Sustainable
agriculture:
Meeting food
security needs, addressing climate change challenges
Agriculture is at a crossroads.
It has to find ways to feed the world while being environmentally, socially and
economically sustainable. Stressing that current agricultural practices are a
threat to the future of agriculture itself, Lim Li Ching highlights, in the
following article, some of the critical issues that need to be resolved to meet
the many challenges facing it, including climate change.
THE challenges facing
agriculture today are immense. Of immediate concern is the global increase in
food prices, starkly brought home by reports of food riots and food shortages
in many countries around the world. During the first three months of 2008,
international nominal prices of all major food commodities reached their
highest levels in nearly 50 years while prices in real terms were the highest
in nearly 30 years (FAO, 2008).
While the United Nations Food
and Agriculture Organisation (FAO)'s food price index1 rose, on average, 8% in
2006 compared with the previous year, it increased by 24% in 2007 compared to
2006. The increase in the average of the index for the first three months of
2008 compared to the same three months in 2007 was 53%. The continuing surge in
prices is led by vegetable oils, which on average increased by more than 97%
during the same period, followed by grains with 87%, dairy products with 58%
and rice with 46%. The FAO estimates
that the number of hungry people increased by about 50 million in 2007 as a
result of soaring food prices.
In addition, the challenges of
climate change are increasingly urgent. The Intergovernmental Panel on Climate
Change makes it clear that warming of the climate system is 'unequivocal', as
observations of increases in air and ocean temperatures, widespread melting of
snow and ice, and sea-level rise have made evident (IPCC, 2007). Agriculture
will therefore have to cope with increased climate variability and more extreme
weather events.
Climate change, coincident with
increasing demand for food, feed, fibre and fuel, has the potential to
irreversibly damage the natural resource base on which agriculture depends,
with significant consequences for food insecurity (IAASTD, 2008). The
relationship between climate change and agriculture is two-way; agriculture
contributes to climate change in several major ways and climate change in
general adversely affects agriculture.
Agriculture is thus at a
crossroads. It has to find ways to feed the world while being environmentally, socially
and economically sustainable. Yet, it is increasingly clear that the path that
agriculture has been on is not sustainable, nor can it feed the world without
destroying the planet (IAASTD, 2008). With the spotlight once more on
agriculture, and with many critical issues that need resolving, finding the
answer to the question of the nature of agricultural development required has
never been more pressing.
'Business-as-usual
is no longer an option'
The International Assessment of
Agricultural Knowledge, Science and Technology for Development (IAASTD) sought
to examine this question. This is the most rigorous and comprehensive
assessment of agriculture to date. Co-sponsored by the World Bank, FAO, UN
Environment Programme (UNEP), UN Development Programme (UNDP), World Health
Organisation (WHO), UN Educational, Scientific and Cultural Organisation
(UNESCO) and Global Environment Facility (GEF), its report clearly concluded
that a radical change is needed in agricultural policy and practice, in order to
address hunger and poverty, social inequities and environmental sustainability
(IAASTD, 2008).
The report's central message is
that the business-as-usual scenario of industrial farming, input and energy
intensiveness, collateral damage to the environment and marginalisation of
small-scale farmers is no longer tenable. While past emphasis on production and
yields had brought benefits, such as afforded under the Green Revolution, this
was at tremendous cost to the environment and social equity.
The Green Revolution drove
widespread shifts in the agricultural sector from subsistence and
low-external-input agriculture to monocropping with high-yielding varieties
(HYVs). This agricultural paradigm required the adoption of a 'package' of
inputs, including irrigation, chemical pesticides and fertilisers, and hybrid
seeds bred for disease resistance and high yield. Participating farmers often
had access to credit and agro-processing facilities, transport and roads,
machinery, marketing infrastructure and government price supports.
By the 1970s, Green
Revolution-style farming had replaced the traditional farming practices of
millions of developing-country farmers. By the 1990s, almost 75% of Asian rice
areas were sown with these new varieties. Overall, it is estimated that 40% of
all farmers in developing countries were using Green Revolution seeds by this
time, with the greatest use found in Asia, followed by Latin America (Rosset et
al., 2000; Shiva, 1991).
The rapid spread of Green
Revolution agriculture throughout most countries of the South was accompanied
by a rapid rise in pesticide use (Rosset et al., 2000). This was because the
HYVs were more susceptible to pest outbreaks. Promising increases of yield were
thus offset by rising costs associated with increased use of chemical inputs.
In the Central Plains of Thailand, yields went up only 6.5%, while fertiliser
use rose 24% and pesticides jumped by 53%. In West Java, profits associated
with a 23% yield increase were virtually cancelled by 65% and 69% increases in
fertilisers and pesticides respectively (Rosset et al., 2000).
Synthetic fertilisers,
pesticides and herbicides are made from non-renewable raw materials such as
mineral oil and natural gas or from minerals that are depleting such as
phosphate and potassium. As the price of petroleum increases, so does the cost
of external inputs and machinery, forcing small farmers who are dependent on
these inputs into debt. The production of agrochemicals is also an important
source of greenhouse gas (GHG) emissions. In particular, fertiliser production
is energy-intensive, accounting for 0.6-1.2% of the world's total GHGs
(Bellarby et al., 2008). Industrial, chemical-intensive agriculture has also
degraded soils and destroyed resources that are critical to storing carbon,
such as forests and other vegetation.
The rise in use of chemical
inputs has also had adverse environmental and health impacts on farmworkers and
consumers. A substantial portion of pesticide residues ends up in the
environment, causing pollution and biodiversity decline (Znaor et al., 2005).
The extensive use of pesticides has also resulted in pesticide resistance in
pests and adverse effects on beneficial natural predators and parasites
(Pimentel, 2005).
The Green Revolution also
brought about a shift from diversity to monocultures. When farmers opted to
plant Green Revolution crop varieties and raise new breeds of livestock, many
traditional, local varieties were abandoned and became extinct. And yet,
maintaining agricultural biodiversity is vital to long-term food security as it
is vital insurance against crop and livestock disease outbreaks and improves
the long-term resilience of rural livelihoods to adverse trends or shocks
(Pimbert, 1999).
Other costs of the Green
Revolution, often underestimated, included the financial costs of building huge
dams for irrigation, the financial costs of the energy required in the
construction and operation of such projects, the health costs of a steadily
affected population due to chemical contamination of food, the costs involved
in soil losses from increasingly degraded soils, genetic erosion and the
draining of groundwater aquifers (Alvares, 1996). Green Revolution farming
systems also required substantial irrigation, putting further strain on the
world's limited water resources.
Traditionally, local farming
communities were close-knit as seed exchange and farming knowledge were shared
freely. The Green Revolution seeds however were hybrids, for which seed saving
is undesirable, as the seed from the first generation of hybrid plants does not
reliably produce true copies. Therefore, new seed must be purchased for each
planting and this meant that farmers were no longer preserving and storing
seeds for the next planting season. This trend not only incurs extra costs for
the farmers but has an impact on social cohesiveness too (Sangaralingam, 2006).
Productivity
declines: Rice as a case study
In recent years, the biggest
claims of success of the Green Revolution model, its productivity gains, have
not been easy to sustain and, in some cases, have become exhausted. This is
best illustrated by the yield trends from long-term trials conducted on
experiment stations, such as the long-term continuous cropping experiment
conducted by the International Rice Research Institute (IRRI). The objective is
to monitor maximum yields obtained over time, holding input levels and crop
management practices constant. The trends indicate that, even with the best
available cultivars and scientific management, rice yields, holding input levels
constant, decline over the long term (Pingali et al., 1997; FAO, 2001).
At the farm level, declining
yield trends are usually not observed since input levels are not held constant
over time. However, in areas where intensive rice monoculture has been
practised over the past two to three decades, stagnant yields and/or declining
trends in partial factor productivities, especially for fertilisers, and
declining trends in total factor productivities, have been observed. Moreover,
the rate of deceleration in yields is higher for countries with higher cropping
intensities (Pingali et al., 1997).
Farm-level evidence from the
rice bowls of Asia thus indicates that intensive rice monoculture systems lead,
over the long term, to declining productivities of inputs (Pingali et al.,
1997). Over time, farmers have been found to use increasing amounts of inputs
to sustain the yield gains made during the Green Revolution years.
Intensive rice monoculture on
the lowlands results in the following changes: (i) rice paddies flooded for
most of the year without an adequate drying period; (ii) increased reliance on
inorganic fertilisers; (iii) asymmetry of planting schedules; and (iv) greater
uniformity of cultivars. Over the long term, the above changes impose significant
ecological costs due to negative biophysical impacts (Pingali et al., 1997).
Adverse biophysical consequences that have reduced productivity have been: the
buildup of salinity and waterlogging: declining soil nutrient status; increased
incidence of soil toxicities; and pest buildup and reduced resilience of the
ecosystem to pest attacks. Pingali et al. (1997) conclude that the practice of
intensive rice monoculture itself thus contributes to the degradation of the
paddy resource base and hence declining productivities.
Sustainable
agriculture as an option
It is thus clear that
agriculture needs to undergo a radical overhaul to become more sustainable.
This is not just because it is important to take care of the environment, but
also because sustainability is absolutely necessary for the continuation of the
productivity of the agroecosystem. Threats to the environmental sustainability
of agriculture threaten agriculture itself.
The IAASTD report (2008) makes
this clear by saying that greater emphasis is needed on safeguarding natural
resources and agroecological practices, as well as on tapping the wide range of
traditional knowledge held by local communities and farmers, which can work in
partnership with formal science and technology. It stresses that sustainable
agriculture that is biodiversity-based, including agroecology and organic
farming, is resilient, productive, beneficial to poor farmers, and will allow
adaptation to climate change.
Sustainable agricultural
approaches can be in many forms, such as agroecology, organic agriculture,
ecological agriculture, biological agriculture, etc. Sustainable agriculture
should (Pretty and Hine, 2001):
Make best use of nature's goods and services
by integrating natural, regenerative processes e.g. nutrient cycling, nitrogen
fixation, soil regeneration and natural enemies of pests.
Minimise non-renewable inputs (pesticides and
fertilisers) that damage the environment or harm human health.
Rely on the knowledge and skills of farmers,
improving their self-reliance.
Promote and protect social capital - people's
capacities to work together to solve problems.
Depend on locally-adapted practices to
innovate in the face of uncertainty.
Be multifunctional and contribute to public
goods, such as clean water, wildlife, carbon sequestration in soils, flood
protection and landscape quality.
Sustainable agricultural
practices include:
Crop rotations that mitigate weed, disease,
and insect problems; increase available soil nitrogen and reduce the need for
synthetic fertilisers; and in conjunction with conservation tillage practices,
reduce soil erosion.
Integrated pest management (IPM), which
reduces the need for pesticides by crop rotations, scouting, timing of planting
and biological pest controls.
Management systems to improve plant health and
crops' abilities to resist pests and disease.
Soil-conserving tillage.
Water conservation and water-harvesting
practices.
Planting of leguminous crops and use of
organic fertiliser or compost to improve soil fertility.
Despite adequate global food
production, many still go hungry because increased food supply does not
automatically mean increased food security. What is important is who produces
the food, who has access to the technology and knowledge to produce it, and who
has the purchasing power to acquire it (Pretty and Hine, 2001). Sustainable
agricultural approaches thus allow farmers to improve local food production
with low-cost, readily available technologies and inputs, without causing
environmental damage.
Sustainable
agriculture is productive
One criticism of sustainable
agriculture, especially organic agriculture, is that it cannot meet the world's
food demands, primarily because of low yields and insufficient organic
fertiliser. However, there is ample evidence to refute this argument. In
general, organic yields can be broadly comparable to conventional yields in
developed countries. In developing countries, organic practices can greatly
increase productivity, particularly if the existing system is low-input.
A recent study has found that
organic methods could produce enough food on a global per capita basis to
sustain the current human population, and potentially an even larger
population, without putting more farmland into production (Badgley et al., 2007).
The researchers examined a global dataset of 293 examples, and found that on
average, in developed countries, organic systems produce 92% of the yield
produced by conventional agriculture. In developing countries, however, organic
systems produce 80% more than conventional farms. Moreover, contrary to fears
that there are insufficient quantities of organically acceptable fertilisers,
the data suggest that leguminous cover crops could fix enough nitrogen to
replace the amount of synthetic fertiliser currently in use.
In a review of 286 projects in
57 countries, farmers were found to have increased agricultural productivity by
an average of 79% by adopting 'resource-conserving' or sustainable agriculture
(Pretty et al., 2006). A variety of resource-conserving technologies and
practices were used, including integrated pest management, integrated nutrient
management, conservation tillage, agroforestry, water harvesting in dryland
areas, and livestock and aquaculture integration into farming systems. These practices
not only increased yields, but also reduced adverse effects on the environment
and contributed to important environmental goods and services (e.g., climate
change mitigation), as evidenced by increased water use efficiency and carbon
sequestration, and reduced pesticide use.
The work built on earlier
research, which assessed 208 sustainable agriculture projects. The earlier
research found that for 89 projects for which there was reliable yield data,
farmers had, by adopting sustainable agriculture practices, achieved
substantial increases in per-hectare food production - the yield increases were
50-100% for rain-fed crops, though considerably greater in a number of cases,
and 5-10% for irrigated crops (Pretty and Hine, 2001). Disaggregated data show:
Average food production per household rose by
1.7 tonnes per year (up by 73%) for 4.42 million small farmers growing cereals
and roots on 3.6 million hectares.
Increase in food production was 17 tonnes per
year (up 150%) for 146,000 farmers on 542,000 hectares cultivating roots
(potato, sweet potato, cassava).
Total production rose by 150 tonnes per
household (up by 46%) for the larger farms in Latin America (average size 90
hectares).
There are many other specific
examples of increased yields following the application of sustainable
agricultural practices, which are summarised here (Parrott and Marsden, 2002;
Pretty and Hine, 2001):
Soil and water conservation in the drylands of
Burkina Faso and Niger have transformed formerly degraded lands. The average
family has shifted from being in cereal deficit of 644 kg per year (equivalent
to 6.5 months of food shortage) to producing an annual surplus of 153 kg.
In Ethiopia, some 12,500 households have
adopted sustainable agriculture, resulting in a 60% increase in crop yields.
Participatory irrigation management in the
Philippines has increased rice yields by about 20%.
45,000 families in Honduras and Guatemala have
increased crop yields from 400-600 kg/ha to 2,000-2,500 kg/ha using green
manures, cover crops, contour grass strips, in-row tillage, rock bunds and
animal manures.
The states of Santa Caterina, Paran and
Rio Grande do Sul in southern Brazil have focused on soil and water
conservation using contour grass barriers, contour ploughing and green manures.
Maize yields have risen from 3 to 5 tonnes/ha and soybeans from 2.8 to 4.7
tonnes/ha.
The high mountain regions of Peru, Bolivia and
Ecuador are some of the most difficult areas in the world for growing crops.
Despite this, farmers have increased potato yields threefold, particularly by
using green manures to enrich the soil.
In Brazil, use of green manures and cover
crops increased maize yields by 20-250%.
In Tigray, Ethiopia, yields of crops from
composted plots were 3-5 times higher than those treated only with chemicals.
Yield increases of 175% were reported from
farms in Nepal adopting agroecological practices.
In Peru, restoration of traditional Incan
terracing led to increases of 150% for upland crops.
Projects in Senegal promoted stall-fed
livestock, composting systems, green manures, water-harvesting systems and rock
phosphate. Yields of millet and peanuts increased dramatically by 75-195% and
75-165% respectively.
In Honduras, soil conservation practices and organic
fertilisers have tripled or quadrupled yields.
Sustainable
agriculture can raise incomes
The productivity of sustainable
agriculture often translates to increased incomes for farmers, who at the same
time are also able to reduce or eliminate the costs of purchasing chemical
inputs. Sustainable agriculture also often adds new productive elements to the
system, and, by maintaining or improving on- and off-farm biodiversity, allows
farmers to market non-cultivated crops and animals.
Moreover, if organic produce is
sold, these carry a premium price on the market. For example, a comprehensive
review of the many comparison studies of grain and soybean production conducted
by six US Midwestern universities since 1978 found that the organic cropping
systems were always more profitable than the most common conventional systems
if organic price premiums were factored in (Welsh, 1999). When the higher
premiums were not factored in, the organic systems were still more productive
and profitable in half the studies. This was attributed to lower production
costs and the ability of organic systems to out-perform the conventional in
drier areas, or during drier periods.
Fifteen-year results from the
Rodale Institute in the US showed that after a transition period with lower
yields, the organic systems were competitive financially with the conventional
system (Petersen et al., 1999). While the costs of the transition are likely to
affect a farm's overall financial picture for some years, projected profits
ranged from slightly below to substantially above those of the conventional
system, even though economic analyses did not assume any organic price premium.
The higher profits for the organic farms came largely from higher yields (of
corn, in this case), which nearly doubled after the transition period. When
prices or yields were low, organic farms suffered less than the conventional
and had fewer income fluctuations, as they had a diversity of crops to sell.
Expenses on the organic farms were significantly lower than on the conventional
- the latter spent 95% more on fertilisers and pesticides. Overall production
costs on the organic farms were 26% lower.
In developing countries,
evidence from hundreds of grassroots development projects shows that increasing
agricultural productivity with agroecological practices not only increases food
supplies, but also increases incomes, thus reducing poverty, increasing food
access, reducing malnutrition and improving the livelihoods of the poor.
Agroecological systems lead to more stable levels of total production per unit
area than high-input systems; they give more economically favourable rates of
return, and provide a return to labour and other inputs for an acceptable
livelihood (Pretty, 1995).
Sustainable
agriculture mitigates climate change and has climate adaptation potential
Sustainable agriculture, by its
very definition, reduces harm to the environment, for example through the
reduction or elimination of polluting substances such as pesticides and
nitrogen fertilisers, water conservation practices, soil conservation
practices, restoration of soil fertility, maintenance of agricultural
biodiversity and biodiversity etc. An FAO review summarises many of these
environmental benefits in relation to organic agriculture (Scialabba and
Hattam, 2002).
Importantly, sustainable
agriculture practices can also mitigate climate change. Organic agriculture,
for example, uses less fossil fuel-based inputs and has a better carbon
footprint than standard agricultural practices. This is because conventional
agriculture production utilises more overall energy than organic systems due to
heavy reliance on energy-intensive fertilisers, chemicals, and concentrated
feed, which organic farmers forgo (Zeisemer, 2007). Organic agriculture
performs better than conventional agriculture on a per-hectare scale, with
respect to both direct energy consumption (fuel and oil) and indirect
consumption (synthetic fertilisers and pesticides), with high efficiency of
energy use (Scialabba and Hattam, 2002).
Agriculture has the potential to
change from being one of the largest GHG emitters to a net carbon sink, while
offering options for mitigation. The solutions call for a shift to sustainable
farming practices that build up carbon in the soil and use less fertiliser
(Bellarby et al., 2008). There are a variety of sustainable farming practices
that can reduce agriculture's contribution to climate change, which are easy to
implement. These include crop rotations and improved farming design, improved
cropland management (such as avoiding leaving land bare, using an appropriate
amount of fertiliser, no burning of crop residues in the field, reducing
tillage), nutrient and manure management, grazing-land and livestock
management, maintaining fertile soils and restoration of degraded land,
improved water and rice management, and set-asides, land-use change and
agroforestry (Bellarby et al., 2008; Niggli et al., 2008).
A report by the International
Trade Centre UNCTAD/WTO and FIBL (Research Institute of Organic Agriculture,
Switzerland) (2007) provides a detailed assessment of the benefits of organic
farming regarding climate change. The benefits are summarised as follows (Khor,
2008):
Organic agriculture has considerable potential
for reducing emissions.
In general it requires less fossil fuel per
hectare and kg of produce due to the avoidance of synthetic fertilisers.
Organic agriculture aims to improve soil fertility and nitrogen supply by using
leguminous crops, crop residues and cover crops.
The enhanced soil fertility leads to a
stabilisation of soil organic matter and in many cases to a sequestration of
carbon dioxide into the soils.
This in turn increases the soil's water
retention capacity, thus contributing to better adaptation of organic
agriculture under unpredictable climatic conditions with higher temperatures
and uncertain precipitation levels. Organic production methods emphasising soil
carbon retention are most likely to withstand climatic challenges particularly
in those countries most vulnerable to increased climate change. Soil erosion,
an important source of carbon dioxide losses, is effectively reduced by organic
agriculture.
Organic agriculture can contribute
substantially to agroforestry production systems.
Organic systems are highly adaptive to climate
change due to the application of traditional skills and farmers' knowledge,
soil fertility-building techniques and a high degree of diversity.
The study concludes that:
'Within agriculture, organic agriculture holds an especially favourable position,
since it realizes mitigation and sequestration of carbon dioxide in an
efficient way... Organic production has great mitigation and adaptation
potential, particularly with regard to topsoil organic matter fixation, soil
fertility and water-holding capacity, increasing yields in areas with medium to
low-input agriculture and in agro-forestry, and by enhancing farmers' adaptive
capacity. Paying farmers for carbon sequestration may be considered a
win-win-win situation as (a) carbon dioxide is removed from the atmosphere
(mitigation); (b) higher organic matter levels in soil enhance their resilience
(adaptation); and (c) improved soil organic matter levels lead to better crop
yield (production).'
Crucially, for farmers who have
to face increased climate variability and extreme weather events in the near
future, sustainable agriculture, by increasing resilience within the
agroecosystem, increases its ability to continue functioning when faced with
unexpected events such as climate change. For example, organic agriculture
builds adaptive capacity on farms as it promotes agroecological resilience,
biodiversity, healthy landscape management, and strong community knowledge
processes (Borron, 2006). Improved soil quality and efficient water use also
strengthen agroecosystems, while practices that enhance biodiversity allow
farms to mimic natural ecological processes, which enables them to better
respond to change. Sustainable farming practices that preserve soil fertility
and maintain, or even increase, organic matter in soils can reduce the negative
effects of drought while increasing crop productivity (Niggli et al., 2008).
Conclusions
There is a clear need for a
systematic redirection of investment, funding, research and policy focus
towards sustainable agriculture. This is the key recommendation of the IAASTD
(2008) report. However, most policy measures to support agriculture currently
act as powerful disincentives against sustainability. In the short term, this means that farmers
switching from modern high-input agriculture to resource-conserving
technologies can rarely do so without incurring some transition costs. In the long term, it means that sustainable
agriculture will not spread widely beyond the types of localised success.
Sustainable agriculture can
contribute significantly to increased food production, as well as make a
significant impact on rural people's welfare and livelihoods. However, without appropriate policy support
at a range of levels, these improvements will remain at best localised in
extent or, worse, will wither away. A thriving and sustainable agricultural
sector requires both integrated action by farmers and communities, and
integrated action by policy makers and planners. It is also vital for
farmer-to-farmer learning and sharing of experiences to be encouraged and
facilitated. Sustainable agriculture needs to be mainstreamed into agricultural
policy and practice to reach its full potential. u
Lim Li Ching is a researcher
with the Third World Network. The above is a revised version of the keynote
presentation at the National Conference on 'Sustainable Agriculture: Moving
from Grassroots Initiatives to Mainstream Policies', organised by the
Consumers' Association of Penang and held in Petaling Jaya, Malaysia on 24
July.
Endnotes
1 The FAO food price index is a trade-weighted
Laspeyres index of international quotations expressed in US dollar prices for
55 food commodities.
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Meeting food
security needs, addressing climate change challenges
Agriculture is at a crossroads.
It has to find ways to feed the world while being environmentally, socially and
economically sustainable. Stressing that current agricultural practices are a
threat to the future of agriculture itself, Lim Li Ching highlights, in the
following article, some of the critical issues that need to be resolved to meet
the many challenges facing it, including climate change.
THE challenges facing
agriculture today are immense. Of immediate concern is the global increase in
food prices, starkly brought home by reports of food riots and food shortages
in many countries around the world. During the first three months of 2008,
international nominal prices of all major food commodities reached their
highest levels in nearly 50 years while prices in real terms were the highest
in nearly 30 years (FAO, 2008).
While the United Nations Food
and Agriculture Organisation (FAO)'s food price index1 rose, on average, 8% in
2006 compared with the previous year, it increased by 24% in 2007 compared to
2006. The increase in the average of the index for the first three months of
2008 compared to the same three months in 2007 was 53%. The continuing surge in
prices is led by vegetable oils, which on average increased by more than 97%
during the same period, followed by grains with 87%, dairy products with 58%
and rice with 46%. The FAO estimates
that the number of hungry people increased by about 50 million in 2007 as a
result of soaring food prices.
In addition, the challenges of
climate change are increasingly urgent. The Intergovernmental Panel on Climate
Change makes it clear that warming of the climate system is 'unequivocal', as
observations of increases in air and ocean temperatures, widespread melting of
snow and ice, and sea-level rise have made evident (IPCC, 2007). Agriculture
will therefore have to cope with increased climate variability and more extreme
weather events.
Climate change, coincident with
increasing demand for food, feed, fibre and fuel, has the potential to
irreversibly damage the natural resource base on which agriculture depends,
with significant consequences for food insecurity (IAASTD, 2008). The
relationship between climate change and agriculture is two-way; agriculture
contributes to climate change in several major ways and climate change in
general adversely affects agriculture.
Agriculture is thus at a
crossroads. It has to find ways to feed the world while being environmentally, socially
and economically sustainable. Yet, it is increasingly clear that the path that
agriculture has been on is not sustainable, nor can it feed the world without
destroying the planet (IAASTD, 2008). With the spotlight once more on
agriculture, and with many critical issues that need resolving, finding the
answer to the question of the nature of agricultural development required has
never been more pressing.
'Business-as-usual
is no longer an option'
The International Assessment of
Agricultural Knowledge, Science and Technology for Development (IAASTD) sought
to examine this question. This is the most rigorous and comprehensive
assessment of agriculture to date. Co-sponsored by the World Bank, FAO, UN
Environment Programme (UNEP), UN Development Programme (UNDP), World Health
Organisation (WHO), UN Educational, Scientific and Cultural Organisation
(UNESCO) and Global Environment Facility (GEF), its report clearly concluded
that a radical change is needed in agricultural policy and practice, in order to
address hunger and poverty, social inequities and environmental sustainability
(IAASTD, 2008).
The report's central message is
that the business-as-usual scenario of industrial farming, input and energy
intensiveness, collateral damage to the environment and marginalisation of
small-scale farmers is no longer tenable. While past emphasis on production and
yields had brought benefits, such as afforded under the Green Revolution, this
was at tremendous cost to the environment and social equity.
The Green Revolution drove
widespread shifts in the agricultural sector from subsistence and
low-external-input agriculture to monocropping with high-yielding varieties
(HYVs). This agricultural paradigm required the adoption of a 'package' of
inputs, including irrigation, chemical pesticides and fertilisers, and hybrid
seeds bred for disease resistance and high yield. Participating farmers often
had access to credit and agro-processing facilities, transport and roads,
machinery, marketing infrastructure and government price supports.
By the 1970s, Green
Revolution-style farming had replaced the traditional farming practices of
millions of developing-country farmers. By the 1990s, almost 75% of Asian rice
areas were sown with these new varieties. Overall, it is estimated that 40% of
all farmers in developing countries were using Green Revolution seeds by this
time, with the greatest use found in Asia, followed by Latin America (Rosset et
al., 2000; Shiva, 1991).
The rapid spread of Green
Revolution agriculture throughout most countries of the South was accompanied
by a rapid rise in pesticide use (Rosset et al., 2000). This was because the
HYVs were more susceptible to pest outbreaks. Promising increases of yield were
thus offset by rising costs associated with increased use of chemical inputs.
In the Central Plains of Thailand, yields went up only 6.5%, while fertiliser
use rose 24% and pesticides jumped by 53%. In West Java, profits associated
with a 23% yield increase were virtually cancelled by 65% and 69% increases in
fertilisers and pesticides respectively (Rosset et al., 2000).
Synthetic fertilisers,
pesticides and herbicides are made from non-renewable raw materials such as
mineral oil and natural gas or from minerals that are depleting such as
phosphate and potassium. As the price of petroleum increases, so does the cost
of external inputs and machinery, forcing small farmers who are dependent on
these inputs into debt. The production of agrochemicals is also an important
source of greenhouse gas (GHG) emissions. In particular, fertiliser production
is energy-intensive, accounting for 0.6-1.2% of the world's total GHGs
(Bellarby et al., 2008). Industrial, chemical-intensive agriculture has also
degraded soils and destroyed resources that are critical to storing carbon,
such as forests and other vegetation.
The rise in use of chemical
inputs has also had adverse environmental and health impacts on farmworkers and
consumers. A substantial portion of pesticide residues ends up in the
environment, causing pollution and biodiversity decline (Znaor et al., 2005).
The extensive use of pesticides has also resulted in pesticide resistance in
pests and adverse effects on beneficial natural predators and parasites
(Pimentel, 2005).
The Green Revolution also
brought about a shift from diversity to monocultures. When farmers opted to
plant Green Revolution crop varieties and raise new breeds of livestock, many
traditional, local varieties were abandoned and became extinct. And yet,
maintaining agricultural biodiversity is vital to long-term food security as it
is vital insurance against crop and livestock disease outbreaks and improves
the long-term resilience of rural livelihoods to adverse trends or shocks
(Pimbert, 1999).
Other costs of the Green
Revolution, often underestimated, included the financial costs of building huge
dams for irrigation, the financial costs of the energy required in the
construction and operation of such projects, the health costs of a steadily
affected population due to chemical contamination of food, the costs involved
in soil losses from increasingly degraded soils, genetic erosion and the
draining of groundwater aquifers (Alvares, 1996). Green Revolution farming
systems also required substantial irrigation, putting further strain on the
world's limited water resources.
Traditionally, local farming
communities were close-knit as seed exchange and farming knowledge were shared
freely. The Green Revolution seeds however were hybrids, for which seed saving
is undesirable, as the seed from the first generation of hybrid plants does not
reliably produce true copies. Therefore, new seed must be purchased for each
planting and this meant that farmers were no longer preserving and storing
seeds for the next planting season. This trend not only incurs extra costs for
the farmers but has an impact on social cohesiveness too (Sangaralingam, 2006).
Productivity
declines: Rice as a case study
In recent years, the biggest
claims of success of the Green Revolution model, its productivity gains, have
not been easy to sustain and, in some cases, have become exhausted. This is
best illustrated by the yield trends from long-term trials conducted on
experiment stations, such as the long-term continuous cropping experiment
conducted by the International Rice Research Institute (IRRI). The objective is
to monitor maximum yields obtained over time, holding input levels and crop
management practices constant. The trends indicate that, even with the best
available cultivars and scientific management, rice yields, holding input levels
constant, decline over the long term (Pingali et al., 1997; FAO, 2001).
At the farm level, declining
yield trends are usually not observed since input levels are not held constant
over time. However, in areas where intensive rice monoculture has been
practised over the past two to three decades, stagnant yields and/or declining
trends in partial factor productivities, especially for fertilisers, and
declining trends in total factor productivities, have been observed. Moreover,
the rate of deceleration in yields is higher for countries with higher cropping
intensities (Pingali et al., 1997).
Farm-level evidence from the
rice bowls of Asia thus indicates that intensive rice monoculture systems lead,
over the long term, to declining productivities of inputs (Pingali et al.,
1997). Over time, farmers have been found to use increasing amounts of inputs
to sustain the yield gains made during the Green Revolution years.
Intensive rice monoculture on
the lowlands results in the following changes: (i) rice paddies flooded for
most of the year without an adequate drying period; (ii) increased reliance on
inorganic fertilisers; (iii) asymmetry of planting schedules; and (iv) greater
uniformity of cultivars. Over the long term, the above changes impose significant
ecological costs due to negative biophysical impacts (Pingali et al., 1997).
Adverse biophysical consequences that have reduced productivity have been: the
buildup of salinity and waterlogging: declining soil nutrient status; increased
incidence of soil toxicities; and pest buildup and reduced resilience of the
ecosystem to pest attacks. Pingali et al. (1997) conclude that the practice of
intensive rice monoculture itself thus contributes to the degradation of the
paddy resource base and hence declining productivities.
Sustainable
agriculture as an option
It is thus clear that
agriculture needs to undergo a radical overhaul to become more sustainable.
This is not just because it is important to take care of the environment, but
also because sustainability is absolutely necessary for the continuation of the
productivity of the agroecosystem. Threats to the environmental sustainability
of agriculture threaten agriculture itself.
The IAASTD report (2008) makes
this clear by saying that greater emphasis is needed on safeguarding natural
resources and agroecological practices, as well as on tapping the wide range of
traditional knowledge held by local communities and farmers, which can work in
partnership with formal science and technology. It stresses that sustainable
agriculture that is biodiversity-based, including agroecology and organic
farming, is resilient, productive, beneficial to poor farmers, and will allow
adaptation to climate change.
Sustainable agricultural
approaches can be in many forms, such as agroecology, organic agriculture,
ecological agriculture, biological agriculture, etc. Sustainable agriculture
should (Pretty and Hine, 2001):
Make best use of nature's goods and services
by integrating natural, regenerative processes e.g. nutrient cycling, nitrogen
fixation, soil regeneration and natural enemies of pests.
Minimise non-renewable inputs (pesticides and
fertilisers) that damage the environment or harm human health.
Rely on the knowledge and skills of farmers,
improving their self-reliance.
Promote and protect social capital - people's
capacities to work together to solve problems.
Depend on locally-adapted practices to
innovate in the face of uncertainty.
Be multifunctional and contribute to public
goods, such as clean water, wildlife, carbon sequestration in soils, flood
protection and landscape quality.
Sustainable agricultural
practices include:
Crop rotations that mitigate weed, disease,
and insect problems; increase available soil nitrogen and reduce the need for
synthetic fertilisers; and in conjunction with conservation tillage practices,
reduce soil erosion.
Integrated pest management (IPM), which
reduces the need for pesticides by crop rotations, scouting, timing of planting
and biological pest controls.
Management systems to improve plant health and
crops' abilities to resist pests and disease.
Soil-conserving tillage.
Water conservation and water-harvesting
practices.
Planting of leguminous crops and use of
organic fertiliser or compost to improve soil fertility.
Despite adequate global food
production, many still go hungry because increased food supply does not
automatically mean increased food security. What is important is who produces
the food, who has access to the technology and knowledge to produce it, and who
has the purchasing power to acquire it (Pretty and Hine, 2001). Sustainable
agricultural approaches thus allow farmers to improve local food production
with low-cost, readily available technologies and inputs, without causing
environmental damage.
Sustainable
agriculture is productive
One criticism of sustainable
agriculture, especially organic agriculture, is that it cannot meet the world's
food demands, primarily because of low yields and insufficient organic
fertiliser. However, there is ample evidence to refute this argument. In
general, organic yields can be broadly comparable to conventional yields in
developed countries. In developing countries, organic practices can greatly
increase productivity, particularly if the existing system is low-input.
A recent study has found that
organic methods could produce enough food on a global per capita basis to
sustain the current human population, and potentially an even larger
population, without putting more farmland into production (Badgley et al., 2007).
The researchers examined a global dataset of 293 examples, and found that on
average, in developed countries, organic systems produce 92% of the yield
produced by conventional agriculture. In developing countries, however, organic
systems produce 80% more than conventional farms. Moreover, contrary to fears
that there are insufficient quantities of organically acceptable fertilisers,
the data suggest that leguminous cover crops could fix enough nitrogen to
replace the amount of synthetic fertiliser currently in use.
In a review of 286 projects in
57 countries, farmers were found to have increased agricultural productivity by
an average of 79% by adopting 'resource-conserving' or sustainable agriculture
(Pretty et al., 2006). A variety of resource-conserving technologies and
practices were used, including integrated pest management, integrated nutrient
management, conservation tillage, agroforestry, water harvesting in dryland
areas, and livestock and aquaculture integration into farming systems. These practices
not only increased yields, but also reduced adverse effects on the environment
and contributed to important environmental goods and services (e.g., climate
change mitigation), as evidenced by increased water use efficiency and carbon
sequestration, and reduced pesticide use.
The work built on earlier
research, which assessed 208 sustainable agriculture projects. The earlier
research found that for 89 projects for which there was reliable yield data,
farmers had, by adopting sustainable agriculture practices, achieved
substantial increases in per-hectare food production - the yield increases were
50-100% for rain-fed crops, though considerably greater in a number of cases,
and 5-10% for irrigated crops (Pretty and Hine, 2001). Disaggregated data show:
Average food production per household rose by
1.7 tonnes per year (up by 73%) for 4.42 million small farmers growing cereals
and roots on 3.6 million hectares.
Increase in food production was 17 tonnes per
year (up 150%) for 146,000 farmers on 542,000 hectares cultivating roots
(potato, sweet potato, cassava).
Total production rose by 150 tonnes per
household (up by 46%) for the larger farms in Latin America (average size 90
hectares).
There are many other specific
examples of increased yields following the application of sustainable
agricultural practices, which are summarised here (Parrott and Marsden, 2002;
Pretty and Hine, 2001):
Soil and water conservation in the drylands of
Burkina Faso and Niger have transformed formerly degraded lands. The average
family has shifted from being in cereal deficit of 644 kg per year (equivalent
to 6.5 months of food shortage) to producing an annual surplus of 153 kg.
In Ethiopia, some 12,500 households have
adopted sustainable agriculture, resulting in a 60% increase in crop yields.
Participatory irrigation management in the
Philippines has increased rice yields by about 20%.
45,000 families in Honduras and Guatemala have
increased crop yields from 400-600 kg/ha to 2,000-2,500 kg/ha using green
manures, cover crops, contour grass strips, in-row tillage, rock bunds and
animal manures.
The states of Santa Caterina, Paran and
Rio Grande do Sul in southern Brazil have focused on soil and water
conservation using contour grass barriers, contour ploughing and green manures.
Maize yields have risen from 3 to 5 tonnes/ha and soybeans from 2.8 to 4.7
tonnes/ha.
The high mountain regions of Peru, Bolivia and
Ecuador are some of the most difficult areas in the world for growing crops.
Despite this, farmers have increased potato yields threefold, particularly by
using green manures to enrich the soil.
In Brazil, use of green manures and cover
crops increased maize yields by 20-250%.
In Tigray, Ethiopia, yields of crops from
composted plots were 3-5 times higher than those treated only with chemicals.
Yield increases of 175% were reported from
farms in Nepal adopting agroecological practices.
In Peru, restoration of traditional Incan
terracing led to increases of 150% for upland crops.
Projects in Senegal promoted stall-fed
livestock, composting systems, green manures, water-harvesting systems and rock
phosphate. Yields of millet and peanuts increased dramatically by 75-195% and
75-165% respectively.
In Honduras, soil conservation practices and organic
fertilisers have tripled or quadrupled yields.
Sustainable
agriculture can raise incomes
The productivity of sustainable
agriculture often translates to increased incomes for farmers, who at the same
time are also able to reduce or eliminate the costs of purchasing chemical
inputs. Sustainable agriculture also often adds new productive elements to the
system, and, by maintaining or improving on- and off-farm biodiversity, allows
farmers to market non-cultivated crops and animals.
Moreover, if organic produce is
sold, these carry a premium price on the market. For example, a comprehensive
review of the many comparison studies of grain and soybean production conducted
by six US Midwestern universities since 1978 found that the organic cropping
systems were always more profitable than the most common conventional systems
if organic price premiums were factored in (Welsh, 1999). When the higher
premiums were not factored in, the organic systems were still more productive
and profitable in half the studies. This was attributed to lower production
costs and the ability of organic systems to out-perform the conventional in
drier areas, or during drier periods.
Fifteen-year results from the
Rodale Institute in the US showed that after a transition period with lower
yields, the organic systems were competitive financially with the conventional
system (Petersen et al., 1999). While the costs of the transition are likely to
affect a farm's overall financial picture for some years, projected profits
ranged from slightly below to substantially above those of the conventional
system, even though economic analyses did not assume any organic price premium.
The higher profits for the organic farms came largely from higher yields (of
corn, in this case), which nearly doubled after the transition period. When
prices or yields were low, organic farms suffered less than the conventional
and had fewer income fluctuations, as they had a diversity of crops to sell.
Expenses on the organic farms were significantly lower than on the conventional
- the latter spent 95% more on fertilisers and pesticides. Overall production
costs on the organic farms were 26% lower.
In developing countries,
evidence from hundreds of grassroots development projects shows that increasing
agricultural productivity with agroecological practices not only increases food
supplies, but also increases incomes, thus reducing poverty, increasing food
access, reducing malnutrition and improving the livelihoods of the poor.
Agroecological systems lead to more stable levels of total production per unit
area than high-input systems; they give more economically favourable rates of
return, and provide a return to labour and other inputs for an acceptable
livelihood (Pretty, 1995).
Sustainable
agriculture mitigates climate change and has climate adaptation potential
Sustainable agriculture, by its
very definition, reduces harm to the environment, for example through the
reduction or elimination of polluting substances such as pesticides and
nitrogen fertilisers, water conservation practices, soil conservation
practices, restoration of soil fertility, maintenance of agricultural
biodiversity and biodiversity etc. An FAO review summarises many of these
environmental benefits in relation to organic agriculture (Scialabba and
Hattam, 2002).
Importantly, sustainable
agriculture practices can also mitigate climate change. Organic agriculture,
for example, uses less fossil fuel-based inputs and has a better carbon
footprint than standard agricultural practices. This is because conventional
agriculture production utilises more overall energy than organic systems due to
heavy reliance on energy-intensive fertilisers, chemicals, and concentrated
feed, which organic farmers forgo (Zeisemer, 2007). Organic agriculture
performs better than conventional agriculture on a per-hectare scale, with
respect to both direct energy consumption (fuel and oil) and indirect
consumption (synthetic fertilisers and pesticides), with high efficiency of
energy use (Scialabba and Hattam, 2002).
Agriculture has the potential to
change from being one of the largest GHG emitters to a net carbon sink, while
offering options for mitigation. The solutions call for a shift to sustainable
farming practices that build up carbon in the soil and use less fertiliser
(Bellarby et al., 2008). There are a variety of sustainable farming practices
that can reduce agriculture's contribution to climate change, which are easy to
implement. These include crop rotations and improved farming design, improved
cropland management (such as avoiding leaving land bare, using an appropriate
amount of fertiliser, no burning of crop residues in the field, reducing
tillage), nutrient and manure management, grazing-land and livestock
management, maintaining fertile soils and restoration of degraded land,
improved water and rice management, and set-asides, land-use change and
agroforestry (Bellarby et al., 2008; Niggli et al., 2008).
A report by the International
Trade Centre UNCTAD/WTO and FIBL (Research Institute of Organic Agriculture,
Switzerland) (2007) provides a detailed assessment of the benefits of organic
farming regarding climate change. The benefits are summarised as follows (Khor,
2008):
Organic agriculture has considerable potential
for reducing emissions.
In general it requires less fossil fuel per
hectare and kg of produce due to the avoidance of synthetic fertilisers.
Organic agriculture aims to improve soil fertility and nitrogen supply by using
leguminous crops, crop residues and cover crops.
The enhanced soil fertility leads to a
stabilisation of soil organic matter and in many cases to a sequestration of
carbon dioxide into the soils.
This in turn increases the soil's water
retention capacity, thus contributing to better adaptation of organic
agriculture under unpredictable climatic conditions with higher temperatures
and uncertain precipitation levels. Organic production methods emphasising soil
carbon retention are most likely to withstand climatic challenges particularly
in those countries most vulnerable to increased climate change. Soil erosion,
an important source of carbon dioxide losses, is effectively reduced by organic
agriculture.
Organic agriculture can contribute
substantially to agroforestry production systems.
Organic systems are highly adaptive to climate
change due to the application of traditional skills and farmers' knowledge,
soil fertility-building techniques and a high degree of diversity.
The study concludes that:
'Within agriculture, organic agriculture holds an especially favourable position,
since it realizes mitigation and sequestration of carbon dioxide in an
efficient way... Organic production has great mitigation and adaptation
potential, particularly with regard to topsoil organic matter fixation, soil
fertility and water-holding capacity, increasing yields in areas with medium to
low-input agriculture and in agro-forestry, and by enhancing farmers' adaptive
capacity. Paying farmers for carbon sequestration may be considered a
win-win-win situation as (a) carbon dioxide is removed from the atmosphere
(mitigation); (b) higher organic matter levels in soil enhance their resilience
(adaptation); and (c) improved soil organic matter levels lead to better crop
yield (production).'
Crucially, for farmers who have
to face increased climate variability and extreme weather events in the near
future, sustainable agriculture, by increasing resilience within the
agroecosystem, increases its ability to continue functioning when faced with
unexpected events such as climate change. For example, organic agriculture
builds adaptive capacity on farms as it promotes agroecological resilience,
biodiversity, healthy landscape management, and strong community knowledge
processes (Borron, 2006). Improved soil quality and efficient water use also
strengthen agroecosystems, while practices that enhance biodiversity allow
farms to mimic natural ecological processes, which enables them to better
respond to change. Sustainable farming practices that preserve soil fertility
and maintain, or even increase, organic matter in soils can reduce the negative
effects of drought while increasing crop productivity (Niggli et al., 2008).
Conclusions
There is a clear need for a
systematic redirection of investment, funding, research and policy focus
towards sustainable agriculture. This is the key recommendation of the IAASTD
(2008) report. However, most policy measures to support agriculture currently
act as powerful disincentives against sustainability. In the short term, this means that farmers
switching from modern high-input agriculture to resource-conserving
technologies can rarely do so without incurring some transition costs. In the long term, it means that sustainable
agriculture will not spread widely beyond the types of localised success.
Sustainable agriculture can
contribute significantly to increased food production, as well as make a
significant impact on rural people's welfare and livelihoods. However, without appropriate policy support
at a range of levels, these improvements will remain at best localised in
extent or, worse, will wither away. A thriving and sustainable agricultural
sector requires both integrated action by farmers and communities, and
integrated action by policy makers and planners. It is also vital for
farmer-to-farmer learning and sharing of experiences to be encouraged and
facilitated. Sustainable agriculture needs to be mainstreamed into agricultural
policy and practice to reach its full potential. u
Lim Li Ching is a researcher
with the Third World Network. The above is a revised version of the keynote
presentation at the National Conference on 'Sustainable Agriculture: Moving
from Grassroots Initiatives to Mainstream Policies', organised by the
Consumers' Association of Penang and held in Petaling Jaya, Malaysia on 24
July.
Endnotes
1 The FAO food price index is a trade-weighted
Laspeyres index of international quotations expressed in US dollar prices for
55 food commodities.
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