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Octa Journal of Environmental Research Jan.–Mar., 2017
International Peer-Reviewed Journal ISSN 2321 3655
Oct. Jour. Env. Res. Vol. 5(1): 022-031
Available online http://www.sciencebeingjournal.com
Octa Journal of Environmental Research
Review Article
AGROFORESTRY SYSTEM: AN OPPORTUNITY FOR CARBON
SEQUESTRATION AND CLIMATE CHANGE ADAPTATION IN THE MID-HILLS OF
NEPAL
Deepa Paudela*, Krishna Raj Tiwaria, Roshan Man Bajracharyab, Nani Rautb, Bishal K. Sitaulac
a.Institute of Forestry, Hariyokharka, Pokhara P.O. Box 33700, Nepal
b.Department of Aquatic Ecology Center, Kathmandu University, Kavre P.O. Box 6250, Kathmandu, Nepal
c.Department of International Environment and Development Studies (Noragric), Norwegian University of Life Sciences
(UMB), Box 5003, 1432, Norway
Corresponding Author’s E-mail: skt.deepa@gmail.com
Abstract: Agroforestry is a natural resource management system that integrates trees, crops and
animals in a manner that produces two or more crops from a small unit of land sustainably. It is a
sustainable land use system that is ecologically and economically sound and offers the added benefit of
carbon sequestration. This paper reviews agroforestry practices in Nepal and its role in carbon
sequestration and climate change adaptation. Agroforestry is being practiced in the mid-hills of Nepal for
the requirement of daily needs like fodder, food and fuel as a substitute to forests. The fodder trees,
fuelwood and fruit trees around the farm have an important role in diet supplement as well as in carbon
storage. Various researchers have estimated carbon content in agroforestry range from between 12 and
228 MgC/ha with a median value of 95 Mg/ha in the terrestrial agro ecosystem. In Nepal, the mid-hills
agroforestry is estimated to store about 48.60 ton C per hectare. Agro-ecosystems also contribute to
the mitigation of the climate change and are being an adaptation strategy for the farmers.
Keywords: Adaptation;Agroforestry; Carbon sequestration.
PostalAddress: Institute of Forestry, Pokhara -15, Hariyokharka 33700, Nepal, Phone: +977-61-431563.
INTRODUCTION
Agroforestry is an interface between
agriculture and forestry as a promising and
sustainable land use practice in developing
countries where trees on farmland form an
integral part of the farming system. Agroforestry
deliberately combines agriculture and forestry
to create integrated and sustainable land-use
systems including annual crops and trees.
However, agroforestry has been defined in
various ways. It has been called a dynamic,
ecologically based, natural resources
management system that, through the
integration of trees on farms and in the
agricultural landscape, diversifies and sustains
production for increased social, economic and
environmental benefits for land users at all
levels (Leaky, 1996; ICRAF, 2006).
Combination of trees on crops is an old practice
defined by Nair (1993) as a land use system
that integrates trees, crops, and animals in a
way that is scientifically sound, ecologically
desirable, practically feasible land socially
acceptable to the farmers. In earlier times
agroforestry was practiced by those farmers
whose ultimate goal was food production and
they retained tree as supportive for the
agriculture crops. This is accepted as holistic
applied science that has potential for
addressing many of the ecological and
livelihood services for the benefit of farmers and
rural communities alike (Regmi, 2003).In other
words agroforestry has been claimed, to have
the possibility of improving agricultural land use
systems and providing lasting benefits and
alleviating adverse environmental effects at
local and global levels (Alao et al., 2011). The
Paudel et al., 2017; Agroforestry System: An Opportunity for Carbon Sequestration and Climate Change
Adaptation in the Mid-Hills of Nepal
Oct. Jour. Env. Res. Vol 5(1):022-031
023
practice of introducing trees in farming has
played a significant role in enhancing land
productivity and improving livelihoods in both
developed and developing countries. In
terrestrial ecosystems, forests are considered
among the easiest means for enhancing carbon
capture and sequestration (Dahal and Kafle,
2013), Although, this is land use system having
tree and crops in a single unit of land with more
than two benefits the recognition of role of
forest trees in reducing emission of carbon is
more (Montagini et al., 2004). Agroforestry and
ecosystem conservation are key approaches in
the integration of climate change adaptation
and mitigation objectives, often generating
significant co-benefits for local ecosystems and
biodiversity (Matocha et al., 2012). At the same
time, FAO 2009 indicates land-based carbon
mitigation schemes, such as avoided
deforestation, reforestation, and agricultural and
agroforestry practices that sequester carbon in
vegetation and soil, can make a substantial
contribution to global climate change mitigation
with potential source of income to poor
farmers. In developing countries agroforestry
has been recognized as land use practice for
the small farmers with improving agroforestry
technique slowly and few studies has been
done in related to agroforestry in relation with
carbon and livelihood.Thus, the purpose of the
paper is to review the different practice of
agroforestry and their role in carbon
sequestration and climate change adaptation
focused particularly in midhills of Nepal.
AGROFORESTRY IN NEPAL
Geographically, diverse country with flat plains
of the Terai in the south and the sloping terrain
of the Mid-hills and snowy mountains in the
north (HMG/N, 2002). It covers 147,181 sq.km.
area where hills and high mountains cover
about 86% of the total land area and the
remaining 14% are the flatlands of the Terai
(NPC, 2012). Agriculture is the principal source
of food income and employment, which
employs 73.9% of its economically active
population (CBS, 2008) and contributes
approximately 34% to GDP (NRB, 2014). In
recent decades, Nepal’s population has grown
rapidly that’s why more people have required
increasing amounts of food and commodities
from agriculture and natural resources. The
land use of Nepal is changing day by day due
to climatic effect and insurgency in country
(Paudel et al., 2016) (Table 1). In midhills of
Nepal there is intermixing of tree with
agriculture land which indicates the peripheral
effects on natural forest (Uddin et al., 2015).
That’s why the recent assessment, done by
government of Nepal represent other woodland
as 4.38% where forest covers 40.36% and
combined together form 44.74% of the total
area of the country. The other wooded land
represents the tree on farm land and fallow land
with tree (DFRS, 2015).
Table 1. Land use change of Nepal from 1979-2015
Category
Percentage
1979 (LRMP)
1994 (NFI)
1999 (DFRS)
Uddinet al., 2015
Cultivated
20.10
21.00
21.00
29.83
Non cultivated
6.70
7.00
7.00
10.65
Forest
38.10
29.00
29.00
39.10
Shrubland
4.70
10.60
10.60
3.40
Grassland
11.90
12.00
12.00
7.90
Water
N/A
2.60
2.60
0.60
other
18.50
17.80
N/A
N/A
Compiled from Uddin et al., 2015 and Paudel, 2016
Land use changes combines and interacts
with social organization, religious beliefs, and
access to land and markets to give rise to a
wide variety of farming systems and great
variances within them (Mahat, 1987; Thapa,
1994) which in turn has resulted in several
agroforestry practices. The practice of
integrating and managing crops, livestock and
forestry for food security and livelihoods has a
long history in Nepal’s mid-hills (Gilmore and
Fisher, 1991; Garforth et al., 1997). Agriculture,
trees, and livestock are intertwined in the
Paudel et al., 2017; Agroforestry System: An Opportunity for Carbon Sequestration and Climate Change
Adaptation in the Mid-Hills of Nepal
Oct. Jour. Env. Res. Vol 5(1):022-031
024
Nepalese farming system which is practiced by
farmers themselves on a regular basis; hence
the sustainability of the farming system
depends on the continuous existence of tree
resources (Garforth et al., 1999). This system
traditionally produces a wide variety of products
from small unit of land, such as, timber,
fuelwood, leaf litter, fruits; vegetables etc. to
meet household needs with generating an
income opportunity to small holder farmers
(Regmi, 2003). Nepal’s hills are characterized
by steep slopes and limited cultivable land
(Gilmour et al., 2014). Most farmlands are
located on steep slopes where farmers practice
cereal-based land management, which requires
intensive soil tillage, particularly frequent
ploughing and hoeing. In that case, growing of
trees, shrubs and herbs species on private
lands to fulfill the basic household needs has
been a long established tradition in the
mountains of Nepal. Farmers maintain trees in
the farmland adopting several forms of
agroforestry, and collect fuel wood, leaf litter
and fodder from these trees for their
subsistence (Pandit et al., 2014). The practice
of agroforestry followed in Nepal can be broadly
categorized as: farm-based and forest-based.
The former include home gardens, trees on or
around agricultural fields, wood lots and
commercial crops under shade trees, and
intercropping of agricultural crops and
commercial trees (Gilmour et al., 2014).The
forest-based practices involve specific
agricultural practices associated with forests
where farmers collect food, fruits and gums
(Tejwani and Lai, 1992). Nowadays government
of Nepal is practicing leasehold forestry or
public land agroforestry, which also symbolizes
forest based agroforestry practice (CBD, 2014).
It has important implications, particularly
through the division of the institutional
landscape, including targeting communities,
institutional involvement and long-term
programs and strategic approaches (Gilmour et
al., 2014). In other words we can say that the
agroforestry played an important role in
sustaining a variety of ecosystem services and
practiced as adaptation tool (Jose, 2009). With
regard to agroforestry, it is a prevalent
traditional Nepalese farming practice that
involves integrating trees within cropping
systems on private land, as opposed to
community forestry on public land. The midhills
agroforestry system involves cultivation of crops
and useful plants under the natural tree canopy,
for example home gardens, tree on farmland,
mostly for household consumption (Tewari,
2008).
Table 2. Different types of Agroforestry practices adopted by farmers in midhills of Nepal.
Agroforestry
practices
Definition
Modified or adopted definition
Home garden
Spatial and temporal arrangement of
diverse trees, shrubs, herbs, and other
agricultural crops within a household
boundary, and managed using family
labor (Fernandes and Nair, 1986).
Generally 0.1 ha in land.
Vertical and horizontal management of agricultural
crops where household members are living
permanently within the same unit of land irrespective
of farm size (Modified from Nair 1986). It provides
60% of total fruit and vegetable consumption in a 5–
6 member household in mid-hills of Nepal (Sthapit et
al., 2010).
Tree on farm land
(strip or scattered
tree)
The number of trees or shrubs scattered
or stripped among crops or pastures and
along farm boundaries (FAO,1985).
Cultivation of multipurpose trees or fruit trees on
boundary of the farmland where trees are on strip or
scattered and agriculture crops (cereals, vegetables)
are intercropped).
For the purpose of soil conservation farmers are
adopting this type of agroforestry practice in mid hills
of Nepal.
Orchards (Block
plantation)
The planting of trees or shrubs that are
maintained for food production comprise
of fruit, vegetable (FAO,1985).
Block plantation of fruits or multipurpose trees on
farmland where agriculture crops (cereals,
vegetables) are either intercropped or cultivated on
adjoining land.
For the protection of agriculture land from soil
erosion, water spring drying up etc.(Neupane et al.,
2002).
Paudel et al., 2017; Agroforestry System: An Opportunity for Carbon Sequestration and Climate Change
Adaptation in the Mid-Hills of Nepal
Oct. Jour. Env. Res. Vol 5(1):022-031
025
Agroforestry
practices
Definition
Modified or adopted definition
Silvi- pasture
The trees and shrubs may be used
primarily to produce fodder for livestock
or they may be grown for timber,
fuelwood, fruit or to improve the soil
(Nair,1999).
Fallow land with at-least one tree species were
livestock are either grazed seasonally or
permanently throughout the year.
Commercial crop
under tree shade
Growing of shade bearer cash crop under
tree shade is practice of agroforestry
system. Such as coffee, Cocoa, tea, etc.
are grown with tree species.
In this system, agricultural cash crops such as tea
and coffee are grown along with tree crops. This is
used for the commercialization of the product.
(Amatya, 1999).This is also known as improved
agroforestry in Nepal.
The traditional farming system in Nepal has not
been adequate to sustain agricultural
production and present level of food
requirements (Neupane, 2002). Agroforestry
practice in Nepal seems like recent practices
followed in developed countries but they are not
scientifically managed. The challenge towards
the traditional agroforestry practice in mid-hills
is to manage scientifically for the betterment of
the livelihoods, sustainable production and
improvement of socio-economic condition of the
people.
CARBON SEQUESTRATION
THROUGH AGROFORESTRY
Trees in agroforestry systems are an important
resource providing products and services to the
society. It has unique role in stabilizing the
atmospheric carbon dioxide concentration and
reducing the carbon emissions or on increasing
the carbon sink in different land use system
(Murthy et al., 2013). Carbon emission is higher
from deforestation and forest degradation which
can be managed through the sustainable
management of land and forests, and
enhancement of forest C stocks through
agroforestry can be considered as one of the
main options for reducing greenhouse gases in
atmosphere (Nair et. al., 2012). Agroforestry
systems have indirect effects on carbon
sequestration because they reduce harvesting
pressure on natural forests as because trees
are the largest source of sinks for terrestrial
carbon. Nowadays, there is a growing attention
in the role of different types of land Carbon
sequestration in the long term storage of carbon
in oceans, soils, vegetation (especially forests),
and geologic formations and carbon storage in
different agroforestry system (ESA, 2001).
Carbon sequestration rate of soil depends upon
the input of dead organic matter provided by
plants, soil properties such as soil structures
and their aggregations, and climate (Lal, 2004).
Whereas, Tree-based agroforestry systems are
a preferred method for aboveground biomass C
sequestration as compared to treeless
pastures, there is evidence that C storage in
deep soil horizons is greater (Takimoto et al.,
2009). The available estimates of C stored in
agroforestry range from 0.29 to 15.21 Mg
C/ha/year above ground, and 30–300 Mg C/ha
up to 1 m depth in the soil (Nair et al., 2010).
Different agroforestry system have different rate
of carbon sequestration in different region
shown in Table 3.
Table 3. Examples of various agroforestry practices with carbon stock
S.No.
Region
AF practices
Carbon stock
Reference
1.
West Africa
Fodder bank AF
0.29 MgC/ha/yr
Nair, 2009
2.
Puerto Rico
Mixed species
15.29 MgC/ha/yr
Nair, 2009
3.
Costa Rica
Silvopastoral
173 Mg C/ha/yr
Nair, 2009
4.
Ecuador
Silvopastoral in above ground
7- 41 MgC/ha
McGroody et al., 2015
5.
Philippines
Mixed multi story system
161.52 MgC/ha
Mildrade et al., 2012
6.
Indonesia
Homegarden system
107 C ton/ha
Roshetko et al., 1999
7.
Indonesia
Agroforestry system
287.9 C/t/ha
Eutis, 2003
8.
Srilanka
Homegarden
10-145Mg/ha/yr
Mattson et al., 2013
9.
India
Poplar based AF system
3.8- 4.82 t/ha/yr
Chauhan et al., 2015
10.
India
Home garden
16-36 Mg/ha/yr
Singh and Panday, 2011
11.
Nepal
Midhills agroforestry
48.6 t/ha/yr
Panditet al., 2012
Paudel et al., 2017; Agroforestry System: An Opportunity for Carbon Sequestration and Climate Change
Adaptation in the Mid-Hills of Nepal
Oct. Jour. Env. Res. Vol 5(1):022-031
026
Another study done by Albrecht et al.
(2003) showed that the carbon sequestration
potential of agroforestry systems is estimated to
be between 12 and 228 Mg C/ha with a median
value of 95 Mg C/ha. Adoption of agroforestry
practices has greater potential to increase C
sequestration of predominantly agriculture
dominated landscapes than monocrop
agriculture (Nair et al., 2009). Beside that
agroforestry has been recognized to bea
distinct position as a carbon sequestration
strategy because of its applicability in
agricultural lands as well as in reforestation
programs (Cairns and Meganck 1994).
Agroforestry systems show significant carbon
accumulation in living biomass, as well as soil
carbon, demonstrating the potential to offer the
environmental service of carbon sequestration.
Soil C stocks have been demonstrated to
generally be larger in agroforestry systems
compared to conventional cropping systems
(Kumar and Nair, 2011).In Nepal, Pandit et al.,
(2012) estimated that a total of 48.60 ton C per
hectare whereas Bajracharya et al., (2015)
found that leasehold agroforestry in cool agro-
ecological has more carbon stock than
conventional agriculture practice. Forestry is
considered to encompass more broadly the
larger landscape beyond individual farms,
where private farmland, common access forest
and grazing land, farm animals, water
resources as well as household members, all
interact. KC (2011) estimated that CO2
emissions from AF systems in Nepal were 0.15
% of the total global carbon sequestered
through AF, which is considered to be a huge
amount relative to the country’s size. In the
country, high carbon stocks and sequestration
potential of forest land have been well
documented by numerous researchers as well
as research and survey department (Dahal and
Kafle 2013). However, AF practices improve
food and nutritional needs and mitigate
environmental degradation by combining trees
and crops (Nair, 2007).
Contribution of Agroforestry to Climate
change Adaption and Mitigation
Climate change due to addition of GHGs has
been one of the biggest issues for the human
welfare in the world (IPCC, 2001). Developing
countries are going to accept the effect of
climate change and are suffering from its
negative impacts with consequences the
vulnerability in the area.The outward fluctuation
of Carbon dioxide, Nitrous oxide and Methane
can be reduced through better management of
agroforestry system which will contribute
significantly in reducing GHG emissions and
mitigation that’s why agroforestry system has
been identified as a long term sink (Verocht et
al., 2007). In developing countries adaptation is
concern and critical because the vulnerability is
high and ability to adapt is low. In that way,
climate change is expected to affect food and
water resources that are critical for livelihoods
(Hassan 2008). Adaptation is necessary to deal
with adverse climatic stresses and hazards and
to take the opportunities such as new
innovations, which can be both to current,
actual or projected conditions (Smith et
al.,1999). Adaptation to climate change is not
something that must start from scratch. It is an
incremental process that can build upon a long
history of previous adaption. The new thing is
the need to adapt much more rapidly because
of the impact of human activities on climate
(Burton 2000). Besides adaptation mitigation is
also important in the climate change aspect. It
means, mitigation is needed to reduce the
impacts and allow for adaptation to takes place,
for ecosystems these boundaries are generally
narrower for human systems. Because
mitigation measures will not be able to
immediately avoid global warming (Parry et al.,
2007) adaptive measurements will be needed
to avoid the negative consequences of climate
change. On the longer term mitigation
measures will be able to avoid further warming
or even reduce the effect. In developing
countries climate change is significantly
affecting the agricultural sector,leading to
serious consequences related to food
production and food security, with bigger
impacts on small-holder farmers and the poor
(IPCC, 2007).
Agroforestry knowledge is being adapted in
rural and urban area to address the challenge
of climate change. Agroforestry is suitable
Paudel et al., 2017; Agroforestry System: An Opportunity for Carbon Sequestration and Climate Change
Adaptation in the Mid-Hills of Nepal
Oct. Jour. Env. Res. Vol 5(1):022-031
027
practice to assist in creating productive and
healthy farm and ranch operations,it has the
potential to contribute to both climate change
mitigation and adaptation by sequestering
carbon, reducing GHG emissions, enhancing
resiliency, and reducing threats while facilitating
migration to more favorable conditions in the
highly fragmented agricultural landscapes
(Schoeneberger et al., 2012). The option for
land use practices should be according to the
condition of the area so that increase the
adaptive capacity of subsistence farmers’ and
hence less vulnerability to climate change
impacts are necessary (Ford et al., 2011). Thus
and agro-ecosystem can be designed to
support adaptation of communities and
households to local and global change (Van
Ardenne et al., 2003). However, traditional
resource management adaptations, such as
agroforestry systems, may potentially provide
options for improving farmer adapting to climate
change through simultaneous production of
food, fodder and firewood as well as mitigation
of the impact of climate change (Adgeret.al,
2010). Tree-based systems are more profitable
and less risky than other agricultural options
because of the variety of products and have
less infected by pest (Kebebew et al., 2011).
The twin objective of climate change adaptation
and mitigation can be addressed by
agroforestry (Murthy et. al., 2013) which has
unique opportunity to accomplish those
prospects. These agroforestry practices are
based on a variety of management approaches
and have potential positive implications for
climate change mitigation (Albrecht et al.,
2003). Agroforestry systems can meaningfully
reduce the pressure on natural forests for
essential energy. Expansion and use of
agroforestry for sustainable fuel wood can
contribute to energy substitution and becomes
an important carbon offset option (Unruh et.al.,
1993).It is reported that Agroforestry systems
that combine trees and shrubs with crops and
livestock enhances organic carbon
accumulation in soils by providing continuous
supply of organic matter, and it also increases
soil microorganisms by which the nutrient cycle
is preserved (Araujo et al., 2011). Reducing the
presence of GHGs specially CO2 in atmosphere
for the decreasing the process of global
warming include the way of removing carbon
from atmosphere and depositing it in reservoir
or transforming Carbon to secure in other long-
lived pools (UNFCCC, 2007). The best
reservoir for the sequestration of carbon is tree
and soil in Tree-based farmland tree play
significant role to carbon sequestration both in
above and below ground as well as reduces
emission of greenhouse gases from agricultural
practices (Branca et al., 2013).
Climate change mitigation through
enhancing carbon sequestration and
strengthening the system’s ability to cope with
adverse impacts of changing climatic condition
can be done by the different practice of
agroforestry system. In a meantime,
agroforestry set best example for the copping of
adverse impact of changing climatic condition
(Verocht et al., 2007). In addition, improved
farming practices, including the use of organic
fertilizers, conservation farming practices, etc.,
can increase crop yields, reduce GHGs
emissions, and enhance soil organic carbon
(SOC) storage (Branca et al., 2013).
Agroforestry is a viable alternative to prevent
and mitigate climate change. IPCC recognized
agroforestry as having high potential for
sequestering carbon under the climate change
mitigations strategies (Watson et al., 2000).
Because trees are the largest component of
aboveground biomass in terrestrial ecosystems,
a number of studies have paid attention to the
role of forests in mitigating climate change,
carbon sequestration and biodiversity
conservation (IPCC, 2007). In addition that,
agroforestry has been proposed as a strategy
not only for adapting to climate change, but also
for mitigating and addressing issues of food
security and environmental degradation in
agricultural systems. Agroforestry is gaining
popularity as an adaptation strategy, in part
because traditional agricultural systems often
include agroforestry practices (Liang et al.,
2009). In such a way, the implementation of
agroforestry is less costly and more effective
than other approaches (ICIMOD, 2013). The
adoption of the practice of agroforestry
increases crop production, income, savings,
improves food security, and provides firewood
Paudel et al., 2017; Agroforestry System: An Opportunity for Carbon Sequestration and Climate Change
Adaptation in the Mid-Hills of Nepal
Oct. Jour. Env. Res. Vol 5(1):022-031
028
and fodder (Akinnifesi et al., 2008). Tree-based
agroforestry practices could bring opportunities
for rural development through promoting agro-
industries and improving local economies by
reducing unemployment (Kumar et al., 2012). In
Nepal, Climate-related changes have been
observed in precipitation patterns, temperature,
high intensity floods, landslides, erosion and
increased sedimentation (IPCC, 2007). These
changes in climatic factors have substantial
impacts at the local level as they change the
agro-ecosystem, resulting in loss of land,
livestock and household assets (Pant, 2011).
As far as possible, raising trees on the farm
is a traditional practice in Nepal, particularly in
the mid-hills with a purpose of producing fodder
for livestock and fuel-wood for heating and
cooking (Amatya and Newman, 1993). Various
forms of agroforestry were adopted by farmers
over time such as homestead agroforestry,
alley cropping, buffer strips, fruit garden,
woodlot, and boundary plantation, improved
agroforestry like coffee plantation in midhills
and terai (Dhakal et al., 2012). That’s why; the
practice of agroforestry is a contributing factor
in reducing human impact on the natural forest
and maintaining agro-biodiversity as well as
reducing greenhouse gas emission (Acharya,
2006). Agroforestry practices have been
approved as a strategy for soil C sequestration
under afforestation and reforestation programs
and also under the Clean Development
Mechanisms of the Kyoto Protocol (IPCC,
2007). Agroforestry has received widespread
attention in tropical and temperate regions of
the world for providing ecosystem services such
as carbon sequestration, biodiversity
conservation, soil quality, and preserving air
and water quality (Thevathasan and Gordon
2004; Jose, 2009).
CONCLUSION
This paper reviewed agroforestry is an
important strategy to sequester C from both
developed and developing nations. Forest and
farm based agroforestry both have equally
important roles in reducing carbon emissions
and providing food security to the people of
rural areas. Agroforestry and sustainable
agricultural methods help to mitigate climate
change by sequestering and storing carbon in
the trees and in the soil. There is need of
management strategy of agroforestry in
developing countries for the climate change
adaptation. Traditional agroforestry mostly seen
in the midhills of Nepal should be changed
towards thecommercialization so that produce
green employment and conserve tree as source
of sink.
REFERENCES
Acharya K.P. (2006).Linking Trees on Farms with
Biodiversity Conservation in Subsistence
Farming Systems in Nepal.Biodiversity and
Conservation, 15(2):631–646.
Adger N, Moran D., Wreford (2010). Climate change
and Agriculture: impacts, adaptation and
mitigation,” Organization for Economic Co-
A. operation and Development (OECD), p.
140
AkinnifesiFK.,Chirwa, PW., Ajayi OC., Sileshi G.,
Matakala P., Kwesiga FR.(2008).
Contributions of Agroforestry Research to
Livelihood of Smallholder Farmers in
Southern Africa: Taking Stock of the
Adaptation, Adoption and Impact of
Fertilizer Tree Options. Agricultural Journal
3(1): 58-75.
Alao JS. Shuaibu, RB. (2011). Agroforestry
Practices and Preferential Agroforestry
Trees among Farmers in Lafia Local
Government Area, Nasarawa State,
Nigeria
Albrecht A, Kandji ST (2003). Carbon sequestration
in tropical agroforestry systems.
Agriculture, Ecosystems and Environment
99: 15-27
Amatya SM., Newman S. (1993). Agroforestry in
Nepal: Research and Practices.
Agroforestry Systems21(3):215–222.
Araujo ASF., Leite LFC., Iwata BDF., Lira MDA.,
Xavier GR., Figueiredo MDVB.
(2011).Microbiological Process in
Agroforestry Systems. Agronomy for
Sustainable Development, 32:215–226
Branca, G., Lipper, L., McCarthy, N., Jolejole, M. C.
(2013).Food security, climate change, and
sustainable land management- A review.
Agronomy for Sustainable Development,
pp 635-660
Burton I. (2000). Adaptation to Climate Change and
Variability in the Context of Sustainable
Development. New Haven and New York:
Climate Change and Development, Yale
Paudel et al., 2017; Agroforestry System: An Opportunity for Carbon Sequestration and Climate Change
Adaptation in the Mid-Hills of Nepal
Oct. Jour. Env. Res. Vol 5(1):022-031
029
School of Forestry and Environmental
Studies and UNDP.
Cairns M.A. and Meganck R.A. (1994). Carbon
sequestration, biological diversity, and
sustainable development: integrated forest
management. Environ Manag 18:13–22.
CBS (2008). Census report of Nepal, Center Bureau
of Statistics, Nepal. Available online at
https://www.cbs.gov.np/
Dahal, K. N. and Kafle, G. (2013).Organic Carbon in
Soil and Biomass of an AlnusNepalensis
Forest in Kathmandu, Nepal.International
Journal of Agriculture and Forestry, 3(6):
240-243.
DFRS, (2015).State of Nepal's Forests. Forest
Resource Assessment (FRA) Nepal,
Department of Forest Research and
Survey (DFRS). Kathmandu, Nepal.
Available online at https://
www.dfrs.gov.np
Dhakal A, Cockfield G, Maraseni T.N (2012).
Evolution of agroforestry based farming
systems: a case of Dhanusha District
Nepal. Agrofor Syst 86(1):17–33
Ford JD, Berrang-Ford L, Paterson J (2011).A
systematic review of observed climate
change adaptation in developed nations.A
letter. Climatic Change 106:327–336
Garforth, C. J., Y.B. Malla, B. H. Pandit, and R. P.
Neopane (1997). Socioeconomic Factors
and Agro-forestry Improvements in the
Hills of Nepal. Mountain Research and
Development, 19(3): 273-278.
Gilmour D, Pradhan U, Malla Y, Bartlett T, Finlayson
R, Shah R. (2014). Enhancing Livelihoods
and Food Security from Agroforestry and
Community Forestry Systems in Nepal:
Current Status, Trends, and Future
Directions. Johari R, eds. Bogor,
Indonesia: World Agroforestry Centre
(ICRAF) Southeast Asia Regional
Program; Kathmandu: International Union
for Conservation of Nature - Nepal;
Canberra: Australian Centre for
International Agricultural Research
(ACIAR).hdfhd
Gilmour, D. A. and R. J. Fisher (1991).Villagers,
Forests, and Foresters: The Philosophy,
Process and Practice of Community
Forestry in Nepal. Kathmandu. pp 1-9.
Hassan R. and Nehmachen C. (2008).
Determinants of African farmers’ strategies
for adapting to climate change: Multinomial
choice analysis , Center for Environmental
Economics
HMG/N (2002).Nepal Biodiversity Strategy.Ministry
of Forests and Soil Conservation,
Kathmandu, Nepal. pp 5-7
ICIMOD (2013). Policy and Institutions in Adaptation
to Climate Change Case study on tree crop
diversity in China, Nepal, and Pakistan.
Available online at http://lib.icimod.org/
ICRAF (2006).The Future of Agroforestry. World
Agroforestry Centre, Nairobi Kenya.
Available online at
www.worldagroforestry.org/downloads/Pub
lication
IPCC (2007). Climate Change 2007 Synthesis
Report: Summary for Policymakers.
Available online at http://pure.iiasa.ac.at
Jose S. (2009). Agroforestry for ecosystem services
and environmental benefits: an overview.
Agrofor Syst 76:1–10
Kebebew Z., Urgessa K. (2011). Agro forestry
Perspective in Land use Pattern and
Farmers Copying Strategy: Experience
from Southwest Ethiopia, World journal of
Agricultural Science., 73-77
Kumar, B Mohan, Singh, A.K., Dhyani, S.K. (2012).
Agroforestry - The Future of Global Land
Use.Advances in Agroforestry, pp 359-389
Leakey R. (1996).Definition of agroforestry ICRAF,
Nairobi (Kenya)) International Centre for
Research in Agroforestry (ICRAF), Nairobi
(Kenya). Available online at
http://agris.fao.org/
Liang L., Shen L., Yang W., Yang X. Zhang Y.
(2009). Building on traditional shifting
cultivation for rotational agroforestry:
Experiences from Yunnan, China.’ Forest
Ecology and Management 257(10):1989–
1994
LRMP (1979) Land Utilization Report. Land
Resource Mapping Project, Kenting Earth
Science Canada andDepartment of
Topography, Government of Nepal,
Kathmandu, Nepal. pp 110
Mahat, T.B.S. (1987). Forestry-Farming Linkages in
the Mountains.Occasional Paper No. 7,
ICIMOD, Kathmandu, Nepal. pp 48
Matocha J. Schroth G. Hills T. D. Hole (2012).
Integrating Climate Change Adaptation and
Mitigation through Agroforestry and
ecosystem conservation,Agroforestry - The
Future of Global 105 Land Use, Advances
in Agroforestry. Available online at
www.indiaenvironmentportal.org.in
Montagnini, F., and Nair, P.K.R. (2004). Carbon
Sequestration: An underexploited
Environmental benefit of Agroforestry
Paudel et al., 2017; Agroforestry System: An Opportunity for Carbon Sequestration and Climate Change
Adaptation in the Mid-Hills of Nepal
Oct. Jour. Env. Res. Vol 5(1):022-031
030
systems. Agroforests. Syst. 61–62:281–
295.
Murthy I.K, Gupta M, Tomar S, Munsi M, Tiwari R,
Hegde GT, and NH Ravindranath (2013).
Carbon Sequestration Potential of
Agroforestry Systems in India. J Earth Sci
Climate Change 4(1):1-7
Nair PKR and Garrity D (2012). Agroforestry
Research and Development: the way
forward. In: Nair PKR, Garrity D (eds)
Agroforestry—the future of global land use.
Springer, Dordrecht, pp 515–531
Nair PKR, Nair VD, Kumar BM, Showalter JM.
(2010). Carbon Sequestration in
Agroforestry Systems. Adv. Agron
108:237–307.
Nair P.K.R., and Nair V.D. (2003). Carbon storage
in North American agroforestry systems.
In:The Potential of U.S. Forest Soils to
Sequester Carbon and Mitigate the
Greenhouse Effect (J. Kimble, L. S. Heath,
R. A. Birdsey, and R. Lal, Eds.)CRC Press,
Boca Raton, USA.pp. 333–346.
Nair, P.K.R. (1993). An Introduction to Agroforestry.
Dordrecht, Netherlands, Kluwer Academic
Publishers.
Nepal Planning Commission (NPC) (2014).Nepal
Status Paper.Kathmandu: Nepal Planning
Commission Available online at
http://www.npc.gov.np/
Neupane RP, Sharma KR, Thapa GB (2002).
Adoption of Agroforestry in the Hills of
Nepal: a Logistic Regression Analysis.
Agric Syst 72(1):177–196
NFI (1994). National Forest Inventory, Report.
Ministry of forest and soil Conservation,
Kathmandu, Nepal. Available online at
https://www.dfrs.gov.np
NRB (2014). Working paper, Nepal Rastra Bank
available online at https://www.nrb.org.np.
Pandit B.H., Shrestha K.K. and Bhattarai S. (2014).
Sustainable Local Livelihoods through
Enhancing Agroforestry Systems in Nepal,
Journal of forest and Livelihood 47-63
Pant, KP (2011). Economics of climate change for
smallholder farmers in Nepal: A Review.
The Journal of Agriculture and
Environment 12:113-126
Parry M.L., O.F. Canziani, J.P. Palutikof, P.J. van
der Linden and C.E. Hanson, Eds., (2007).
Climate Change 2007: Impacts, Adaptation
and Vulnerability. Contribution of Working
Group II to the Fourth Assessment Report
of the Intergovernmental Panel on Climate
Change, Cambridge University Press,
Cambridge, UK, pp 982
Paudel B., Zhyang YL, Shi-Cheng LI, Lin-Shan
L.,Xue W., and Khanal N.R. (2016).
Review of Studies on Landuse and Land
cover change in Nepal, Journal of
Mountain Sciences, 13(4):663-660
Regmi, B. N., (2003). Contribution of Agroforestry
for Rural Livelihoods: A Case of Dhading
District, Nepal. Paper presented at The
International Conference on Rural
Livelihoods, Forests and Biodiversity 19-23
May 2003, Bonn, Germany.
Smith J, Pearce BD, Wolfe MS (2012). A European
Perspective for Developing Modern
Multifunctional Agroforestry Systems for
Sustainable Intensification.Agric Food
system in southern USA. Agroforest Syst
58:45–54
Sthapit S. Suwal R. and Pudasaini R. (2010).In Nepal,
A Home Garden Is Greater Than the Sum of
Its Parts, Online at nourishing the planet.
http://blogs.worldwatch.org/nourishingtheplan
et/in-nepal
Takimoto, A., V.D. Nair, and P.K.R. Nair (2009).
Contribution of Trees to Soil carbon
Sequestration Under agroforestry systems
in the Western Sahel.Agrofor. Syst. 76:11–
25.
Tejwani, K. G. and C.K. Lai (1992). Asia-pacific
Agroforestry Profiles, Agroforestry in the
Hills of Nepal: A Logistic Regression
Analysis. Agricultural System, 72:34-40
Tewari, S.K. (2008). Farm Foresty. Agroforestry
Project, G..B.Pant University of Agricultute
and Technology.pp 9-18
Thapa, B. (1994). Farmer’s Ecological Knowledge
about the Management and Use of
Farmland Tree Fodder Resources in the
Midhills of Eastern Nepal. Ph.D. Thesis,
University of Wales, UK
Thevathasan NV, Gordon AM. (2004). Ecology of
Tree Intercropping Systems in the North
Temperate Region: Experience from
Southern Ontario, Canada. Agrofor Syst
61:257
Uddin K, Shrestha HL, Murthy MSR, Bajracharya B.,
Shrestha B., Gilani H., Pradhan S., Dangol
B. (2015). Development of 2010 National
Land Cover Database for the Nepal.
Journal of Environmental Management
148:82-90
Unruh JD, Houghton RA, Lefebvre PA (1993).
Carbon Storage in Agroforestry: an
Paudel et al., 2017; Agroforestry System: An Opportunity for Carbon Sequestration and Climate Change
Adaptation in the Mid-Hills of Nepal
Oct. Jour. Env. Res. Vol 5(1):022-031
031
Estimate for sub-Saharan Africa. Climate
Res 3:39-52.
Van Ardenne-van der Hoeven A, Benn H, Malloch
Brown M, Chino T, Johnston DJ, Kabbaj O,
Nielson P, Töpfer K, Wieczorek-Zeul H,
Zhang S. (2003). Poverty and climate
change: Reducing the Vulnerability of the
Poor through Adaptation. Paris:
Organisation for Economic Co-operation
and Development; available on
http://www.oecd.org/environment/cc
Verchot, L. V., Van Noordwijk, M., Kandji, S.,
Tomich, T., Ong, C., Albrecht, A.,
Mackensen, J., Bantilan, C., Anupama, K.
V., and Palm, C. (2007). Climate Change,
Linking Adaptation and Mitigation through
Agroforestry. Mitig. Adapt.
Strateg.Glob.Change 12:901–918.
Watson R.T., Noble I.R., Bolin B., Ravindranath
N.H., Verardo D.J., Dokken D.J. (eds)
(2000). Land Use, Land-Use Change, and
Forestry. Intergovernmental Panel on
Climate Change (IPCC), Special
report.Cambridge Univ. Press. New York.
Sources of Financial Support: None.
Conflict of interest: None. Declared.