; McDonald-Madden, E. Conservation opportunities on uncontested lands. Nat. Sustain. 2019, 3, 9–15. [Google Scholar] [CrossRef]
  26. Anache, J.A.; Flanagan, D.C.; Srivastava, A.; Wendland, E.C. Land use and climate change impacts on runoff and soil erosion at the hillslope scale in the Brazilian Cerrado. Sci. Total Environ. 2018, 622, 140–151. [Google Scholar] [CrossRef]
  27. García-Ruiz, J.M.; Lana-Renault, N. Hydrological and erosive consequences of farmland abandonment in Europe, with special reference to the Mediterranean region–A review. Agric. Ecosyst. Environ. 2011, 140, 317–338. [Google Scholar] [CrossRef]
  28. Unit, E.I. Global Food Security Index 2018: Building Resilience in the Face of Rising Food-Security Risks; EIU, 2018; Commissioned by Corteva Agriscience, The Agriculture Division of DowDuPont. [Google Scholar]
  29. Bruinsma, J. World Agriculture: Towards 2015/2030: An FAO Study; Routledge: London, UK, 2017. [Google Scholar]
  30. Antrop, M. The concept of traditional landscapes as a base for landscape evaluation and planning. The example of Flanders Region. Landsc. Urban Plan. 1997, 38, 105–117. [Google Scholar] [CrossRef]
  31. Bhandari, B.; Grant, M. Analysis of livelihood security: A case study in the Kali-Khola watershed of Nepal. J. Environ. Manag. 2007, 85, 17–26. [Google Scholar] [CrossRef]
  32. MOAD. Statistical Information on Nepalese Agriculture; Government of Nepal (GoN), Ministry of Agricultural Development, Agri-Business Promotion and Statistics Division, Singha Durbar: Kathmandu, Nepal, 2012.
  33. Nepali, P.B.; Pyakuryal, K.N. Livelihood Options for Landless and Marginalised Communities in an Agrarian Society: A Case Study from Far Western Nepal’. Pak. J. Agric. Sci. 2011, 48, 1–10. [Google Scholar]
  34. MOALD. National Agriculture and Forest Development Policy 2019; Government of Nepal: Kathmandu, Nepal, 2019.
  35. Lasanta, T.; Arnáez, J.; Pascual, N.; Ruiz-Flaño, P.; Errea, M.; Lana-Renault, N. Space–time process and drivers of land abandonment in Europe. Catena 2017, 149, 810–823. [Google Scholar] [CrossRef]
  36. Jepsen, M.R.; Kuemmerle, T.; Müller, D.; Erb, K.; Verburg, P.H.; Haberl, H.; Vesterager, J.P.; Andrič, M.; Antrop, M.; Austrheim, G. Transitions in European land-management regimes between 1800 and 2010. Land Use Policy 2015, 49, 53–64. [Google Scholar] [CrossRef]
  37. Khorchani, M.; Nadal-Romero, E.; Tague, C.; Lasanta, T.; Zabalza, J.; Lana-Renault, N.; Domínguez-Castro, F.; Choate, J. Effects of active and passive land use management after cropland abandonment on water and vegetation dynamics in the Central Spanish Pyrenees. Sci. Total Environ. 2020, 717, 137160. [Google Scholar] [CrossRef]
  38. Smith, P.; House, J.I.; Bustamante, M.; Sobocká, J.; Harper, R.; Pan, G.; West, P.C.; Clark, J.M.; Adhya, T.; Rumpel, C. Global change pressures on soils from land use and management. Glob. Chang. Biol. 2016, 22, 1008–1028. [Google Scholar] [CrossRef]
  39. Nguyen, T.T.; Nguyen, L.D.; Lippe, R.S.; Grote, U. Determinants of Farmers’ Land Use Decision-Making: Comparative Evidence From Thailand and Vietnam. World Dev. 2017, 89, 199–213. [Google Scholar] [CrossRef]
  40. Lambin, E.F.; Meyfroidt, P. Global land use change, economic globalization, and the looming land scarcity. Proc. Natl. Acad. Sci. 2011, 108, 3465–3472. [Google Scholar] [CrossRef] [Green Version]
  41. Milenov, P.; Vassilev, V.; Vassileva, A.; Radkov, R.; Samoungi, V.; Dimitrov, Z.; Vichev, N. Monitoring of the risk of farmland abandonment as an efficient tool to assess the environmental and socio-economic impact of the Common Agriculture Policy. Int. J. Appl. Earth Obs. Geoinf. 2014, 32, 218–227. [Google Scholar] [CrossRef]
  42. Prishchepov, A.V.; Müller, D.; Dubinin, M.; Baumann, M.; Radeloff, V.C. Determinants of agricultural land abandonment in post-Soviet European Russia. Land Use Policy 2013, 30, 873–884. [Google Scholar] [CrossRef] [Green Version]
  43. López-i-Gelats, F.; Milán, M.J.; Bartolomé, J. Is farming enough in mountain areas? Farm diversification in the Pyrenees. Land Use Policy 2011, 28, 783–791. [Google Scholar] [CrossRef]
  44. Ortega, M.; Pascual, S.; Elena-Rosselló, R.; Rescia, A.J. Land-use and spatial resilience changes in the Spanish olive socio-ecological landscape. Appl. Geogr. 2020, 117, 102171. [Google Scholar] [CrossRef]
  45. Sharma, K.; Khanal, S. A review and analysis of existing legal and policy issues related to land tenure and agriculture in Nepal. Kathmandu Univ. J. Sci. Eng. Technol. 2010, 6, 133–141. [Google Scholar] [CrossRef]
  46. Paudel, K.P.; Tamang, S.; Shrestha, K.K. Transforming land and livelihood: Analysis of agricultural land abandonment in the Mid Hills of Nepal. J. For. Livelihood 2014, 12, 11–19. [Google Scholar]
  47. Paudel, B.; Gao, J.; Zhang, Y.; Wu, X.; Li, S.; Yan, J. Changes in cropland status and their driving factors in the Koshi River basin of the Central Himalayas, Nepal. Sustainability 2016, 8, 933. [Google Scholar] [CrossRef] [Green Version]
  48. Chalise, H.N. Demographic situation of population ageing in Nepal. Kathmandu Univ. Med J. 2006, 4, 354–362. [Google Scholar]
  49. Sharma, K. The political economy of civil war in Nepal. World Dev. 2006, 34, 1237–1253. [Google Scholar] [CrossRef]
  50. Campbell, B. Rhetorical routes for development: A road project in Nepal. Contemp. South Asia 2010, 18, 267–279. [Google Scholar] [CrossRef]
  51. CBS. National Population and Housing Census 2011; National Report; National Planning Commission, Government of Nepal: Kathmandu, Nepal, 2012.
  52. Dahal, B.M.; Nyborg, I.; Sitaula, B.K.; Bajracharya, R.M. Agricultural intensification: Food insecurity to income security in a mid-hill watershed of Nepal. Int. J. Agric. Sustain. 2009, 7, 249–260. [Google Scholar] [CrossRef]
  53. Haddaway, N.R.; Styles, D.; Pullin, A.S. Evidence on the environmental impacts of farm land abandonment in high altitude/mountain regions: A systematic map. Environ. Evid. 2014, 3, 17. [Google Scholar] [CrossRef] [Green Version]
  54. Pointereau, P. Analysis of Farmland Abandonment and the Extent and Location of Agricultural Areas That Are Actually Abandoned or Are in Risk to be Abandoned; EUR-OP: JRC Scientific and Technical Report; European Commission Joint Research Centre, Institute for Environment an Sustainability, 2008. [Google Scholar]
  55. Coppola, A. An economic perspective on land abandonment processes. In Proceedings of the AVEC Workshop on Effects of Land Abandonment and Global Change on Plant and Animal Communities, Capri, Italy, 11–13 October 2004. [Google Scholar]
  56. Sirami, C.; Brotons, L.; Burfield, I.; Fonderflick, J.; Martin, J.L. Is land abandonment having an impact on biodiversity? A meta-analytical approach to bird distribution changes in the north-western Mediterranean. Biol. Conserv. 2008, 141, 450–459. [Google Scholar] [CrossRef]
  57. Plieninger, T.; Hui, C.; Gaertner, M.; Huntsinger, L. The impact of land abandonment on species richness and abundance in the Mediterranean Basin: A meta-analysis. PLoS ONE 2014, 9, e98355. [Google Scholar] [CrossRef]
  58. Zagaria, C.; Schulp, C.J.; Kizos, T.; Verburg, P.H. Perspectives of farmers and tourists on agricultural abandonment in east Lesvos, Greece. Reg. Environ. Chang. 2018, 18, 1467–1479. [Google Scholar] [CrossRef] [Green Version]
  59. Benjamin, K.; Bouchard, A.; Domon, G. Abandoned farmlands as components of rural landscapes: An analysis of perceptions and representations. Landsc. Urban Plan. 2007, 83, 228–244. [Google Scholar] [CrossRef]
  60. Keenleyside, C.; Tucker, G.; McConville, A. Farmland Abandonment in the EU: An Assessment of Trends and Prospects; Institute for European Environmental Policy: London, UK, 2010. [Google Scholar]
  61. MacDonald, D.; Crabtree, J.; Wiesinger, G.; Dax, T.; Stamou, N.; Fleury, P.; Lazpita, J.G.; Gibon, A. Agricultural abandonment in mountain areas of Europe: Environmental consequences and policy response. J. Environ. Manag. 2000, 59, 47–69. [Google Scholar] [CrossRef]
  62. Mahoney, J. Toward a unified theory of causality. Comp. Political Stud. 2008, 41, 412–436. [Google Scholar] [CrossRef] [Green Version]
  63. Ummenhofer, C.C.; England, M.H.; McIntosh, P.C.; Meyers, G.A.; Pook, M.J.; Risbey, J.S.; Gupta, A.S.; Taschetto, A.S. What causes southeast Australia’s worst droughts? Geophys. Res. Lett. 2009, 36. [Google Scholar] [CrossRef] [Green Version]
  64. Geist, H.J.; Lambin, E.F. Proximate Causes and Underlying Driving Forces of Tropical DeforestationTropical forests are disappearing as the result of many pressures, both local and regional, acting in various combinations in different geographical locations. BioScience 2002, 52, 143–150. [Google Scholar] [CrossRef]
  65. Meyfroidt, P. Approaches and terminology for causal analysis in land systems science. J. Land Use Sci. 2016, 11, 501–522. [Google Scholar] [CrossRef]
  66. Guzha, A.; Rufino, M.C.; Okoth, S.; Jacobs, S.; Nóbrega, R. Impacts of land use and land cover change on surface runoff, discharge and low flows: Evidence from East Africa. J. Hydrol. Reg. Stud. 2018, 15, 49–67. [Google Scholar] [CrossRef]
  67. Kiruki, H.M.; van der Zanden, E.H.; Malek, Ž.; Verburg, P.H. Land cover change and woodland degradation in a charcoal producing semi-arid area in Kenya. Land Degrad. Dev. 2017, 28, 472–481. [Google Scholar] [CrossRef] [Green Version]
  68. Kristensen, L.S.; Thenail, C.; Kristensen, S.P. Landscape changes in agrarian landscapes in the 1990s: The interaction between farmers and the farmed landscape. A case study from Jutland, Denmark. J. Environ. Manag. 2004, 71, 231–244. [Google Scholar] [CrossRef]
  69. Mishra, A.K.; Raggi, M.; Viaggi, D. Determinants of Farm Exit: A comparison between Europe and United States. Paper Prepared for Presentation at the 114th EAAE Seminar ‘Structural Change in Agriculture’, Berlin, Germany, 15–16 April 2010. [Google Scholar]
  70. Lieskovský, J.; Bezák, P.; Špulerová, J.; Lieskovský, T.; Koleda, P.; Dobrovodská, M.; Bürgi, M.; Gimmi, U. The abandonment of traditional agricultural landscape in Slovakia–Analysis of extent and driving forces. J. Rural Stud. 2015, 37, 75–84. [Google Scholar] [CrossRef]
  71. Long, H.; Tang, G.; Li, X.; Heilig, G.K. Socio-economic driving forces of land-use change in Kunshan, the Yangtze River Delta economic area of China. J. Environ. Manag. 2007, 83, 351–364. [Google Scholar] [CrossRef]
  72. Sharma, P.; Rai, S. Carbon sequestration with land-use cover change in a Himalayan watershed. Geoderma 2007, 139, 371–378. [Google Scholar] [CrossRef]
  73. Bojnec, Š.; Latruffe, L. Farm size, agricultural subsidies and farm performance in Slovenia. Land Use Policy 2013, 32, 207–217. [Google Scholar] [CrossRef]
  74. Vranken, L.; Macours, K.; Noev, N.; Swinnen, J. Property rights imperfections and asset allocation: Co-ownership in Bulgaria. J. Comp. Econ. 2011, 39, 159–175. [Google Scholar] [CrossRef] [Green Version]
  75. Sikor, T.; Müller, D.; Stahl, J. Land fragmentation and cropland abandonment in Albania: Implications for the roles of state and community in post-socialist land consolidation. World Dev. 2009, 37, 1411–1423. [Google Scholar] [CrossRef]
  76. Ciaian, P.; Swinnen, J.F. Credit market imperfections and the distribution of policy rents. Am. J. Agric. Econ. 2009, 91, 1124–1139. [Google Scholar] [CrossRef] [Green Version]
  77. Müller, D.; Kuemmerle, T.; Rusu, M.; Griffiths, P. Lost in transition: Determinants of post-socialist cropland abandonment in Romania. J. Land Use Sci. 2009, 4, 109–129. [Google Scholar] [CrossRef]
  78. CBS. Population Monograph of Nepal 2014, Economic Demography; Government of Nepal (GoN), National Planning Commission Secretariat, Central Bureau of Statistics, Ramshah Path: Kathmandu, Nepal, 2014.
  79. Aryal, K.R. Disaster vulnerability in Nepal. Int. J. Disaster Risk Reduct. 2014, 9, 137–146. [Google Scholar] [CrossRef]
  80. Gautam, A.; Shivakoti, G.; Webb, E. A review of forest policies, institutions, and changes in the resource condition in Nepal. Int. For. Rev. 2004, 6, 136–148. [Google Scholar] [CrossRef]
  81. Raut, N.; Sitaula, B.K.; Bajracharya, R.M. Agricultural intensification: Linking with livelihood improvement and environmental degradation in mid-hills of Nepal. J. Agric. Environ. 2010, 11, 83–94. [Google Scholar] [CrossRef] [Green Version]
  82. Bhattarai, S. The Bola or Parma of the Newar in Manamaiju Village. The Significance of a Farm Labor Exchange System among Indigenous Peasants in Nepal. Masters Thesis, Universitetet i Tromsø, Tromsø, Norway, 2006. [Google Scholar]
  83. Poudel, D.D.; Duex, T.W. Vanishing Springs in Nepalese Mountains: Assessment of Water Sources, Farmers’ Perceptions, and Climate Change Adaptation. Mt. Res. Dev. 2017, 37, 35–46. [Google Scholar] [CrossRef]
  84. Paudel, G.S.; Thapa, G.B. Changing farmers’ land management practices in the hills of Nepal. Environ. Manag. 2001, 28, 789–803. [Google Scholar] [CrossRef]
  85. Blaikie, P.; Cameron, J.; Seddon, D. Understanding 20 years of change in West-Central Nepal: Continuity and change in lives and ideas. World Dev. 2002, 30, 1255–1270. [Google Scholar] [CrossRef]
  86. Lam, W.F.; Ostrom, E. Analyzing the dynamic complexity of development interventions: Lessons from an irrigation experiment in Nepal. Policy Sci. 2010, 43, 1–25. [Google Scholar] [CrossRef]
  87. Uddin, K.; Shrestha, H.L.; Murthy, M.; Bajracharya, B.; Shrestha, B.; Gilani, H.; Pradhan, S.; Dangol, B. Development of 2010 national land cover database for the Nepal. J. Environ. Manag. 2015, 148, 82–90. [Google Scholar] [CrossRef]
  88. Brenner, N. Theses on urbanization. Public Cult. 2013, 25, 85–114. [Google Scholar] [CrossRef]
  89. Bakrania, S. Urbanisation and Urban Growth in Nepal; GSDRC, University of Birmingham: Birmingham, UK, 2015. [Google Scholar]
  90. Kollmair, M.; Manandhar, S.; Subedi, B.; Thieme, S. New figures for old stories: Migration and remittances in Nepal. Migr. Lett. 2006, 3, 151–160. [Google Scholar] [CrossRef] [Green Version]
  91. Subedi, B.P. International migration in Nepal: Towards an analytical framework. Contrib. Nepal. Stud. 1991, 18, 83–102. [Google Scholar]
  92. CBS. Population Monograph of Nepal, Population Dynamics; Government of Nepal (GoN), National Planning Commission Secretariat, Central Bureau of Statistics, Ramshah Path: Kathmandu, Nepal, 2014.
  93. Gumma, M.K.; Gauchan, D.; Nelson, A.; Pandey, S.; Rala, A. Temporal changes in rice-growing area and their impact on livelihood over a decade: A case study of Nepal. Agric. Ecosyst. Environ. 2011, 142, 382–392. [Google Scholar] [CrossRef]
  94. Lam, L.M. Park, Hill Migration and Changes in Household Livelihood Systems of Rana Tharus in Far-Western Nepal. Ph.D. Thesis, School of Social Sciences, Ahmedabad, India, 2009. [Google Scholar]
  95. Paudel, G.S.; Thapa, G.B. Impact of social, institutional and ecological factors on land management practices in mountain watersheds of Nepal. Appl. Geogr. 2004, 24, 35–55. [Google Scholar] [CrossRef]
  96. Manandhar, S.; Vogt, D.S.; Perret, S.R.; Kazama, F. Adapting cropping systems to climate change in Nepal: A cross-regional study of farmers’ perception and practices. Reg. Environ. Chang. 2011, 11, 335–348. [Google Scholar] [CrossRef]
  97. Zurick, D.N. Historical links between settlement, Ecology, and Politics in the Mountains of West Nepal. Hum. Ecol. Himalaya 1989, 17, 229–255. [Google Scholar] [CrossRef]
  98. Shrestha, N.R. Frontier settlement and landlessness among hill migrants in Nepal Tarai. Ann. Assoc. Am. Geogr. 1989, 79, 370–389. [Google Scholar] [CrossRef]
  99. Kosinski, L.A.; Elahi, K.M. Population Redistribution and Development in South Asia; Springer: Dordrecht, The Netherlands, 1985. [Google Scholar]
  100. Skeldon, R. Migration in South Asia: An overview. In Population Redistribution and Development in South Asia; Springer: Dordrecht, The Netherlands, 1985; pp. 37–63. [Google Scholar]
  101. Rana, R.B.; Garforth, C.; Sthapit, B.; Jarvis, D. Influence of socio-economic and cultural factors in rice varietal diversity management on-farm in Nepal. Agric. Hum. Values 2007, 24, 461–472. [Google Scholar] [CrossRef]
  102. UNDP. Nepal Human Development Report 2014: Beyond Geography, Unlocking Human Capital; National Planning Commission: Kathmandu, Nepal, 2014. [Google Scholar]
  103. Devkota, S.R. Socio-economic Development in Nepal: Past Mistakes and Future Possibilities. South Asia Econ. J. 2007, 8, 285–315. [Google Scholar] [CrossRef]
  104. Maharjan, A.; Bauer, S.; Knerr, B. International migration, remittances and subsistence farming: Evidence from Nepal. Int. Migr. 2013, 51, e249–e263. [Google Scholar] [CrossRef]
  105. Sharma, R.H.; Awal, R. Hydropower development in Nepal. Renew. Sustain. Energy Rev. 2013, 21, 684–693. [Google Scholar] [CrossRef]
  106. Malik, K. Human Development Report 2014: Sustaining Human Progress: Reducing Vulnerabilities and Building Resilience; United Nations Development Programme: New York, NY, USA, 2014. [Google Scholar]
  107. CBS. Nepal Living Standards Survery (NLSS) 2010/11; Statistical Report Volume Two; Central Bureau Of Statistics, National Planning Commission, Government of Nepal: Kathmandu, Nepal, 2011.
  108. Pandit, B.H.; Wagley, M.P.; Neupane, R.P.; Adhikary, B.R. Watershed management and livelihoods: Lessons from Nepal. J. For. Livelihood 2007, 6, 67–75. [Google Scholar]
  109. Guha-Sapir, D.; Vos, F.; Below, R.; Ponserre, S. Annual Disaster Statistical Review 2011: The Numbers and Trends; Centre for Research on the Epidemiology of Disasters (CRED): Brussels, Belgium, 2012. [Google Scholar]
  110. MoHA, D.N.; UNDP, O. Nepal Disaster Report: The hazardscape and Vulnerability; Jagadamba Press: Kathmandu, Nepal, 2009. [Google Scholar]
  111. NSET. United Nations International Strategy for Disaster Reduction: Global Assessment Report on Poverty and Disaster Risk 2009: Global Assessment of Risk—Nepal Country Report (Final Draft); NSET Nepal: Kathmandu, Nepal, 2008. [Google Scholar]
  112. Uddin, K.; Shrestha, B. Assessing flood and flood damage using Remote Sensing: A case study from Sunsari, Nepal. In Proceedings of the 4th International Conference on Water and Flood Management, Rganized by Institute of Water and Flood Management (IWFM), Bangladesh University of Engineering and Technology, Dhaka, Bangladesh, 8–10 January 2011; pp. 293–301. [Google Scholar]
  113. Aryal, K.R. The history of disaster incidents and impacts in Nepal 1900–2005. Int. J. Disaster Risk Sci. 2012, 3, 147–154. [Google Scholar] [CrossRef] [Green Version]
  114. Edwards, P.; Rana, G.; Shrestha, A. Nepal: State of the Environment 2001; Published by United Nations Environment Program (UNEP) in collaboration with Ministry of Population and Government (MoPE); Government of Nepal: Kathmandu, Nepal, 2001.
  115. Jaquet, S.; Shrestha, G.; Kohler, T.; Schwilch, G. The effects of migration on livelihoods, land management, and vulnerability to natural disasters in the Harpan watershed in western Nepal. Mt. Res. Dev. 2016, 36, 494–506. [Google Scholar] [CrossRef] [Green Version]
  116. Niroula, G.; Thapa, G.B. Impacts of land fragmentation on input use, crop yield and production efficiency in the mountains of Nepal. Land Degrad. Dev. 2007, 18, 237–248. [Google Scholar] [CrossRef]
  117. Manjunatha, A.; Anik, A.R.; Speelman, S.; Nuppenau, E. Impact of land fragmentation, farm size, land ownership and crop diversity on profit and efficiency of irrigated farms in India. Land Use Policy 2013, 31, 397–405. [Google Scholar] [CrossRef]
  118. Neupane, R.P.; Sharma, K.R.; Thapa, G.B. Adoption of agroforestry in the hills of Nepal: A logistic regression analysis. Agric. Syst. 2002, 72, 177–196. [Google Scholar] [CrossRef]
  119. Bjønness, I.M. Mountain hazard perception and risk-avoiding strategies among the Sherpas of Khumbu Himal, Nepal. Mt. Res. Dev. 1986, 6, 277–292. [Google Scholar] [CrossRef]
  120. Regmi, M.C. Landownership in Nepal; University of California Press: Berkeley, CA, USA, 1976. [Google Scholar]
  121. Toffin, G. Urban fringes: Squatter and slum settlements in the Kathmandu Valley (Nepal). Contrib. Nepal. Stud. 2010, 37, 151–168. [Google Scholar]
  122. Pradhan, P.K. Population growth, migration and urbanisation. Environmental consequences in Kathmandu valley, Nepal. In Environmental Change and Its Implications for Population Migration; Springer: Dordrecht, The Netherlands, 2004; pp. 177–199. [Google Scholar]
  123. Hachhethu, K. Nepali politics: Political parties, political crisis and problems of governance. In Domestic Conflict and Crisis of Governability in Nepal; CNAS (Centre for Nepal and Asian Studies): Kathmandu, Nepal, 2000; pp. 1–19. [Google Scholar]
  124. Webster, N. Nepal: Governance and democracy in a frail state. In Trysts with Democracy: Political Practice in South Asia; Madsen, S.T., Nielsen, K.B., Skoda, U., Eds.; Anthem Press: London, UK, 2011; pp. 195–213. [Google Scholar]
  125. Lawoti, M. Evolution and growth of the Maoist insurgency in Nepal. In The Maoist Insurgency in Nepal; Routledge: London, UK, 2009; pp. 23–50. [Google Scholar]
  126. MoPE. Nepal National Action Programme (NAP) on Land Degradation and Desertification under the United Nations Convenstions to Combat Desertification (UNCCD); Ministry of Population and Environment, Government of Nepal: Kathmandu, Nepal, 2016.
  127. Nepal Law Commission. Land Rules Act 2021 (1964); International Convention Centre, New Baneshwor: Kathmandu, Nepal.
  128. Gentle, P.; Thwaites, R.; Race, D.; Alexander, K.; Maraseni, T. Household and community responses to impacts of climate change in the rural hills of Nepal. Clim. Chang. 2018, 147, 267–282. [Google Scholar] [CrossRef]
  129. Bhattarai, K.R.; Vetaas, O.R. Variation in plant species richness of different life forms along a subtropical elevation gradient in the Himalayas, east Nepal. Glob. Ecol. Biogeogr. 2003, 12, 327–340. [Google Scholar] [CrossRef]
  130. Care Nepal. Preliminary Assessment for Piloting Payment for Ecosystem Services in Lamjung; Breifing Document; Care Nepal: Lalitpur, Nepal, 2014. [Google Scholar]
  131. Mandal, U.K. Geo-information-Based Soil Erosion Modeling for Sustainable Agriculture Development in Khadokhola Watershed, Nepal. In Land Cover Change and Its Eco-environmental Responses in Nepal; Springer: Dordrecht, The Netherlands, 2017; pp. 223–241. [Google Scholar]
  132. Ghimire, M. Impact of Hydro-Geological Processes and Land Degradation on Livelihood Strategy in the Churia and Terai Region Of Nepal: A Study Report on Hazard Mapping and Land Resources Management of the Jalad Khola Under the Jalad Integrated Watershed and Natural Resources Management (JIWAN) Program; CARE Nepal: Lalitpur, Nepal, 2008. [Google Scholar]
  133. Shrestha, D.P. Assessment of soil erosion in the Nepalese Himalaya: A case study in Likhu Khola Valley, Middle Mountain Region. Land Husb. 1997, 2, 59–80. [Google Scholar]
  134. Chaudhary, S.; Wang, Y.; Khanal, N.; Xu, P.; Fu, B.; Dixit, A.; Yan, K.; Liu, Q.; Lu, Y. Social Impact of Farmland Abandonment and Its Eco-Environmental Vulnerability in the High Mountain Region of Nepal: A Case Study of Dordi River Basin. Sustainability 2018, 10, 2331. [Google Scholar] [CrossRef] [Green Version]
  135. Usher, P.J. Traditional Ecological Knowledge in Environmental Assessment and Management. Arctic 2000, 53, 183–193. [Google Scholar] [CrossRef]
  136. Pant, L.P.; Kc, K.B.; Fraser, E.D.; Shrestha, P.K.; Lama, A.B.; Jirel, S.K.; Chaudhary, P. Adaptive transition management for transformations to agricultural sustainability in the Karnali Mountains of Nepal. Agroecol. Sustain. Food Syst. 2014, 38, 1156–1183. [Google Scholar] [CrossRef]
  137. LRMP. Land Capability Map. In Land Resource Mapping Project, Kathmandu (LRMP); Kenting Earth Sciences Limited: Ottawa, ON, Canada; Majestys Government of Nepal: Kathmandu, Nepal, 1986. [Google Scholar]
  138. Loveland, T.R.; Reed, B.C.; Brown, J.F.; Ohlen, D.O.; Zhu, Z.; Yang, L.; Merchant, J.W. Development of a global land cover characteristics database and IGBP DISCover from 1 km AVHRR data. Int. J. Remote Sens. 2000, 21, 1303–1330. [Google Scholar] [CrossRef]
  139. Hansen, M.C.; Reed, B. A comparison of the IGBP DISCover and University of Maryland 1 km global land cover products. Int. J. Remote Sens. 2000, 21, 1365–1373. [Google Scholar] [CrossRef]
  140. Fonte, C.; Minghini, M.; Patriarca, J.; Antoniou, V.; See, L.; Skopeliti, A. Generating up-to-date and detailed land use and land cover maps using OpenStreetMap and GlobeLand30. Isprs Int. J. Geo-Inf. 2017, 6, 125. [Google Scholar] [CrossRef]
  141. Lesschen, J.; Cammeraat, L.; Nieman, T. Erosion and terrace failure due to agricultural land abandonment in a semi-arid environment. Earth Surf. Process. Landf. J. Br. Geomorphol. Res. Group 2008, 33, 1574–1584. [Google Scholar] [CrossRef]
  142. Leal Filho, W.; Mandel, M.; Al-Amin, A.Q.; Feher, A.; Chiappetta Jabbour, C.J. An assessment of the causes and consequences of agricultural land abandonment in Europe. Int. J. Sustain. Dev. World Ecol. 2017, 24, 554–560. [Google Scholar] [CrossRef] [Green Version]
  143. Tarolli, P.; Preti, F.; Romano, N. Terraced landscapes: From an old best practice to a potential hazard for soil degradation due to land abandonment. Anthropocene 2014, 6, 10–25. [Google Scholar] [CrossRef]
  144. Giri, B.R.; Xie, Y.; Baral, P.; Bikram, R. Significant Contribution of Community Forests to Users’ Household Income in Far-West Mid-Hill of Nepal. Int. J. Sci. 2018, 7, 36–55. [Google Scholar]
  145. Avouac, J.P. Mountain building, erosion, and the seismic cycle in the Nepal Himalaya. Adv. Geophys. 2003, 46, 1–80. [Google Scholar]
  146. Höchtl, F.; Lehringer, S.; Konold, W. “Wilderness”: What it means when it becomes a reality—A case study from the southwestern Alps. Landsc. Urban Plan. 2005, 70, 85–95. [Google Scholar] [CrossRef]
Figure 1. Frameworks for the causes of farmland abandonment and the underlying driving forces, adapted from Reference [64].
Figure 1. Frameworks for the causes of farmland abandonment and the underlying driving forces, adapted from Reference [64].
Land 09 00084 g001
Figure 2. Map of Nepal.
Figure 2. Map of Nepal.
Land 09 00084 g002
Figure 3. Collection of literatures to collect and extract information for farmland abandonment and its driving factors in Nepal. (INGOs indicates International Non-governmental organizations).
Figure 3. Collection of literatures to collect and extract information for farmland abandonment and its driving factors in Nepal. (INGOs indicates International Non-governmental organizations).
Land 09 00084 g003
Figure 4. Spatial distribution of farmland abandonment in Nepal, 2010/11.
Figure 4. Spatial distribution of farmland abandonment in Nepal, 2010/11.
Land 09 00084 g004
Figure 5. Urban centers and the population in Nepal, 1961–2014. Data Source: Central Bureau of Statistics 2019, Government of Nepal.
Figure 5. Urban centers and the population in Nepal, 1961–2014. Data Source: Central Bureau of Statistics 2019, Government of Nepal.
Land 09 00084 g005
Table 1. List of data and sources for shaping of farmland abandonment in Nepal.
Table 1. List of data and sources for shaping of farmland abandonment in Nepal.
Serial NumberData SourceData TypeTime PeriodReferences
1Population Monograph of Nepal, Volume I, Population dynamicsStatistics1961,1971,1981,1991, 2001, 2011Central Bureau of Statistics (CBS), Government of Nepal
2Population Monograph of Nepal, Volume II, Social DemographyStatistics1961,1971,1981,1991, 2001, 2011Central Bureau of Statistics (CBS), Government of Nepal
3Population Monograph of Nepal, Volume III, Economic DemographyStatistics1961,1971,1981,1991, 2001, 2011Central Bureau of Statistics (CBS), Government of Nepal
4Land use land cover map of NepalGIS1986Land Resource Mapping Project (LRMP), Survey Department, Government of Nepal
5Land use land cover map of NepalGIS2000 and 2010International Centre for Integrated Mountain Development (ICIMOD) (http://rds.icimod.org)
National Living Standard SurveyStatistics2010/11Central Bureau of Statistics (CBS), Government of Nepal
7Statistical Information on Nepalese Agriculture,Statistics2012/2013Central Bureau of Statistics (CBS), Government of Nepal
8Quarterly Economic Bulletin of Nepal Rastra BankStatistics2015, 2016, 2017Nepal Rastra Bank, Central office, Kathmandu, Nepal
Table 2. Temporal variation of cultivated area and farmland abandonment in Nepal (1961–2017).
Table 2. Temporal variation of cultivated area and farmland abandonment in Nepal (1961–2017).
Year1961/621971/721981/821991/922001/022010/112014/152015/162016/17
Cultivated land (104 ha)1685.41654.02463.72968.04061.63091.02599.22579.12548.8
Farmland abandonment (’000 ha) 31.4 970.6491.820.130.3
% of change as compared to cultivated land during the time period −1.949.020.536.8−23.9−15.9−0.8−1.2
Table 3. Land ownership and fragmentation in Nepal. Data Source: Reference [78].
Table 3. Land ownership and fragmentation in Nepal. Data Source: Reference [78].
Farm Size Class (ha)High MountainsMiddle and Low Mountains
% of HouseholdsDistribution of Agricultural Land (%)% of HouseholdsDistribution of Agricultural Land (%)
Less than 0.13.40.38.10.7
0.10–0.2517.24.118.65.2
0.25–0.5028.315.028.517.0
0.50–131.330.829.034.1
1–216.731.513.230.0
2 and over3.218.42.613.0

Share and Cite

MDPI and ACS Style

Chaudhary, S.; Wang, Y.; Dixit, A.M.; Khanal, N.R.; Xu, P.; Fu, B.; Yan, K.; Liu, Q.; Lu, Y.; Li, M. A Synopsis of Farmland Abandonment and Its Driving Factors in Nepal. Land 2020, 9, 84. https://0-doi-org.brum.beds.ac.uk/10.3390/land9030084

AMA Style

Chaudhary S, Wang Y, Dixit AM, Khanal NR, Xu P, Fu B, Yan K, Liu Q, Lu Y, Li M. A Synopsis of Farmland Abandonment and Its Driving Factors in Nepal. Land. 2020; 9(3):84. https://0-doi-org.brum.beds.ac.uk/10.3390/land9030084

Chicago/Turabian Style

Chaudhary, Suresh, Yukuan Wang, Amod Mani Dixit, Narendra Raj Khanal, Pei Xu, Bin Fu, Kun Yan, Qin Liu, Yafeng Lu, and Ming Li. 2020. "A Synopsis of Farmland Abandonment and Its Driving Factors in Nepal" Land 9, no. 3: 84. https://0-doi-org.brum.beds.ac.uk/10.3390/land9030084

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop