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8/22/2019 Thesis on Climate Change and Its Impact on Agricultural fields
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INTRODUCTION
Most agronomists believe that agricultural production will be affected by
the severity and pace of climate change. If change is gradual, there may be
enough time for adjustment. Rapid climate change, however, could harm
agriculture in many countries, especially those that are already suffering
from poor soil and climate conditions, because there is less time for
optimum natural selection and adoption.
People in India, especially the poorest, are vulnerable to the impact
of climate change, because the nations economy is so closely tied to
nature resources .For example, more than 57% of works are engaged in
agriculture and allied sectors, areas through earn their living in coastal
areas though tourism or fishing. Most of Indians poorest people live in
rural areas, almost totally reliant on natural resources for their food,
shelter and incomes. The yare already experiencing the impact of climate
change, with few resources to cope.
INDIA AND AGRICULTURE
CONTEXT
Population : 1 billion +
GDP from Agriculture : 34 % (1994), 42 % (1980)
Area under Agriculture : 50 % (160 mha)
Population dependent on Agriculture: 70%
Average farm size: : 1 to5 ha
Indian Agriculture- Some Facts
Total Geographical Area - 328 million hectares
Net Area sown - 142 million hectares
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Gross Cropped Area 190.8 million hectares
Major Crop Production (1999-2000)
Rice 89.5 million tonnes
Wheat 75.6 million tonnes
Coarse Cereals 30.5 million tonnes
Pulses 13.4 million tonnes
Oilseeds 20.9 million tonnes
Sugarcane 29.9 million tonnes
Indian Agriculture- Some Facts
Contributes to 24% of GDP
Provides food to 1Billion people
Sustains 65% of the population : helps alleviate poverty
Produces 51 major Crops
Provides Raw Material to Industries
Contributes to 1/6th of the export earnings
One of the 12 Bio-diversity centers in the world with over 46,000
species of plants and 86,000 species of animals recorded
During the last decade, the Indian state of Uttar Pradesh has been
witness to many climatic changes. Eastern Uttar Pradesh has faced severe
floods, while Bundelkhand region has faced one of the warmest famines
of the last decade. Thus, the impact of climate change has adversely
affected agricultural production resulting in huge loss of paddy and corn
crops in eastern districts and regional crops in Bundelkhand.
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Climate change impeding agricultural production in India during
the last decade, the Indian state of Uttar Pradesh has been witness to many
climatic changes. Eastern Uttar Pradesh has faced severe floods, while
Bundelkhand region has faced one of the worst famines of the last decade.
Thus, the impact of climate change has adversely affected agricultural
production resulting in huge loss of paddy and corn crops in eastern
districts and regional crops in Bundelkhand. Climate-related disasters
have brought widespread misery and huge economic losses to Uttar
Pradesh, adversely affecting public health, food security, agriculture,
water resources and biodiversity in the state. Floods are the most common
annual occurrence in the state, affecting one or the other part of the state;the most affected being the districts of the eastern U.P. and terai region.
Agriculture in India is very much weather-dependent. It is ironic, then,
that a significant percentage of greenhouse-gas emissions come from
agriculture. Fossil-fuel intensive agriculture is contributing to the creation
of the unpredictable weather conditions which all farmers will need to
battle in the not so distant future. Scientists believe that the fluctuating
weather conditions in the state suggest that the state is reeling under
climatic chaos. For more than a decade now, the state has been
experiencing contrasting extreme weather conditions and agriculture has
been worst affected by these climatic changes. A little decrease in
temperatures can reduce the production of wheat crops, but help in the
growth of paddy. Such changes may often tilt the farmers towards
growing one crop at the expense of the other. This would lead to
imbalances in crop production. According to the 2001 census, 62.12
percent of the states total workers are engaged in agriculture. UP
contributes, on an average, 21 percent to the national production of food
grain. With an average annual food grain production of about 42.7 million
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tons and per capita production of 234 kg, U.P. ranks third highest among
major states, and is considered to be a food grain surplus state. The
growing water scarcity poses further problems of survival to people and
animals alike. Already there have been reports of cattle deaths due to
water scarcity in the district. In recent years, the water level has gone
down significantly. The ill effects of climate change can also be seen on
women farmers, especially poor women farmers because of their low
social and economic status. They also have lesser accessibility to
livelihood resources and land holdings. There is a serious danger of
climatic changes. (In the form of severe droughts, floods, intense rainfall,
and storms) undermining development programmes and millenniumdevelopment goals aimed at reducing poverty. Currently India is spending
2.5% of its total GDP on measures to control the adverse impact of
climatic change, which is a big amount for any developing nations. The
zeal of rapid industrialization, deforestation and willful consumption of
natural resources is likely to make the situation worse. Policy makers at
the state, regional and national level should take a serious view of the
economic, agricultural, health-related and environmental impacts of
climate changes.
Land Use, Land Cover Change, & Agriculture
Land use and land cover are linked to climate and other
environmental changes in complex ways, such as the exchange of
greenhouse gases between plants and soils and the atmosphere, the effects
of changes in land use and land cover on Earth's heat balance, and the
impacts of changing environmental conditions on terrestrial ecosystems
and biodiversity. Past land-cover changes are important to understanding
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past climate variability and change, and projections of future land cover
change are needed as input to models of future climate changes. Changes
in land use and land cover affect ecosystems, biodiversity, agricultural
productivity, and other goods and services of value to society. The
National Research Council carries out a variety of studies, workshops, and
meetings and publishes numerous reports on science-policy issues related
to environmental change, land use, land cover change, and agriculture
.Land Use, Land Cover Change, & Agriculture activities at the National
Academies. Agriculture effects climate change & climate change
effects agriculture The greenhouse effect.
The earth is surrounded by an atmosphere through which solar
radiation is received. The atmosphere is not static but contains air, in
constant motion, being heated, cooled and moved, water being added and
removed along with smoke and dust. Only a tiny proportion of the sun's
energy reaches earth and some of this is reflected back into space (from
clouds etc.). When the radiant energy reaches the land surface, most of it
is absorbed, being used to heat the earth, evaporate water and to power
photosynthetic processes. The earth also radiates energy but, because it is
less hot than the sun, this is of a longer wavelength and is absorbed by the
atmosphere. The Earths atmosphere, thus acts like the glass of a green
house, hence the 'greenhouse effect'. The greenhouse gases (dealt with in
subject 3) are those that absorb the Earths radiation and thus contribute to
the greenhouse effect, but water is also a major absorber of energy. Where
there is an increase in the concentration of greenhouse gases (as with CO2
due to the burning of fossil fuels) this result in an enhanced greenhouse
effect - which is of concern as it could lead to climate change (i.e. global
warming).
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Global Warming
Global temperatures have risen by over 0.7oC in the last 100 years
and eleven of the last twelve years (1995-2006) are the warmest on
record. In the UK in 1990s were very warm about 0.6oC warmer than the
mean 1961 - 1990 temperature. Warm winters have reduced the number of
frosts, and the warmer summers have included record hot spells and high
sunshine totals.
How will climate change effect agriculture
Soil processes
The potential for soils to support agriculture and distribution of land use
will be influenced by changes in soil water balance:
Increase in soil water deficits i.e. dry soils become drier, therefore
increased need for irrigation but: Could improve soil workability in
wetter regions and diminish poaching and erosion risk Crops
The range of current crops will move northwardNew crop varieties may need to be selectedHorticultural crops are more susceptible to changing conditions than
arable cropsField vegetables will be particularly affected by temperature changesPhaselous bean, onion and sweetcorn are most likely to benefit
commercially from higher temperaturesWater deficits will directly affect fruit and vegetable production
The effect of increased temperature and CO2 levels on arable crops
will be broadly neutral:
How will climate change effect cropping in tropical and arid Countries?
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Grasslands and livestock
There is unlikely to be a significant change in suitability of livestock for
UK systemsPigs and poultry could be exposed to higher incidences of heat stress,
thus influencing productivityIncrease in disease transmission by faster growth rates of pathogens in
the environment and more efficient and abundant vectors (such as
insects)Consequences for food quality and storage
Weeds, pests and diseases:
Weeds evolve rapidly to overcome control measures, short lived weeds
and those that spread vegetatively (creeping buttercup, couch etc) evolve
at the greatest rate:
Grassland and arable weeds could become more tolerant to control
measures
Rate of evolution will increase in hotter, drier conditions and in 'extreme
years', could lead to some types of herbicide tolerance becoming more
commonPossible increase in the range of many native pests, and species that at
present are not economically important may become soSurveillance and eradication processes for other significant pests, such
as the Colarado beetle will become increasingly important
Predicted effects of climate change on agriculture over the next 50 years
Climatic
element
Expected changes
by 2050's
Confidence
in
Effects on agriculture
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prediction
CO2
Increase from 360
ppm to 450 - 600
ppm (2005 levels
now at 379 ppm)
Very high
Good for crops: increased
photosynthesis; reduced
water use
Sea level rise
Rise by 10 -15 cm
Increased in south
and offset in north
by natural
subsistence/rebound
Very high
Loss of land, coastal
erosion, flooding,
salinisation of groundwater
Temperature
Rise by 1-2oC.
Winters warming
more than summers.
Increased frequency
of heat waves
High
Faster, shorter, earlier
growing seasons, range
moving north and to higher
altitudes, heat stress risk,
increased
evapotranspiration
PrecipitationSeasonal changes by
10%Low
Impacts on drought risk'
soil workability, water
logging irrigation supply,
transpiration
Storminess
Increased wind
speeds, especially in
north. More intense
rainfall events.
Very low
Lodging, soil erosion,
reduced infiltration of
rainfall
Variability Increases across
most climatic
variables.
Predictions uncertain
Very low Changing risk of damaging
events (heat waves, frost,
droughts floods) which
effect crops and timing of
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farm operations
Source: Climate change and Agriculture, MAFF (2000)
Current projections, from the 4th Assessment report by the
Intergovernmental Panel on Climate Change (IPCC) published in 2007,
suggest that global temperatures will rise between 1.8oC and 4.0oC (best
estimate) by 2100 depending on emissions of greenhouse gases and that
global sea levels are likely to rise from anywhere between 180mm and
590mm. For further details go to the IPCC website.Pause for
thought......Should farmers take into account predicted climate changes
when 'planning for the long term future' of their businesses? he
Implications of Climate Change for Crop Yields, Global Food Supply and
Risk of Hunger The potential effects of climate change on crop yield, food
production and risk of hunger. There are two global studies of crop yield
responses and several additional estimates of production that are based on
the first of these. The studies cover three broad type of analysis:
1) Effects under climate change but with underlying socio-economic
characteristics largely unspecified,
2) Effects under both changes in climate and with varying development
pathways assumed to affect underlying socio-economics, and
3) Effects under different policies of stablisation of greenhouse gases.
There are some conclusions common to all studies: that climate change
will generally reduce production potential and increase risk of hunger, and
that Africa is the most adversely affected region. An additionally
important initial conclusion is that pathways of sustainable economic
development have a marked effect in reducing the adverse effects on
climate change.
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The early 1990s that have considered the effects of climate change
on crop yield potential, cereal production, food prices and the implications
for changes in the number of hungry people. The IPCC has recently
concluded that, while there is extensive potential to adapt to small
amounts of warming, and that the next few decades might even bring
benefits to higher latitudes through longer growing seasons, at lower
latitudes even small amounts of warming would tend to decrease yields
and, beyond about two degrees of warming would decrease yields in
almost all parts of the world 1. This regional unevenness of effect climate
change on agriculture around the world has very great implications for
food security, especially when (even without the challenge of climatechange) almost 800 million people in the developing world are estimated
to be to experiencing some form of shortage in food supply 2. Where
crops are grown near their maximum temperature tolerance and where
dryland, non-irrigated agriculture predominates, the challenge of climate
change could be overwhelming, especially on the livelihoods of
subsistence farmers and pastoral people, who are weakly coupled to
markets.
The paper is divided into four parts, reflecting the four main sets of
studies that have been published: 1) Studies in the early 1990s using
point-based crop growth models with what are now termed low
resolution models of climate, 2) later studies which used higher
resolution models, 3) Ricardian and other economic approaches that used
the yield estimates from the foregoing to develop estimates of production,
and 4) studies which have incorporated more spatially resolute analyses of
altered yield potential based on GIS systems rather than point-based
modelling.
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Effects on yields and production
The results show that climate change scenarios which exclude the
direct physiological effects of CO2 predict decreases in simulated yields
in many cases, while the direct effects of increasing atmospheric CO2
mitigate the negative effects primarily in mid and high latitudes. The
differences between countries in yield responses to climate change are
related to differences in current growing conditions. At low latitudes crops
are grown nearer the limits of temperature tolerance and global warming
may subject them to higher stress. In many mid and high latitude areas,
increasing temperatures may benefit crops otherwise limited by coldtemperatures and short growing seasons in the present climate.
Under the estimated effects of climate change and atmospheric CO2
on crop yields, world cereal production is estimated to decrease between 1
and 7% depending on the GCM climate scenario. The largest negative
changes occur in developing countries, averaging 9% to 4, 11%. By
contrast, in developed countries production is estimated to increase under
all but the UKMO scenario (+11% to 3%). Thus existing disparities in
crop production between the developed and developing countries are
estimated to grow. Decreases in production are estimated by the BLS to
lead to increase in prices (by 25 to 150%) and increases in hunger (by 10
to 60 %) The study tested the efficacy of two levels of adaptation: Level
1 adaptation included: shifts in planting date that do not imply major
changes in the crop calendar; additional application of irrigation water to
crops already under irrigation; changes in crop variety to currently
available varieties better adapted to the projected climate. Level 2
adaptation included: large shifts in planting date; increased fertiliser
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application; development of new varieties; installation of irrigation
systems.
Effect under different levels of adaptation
Level 1 adaptation largely offset the negative climate change
induced effects in developed countries, improving their comparative
advantage in world markets. In these regions cereal production increases
by 4% to 14% over the reference case. However, developing countries are
estimated to benefit little from adaptation (-9% to 12%). Averaged
global production is altered by between 0% and 5% from the reference
case. As a consequence, world cereal prices are estimated to increase by10-100% and the number of people at risk from hunger by c 5-50% . This
indicates that Level 1 adaptations would have relatively little influence on
reducing the global effects of climate change. More extensive adaptation
(Level 2) reduces impacts by a third and in some cases virtually eliminates
them. However, the decrease in the comparative advantage of developing
countries under these scenarios leads to decreased areas planted to cereals
in these areas. Cereal production in developing countries still decreases by
around 5%. Globally, however, cereal prices increase by only 5 to 35%,
and the number of people at risk from hunger is altered by between 2%
and +20% from the reference case (Figure 3). This suggests that Level 2
adaptations are required to mitigate 5 the negative effects of climate
change but that these still do not eliminate them in developing countries.
Net imports of cereals into developing countries will increase under all
scenarios. The change in cereal imports is largely determined by the size
of the assumed yield changes, the change in relative productivity in
developed and developing regions, the change in world market prices and
changes in incomes of developing countries. Under the GISS climate
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scenario productivity is depressed largely in favour of developed
countries, resulting in pronounced increases of net cereal imports into
developing countries. Under the UKMO scenario large cereal price
increases limit the increase of exports to developing countries.
Consequently, despite its beneficial impact for developed countries, the
Adaptation Level 1 scenarios show only small improvements for
developing countries as compared to the corresponding impacts without
such adaptation.
Effects of climate change
Changes in cereal production, cereal prices, and people at risk of
hunger estimated for the HadCM2 climate change scenarios (with the
direct CO2 effects taken into account) show that world is generally able to
feed itself in the next millennium. Only a small detrimental effect is
observed on cereal production, manifested as a shortfall on the reference
production level of around 100mmt (-2.1%) by the 2080s (+/-10mmt
depending on which HadCM2 climate simulation is selected). In
comparison, HadCM3 produces a greater disparity between the reference
and climate change scenario - a reduction of more than 160mmt (about
-4%) by the 2080s . Reduced production leads to increases in prices.
Under the HadCM2 scenarios cereal prices increase by as much as 17%
(+/- 4.5%) by the 2080s (Figure 4). The greater negative impacts on yields
projected under HadCM3 are carried through the economic system with
prices estimated to increase by about 45% by the 2080s. In turn these
production and price changes are likely to affect the number of people
with insufficient resources to purchase adequate amounts of food.
Estimations based upon dynamic simulations by the BLS show that the
number of people at risk of hunger increases, resulting in an estimated
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additional 90 million people in this condition due to climate change
(above the reference case of ~250 million) by the 2080s (Figure 4). The
HadCM3 results are again more extreme, falling outside the HadCM2
range with an estimated 125+ million additional people at risk of hunger
by the 2080s. All BLS experiments allow the world food system to
respond to climate-induced supply shortfalls of cereals and higher
commodity prices through increases in production factors (cultivated land,
labour, and capital) and inputs such as fertiliser.
Initial analyses using low resolution climate models
The first model-based studies of effects on global food supply were
published in the early 1990s. The general conclusions of that work stillhold today: that climate change is likely to reduce global food potential
and that risk of hunger will increase in the most marginalised economies
3. In these studies there were two main tasks: Firstly, the estimation of
potential changes in crop yield using crop models and a decision support
system developed by the US Agency for International Developments
International Benchmark Sites Network for Agrotechnology Transfer
(IBSNAT) 4,5. The crops modelled were wheat, rice, maize and soybean,
accounting for more than 85% of the worlds traded grains and legumes.
Secondly, the estimation of food production, prices and the number of
people at risk of hunger by using estimated yield changes in a world food
trade model, The Basic Linked System (BLS) developed at the
International Institute for Applied Systems Analysis (IIASA) 6. The
scenarios for these early studies were created by changing the observed
data on current climate (1951-80) according to doubled CO2 simulations
of three general circulation models (GCMs). The 2 as to understand the
nature of these complex interactions, and how they affect people at risk of
hunger in the GCMs used were those from the Goddard Institute for Space
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Studies (GISS) 7,8, Geophysical Fluid Dynamics Laboratory (GFDL)9
and the United Kingdom Meteorological Office (UKMO) 10. The
IBSNAT crop models were used to estimate how climate change and
increasing levels of carbon dioxide may alter yields of work crops at 112
sites in 18 countries representing both major production areas and
vulnerable regions at low, mid and high latitudes 11. The IBSNAT models
employ simplified functions to predict the growth of crops as influenced
by the major factors that affect yields, e.g. genetics, climate (daily solar
radiation, maximum and minimum temperatures and precipitation), soils
and management practices. Models used were for wheat 12, 13, maize 14,
15, paddy and upland rice 16 and soybean 17. The analyses included theeffects of enhanced ambient C02 levels on crop growth both through
altered water-use efficiency and rates of photosynthesis 19,20
21,22,23,24,25, . but the crop models did not simulate effects of altered
climate on weeds and insect pests. Regional yield estimates were derived
from the modelled site information, assuming the current mix of rainfed
and irrigated production, the current crop varieties, nitrogen management
and soils. Although the number of sites was limited (112 in all) it was
argued that these related to regions that account for about 70% of the
worlds grain production 26, and thus could enable credible conclusions
concerning world production to be drawn. The altered yield data was input
to a dynamic model of the world food system (the Basic Linked System)
in order to assess the possible impacts on the future levels of food
production, food prices and the number of people at risk from hunger27. It
consists of 20 national and/or regional models that cover around 80% of
the world food trade system. The remaining 20% is covered by 14
regional models for the countries that have broadly similar attributes (e.g.
African oil exporting countries, Latin American high income exporting
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countries, Asian low income countries). The grouping is based on country
characteristics such as geographical location, income per capita and the
countrys position with regard to net food trade 3,27. The BLS does not
incorporate any climate relationships per se. Effects of changes in climate
were introduced to the model as changes in average national or regional
yield per commodity as estimated above. Ten commodities are 3 included
in the model: Wheat, rice, coarse grains (e.g. maize, millet, sorghum, and
barley), bovine and ovine meat, dairy products, other animal products,
protein feeds, other food, non-food agriculture and non-agriculture. In this
context, however, consideration is limited to the major grain food crops.
As in most studies of impacts of climate change, the modelled yields werefirst estimated for a baseline scenario (a trended future case assuming no
climate change). This involved projection of the agricultural system to the
year 2060 with projected yields and a projected political and economic
context of the world food trade. These projections assumed: a world
population of 10.2 billion by 2060 (the UN median estimate); 50% trade
liberalisation in agriculture introduced gradually by 2020; moderate
economic growth (ranging from 3.0% per year in 1980-2000 to 1.1% per
year in 2040-2060); crop yield for world total, developing and developed
countries increasing annually by 0.7%, 0.9% and 0.6%, respectively.
Three further scenarios were introduced: those which assumed differing
levels of adaptation, which assumed varying amounts of future economic
and population growth , and assumed full rather than partial trade
liberalisation,
Analyses for different socio-economic scenarios
More recently, the projected effects of climate change on global
food supply have been considered under different pathways of future
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socio-economic development, expressed in terms of population and
income level, which have been characterised by the Special Report on
Emissions Scenarios (SRES) of the Intergovernmental Panel on Climate
Change (IPCC). Differing trajectories of population growth and economic
development will affect the level of future climate change and,
simultaneously, the responses of agriculture to changing climate
conditions at regional and global scales. The goal of the study wcoming
decades Consistent climate change scenarios have been taken from SRES-
driven experiments conducted using the UK Hadley Centres third
generation coupled atmosphere-ocean global climate model (HadCM3)32.
The use of a transient AOGCM (HadCM3) allows not only the effect ofthe magnitude of climate change on food production to be assessed but
also the effects of rate of change. The structure and research methods
remain the same as in previous work 3,31,33. Population levels for each
SRES scenario for given timelines were taken from the CIESIN
database33. These levels, together with income level, drive estimated
future demand for cereals in the BLS. The BLS was first run for a
reference case (i.e. assuming no climate change) for each SRES pathway
(A1, A2, B1 and B2) where fluctuations in productivity and prices are
solely the outcome of the socio-economic development pathway. The
model was then re-run with estimated changes in regional cereal yields
due to climate change entered into the model altering regional agricultural
productivity, global food prices and the level of exposure of the global
population to the risk of hunger.
Effects on yields
Each HadCM3 climate change scenario produced by the four
different SRES emissions scenarios instigates a different development
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path for global crop yields. These paths do not diverge, however, until
mid-century. By the 2020s, small changes in cereal yield are evident in all
scenarios, but these fluctuations are within historical variations. Although
there are differences in the mean impacts of the SRES scenarios, the range
of the spatial variability projected is similar. Generally, the SRES
scenarios result in crop yield decreases in developing countries and yield
increases in developed countries (Table 1)33. The A1FI scenario, as
expected with its large increase in global temperatures, exhibits the
greatest decreases both regionally and globally in yields, especially by the
2080s. Decreases are especially significant in Africa and parts of Asia
with expected losses up to 30 percent. In these locations, effects oftemperature and precipitation changes on crop yields are beyond the
inflection point of the beneficial direct effects of CO2. In North America,
South East South America, and Australia, the effects of CO2 on the crops
partially compensate for the stress that the A1FI climate conditions
impose on the crops and result in small yield increases. In contrast to the
A1FI scenario, the coolest climate change scenario (B1) results in smaller
cereal yield decreases.
The contrast between the yield change in developed and developing
countries is largest under the A2 scenarios. Under the A2 scenarios, crop
yields in developed countries increase as a result of moderate temperature
increases, and the direct effects of the high concentration of CO2. In
contrast, crop yields decrease in developing countries as a result of
regional decreases in precipitation and temperature increases. The results
highlight the complex regional patterns of projected climate variables,
CO2 effects, and agricultural systems that affect crop production under
the different SRES futures.
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Effects on cereal production, cereal prices, and risk of hunger
The reference case - the future without climate change. The BLS
projects year-on-year increases in production, assuming no change in
climate, as indicated. The differences between the SRES scenarios reflects
different assumptions about population (and resulting demand) and
income levels (and resulting consumption). While more cereals are being
produced, the increase in demand ensures that global cereal prices also
rise, most notably under the A2 world where increases of more than 160%
(compared to current day market prices) are to be expected by the 2080s.
In contrast, in the A1 and B1 worlds, after a moderate increase of between
30 and 70% by the 2050s, a decline in cereal prices towards the end of thiscentury is projected in accordance with the expected decline in global
populations. The difference between the A1 and B1 worlds which share
identical population growth projections is primarily due to the higher level
of economic development in the A1 world which allows higher market
prices. The result is that A1, B1 and B2 see a decline in the global number
of people at risk of hunger throughout this century as the pressure caused
by increases in cereal prices is offset by an increase in global purchasing
power. In contrast in the A2 world, where inequality of income remains
great, the number is largely unaltered, at around 800 million people.
The future with climate change. The impact of climate change on
global cereal production under the seven SRES scenarios. The changes are
shown as reductions in millions of metric tonnes from the reference case
(the future without climate change). Substantial reductions in production
are estimated assuming no beneficial effects of CO2: About 5 per cent
reductions for B1 and B2 by the 2080s, and 10 per cent for A1 and A2.
The difference can be explained by greater temperature increases in the
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latter. However, when CO2 effects are assumed to be fully operative, the
levels of reduction diminish by about two-thirds, and the differences
between the scenarios are much less clear. It appears that smaller
fertilization effects under B1 and B2 lead to greater reductions than A1
and A2. Much thus depends on how these CO2 effects play out in reality.
At present we do not know, suffice to say that the effects will fall
somewhere between the with CO2 levels and the without CO2 levels.
As would be expected, an inverse pattern in the estimated change in
global cereal prices tends to occur with large price increases (under no
CO2) for the A1 and A2 scenarios, more than a three-fold increase over
the reference case by the 2080s, and less than half this increase under B1and B2. Under both scenarios there is little sign of any effect until after c.
2020.
The measure risk of hunger is based on the number of people whose
incomes allow them to purchase sufficient quantities of cereals31, and
therefore depends on the price of cereals and the number of people at
given levels of income. The number of additional millions at risk of
hunger due to climate change (that is, compared with the reference case)
is shown in Figure 10. Assuming no CO2 effects, the number at risk is
very high under A2 (approaching double the reference case) partly
because of higher temperatures and reduced yields but primarily because
there are many more poor people in the A2 world which has a global
population of 15 billion (c.f. 7 billion in A1FI). And the number of people
at risk is much lower in the B1 and B2 worlds which are characterised
generally by fewer poor people.
Analyses of production potential using Ricardian methods
Based on broadly the same set of the crop yield estimates 34 a
recent study has used a series of Ricardian country and regional models to
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estimate altered food production due to climate change 35. The assumed
climate scenarios are the same as previously discussed, but the economic
models allow for land-use changes that would accompany shifts in land
values due to alterations in comparative advantage between crops, giving
a more realistic indication of the potential response. The results differ only
in degree from those of the previous studies. Global agricultural output is
estimated to decrease by 16 per cent assuming no carbon fertilisation, and
by 3 per cent with full carbon fertilisation . The regional pattern shows
quite strong adverse effects on yield in tropical areas, especially Africa,
the Middle East and the south Asia.
Analyses based on changes in agro-ecological zones.
A very different approach from point-based crop-growth modelling
is the study of how zones of crop suitability may shift location in response
to changes of climate. When combined with modelling of the length of
crop growing season, either due to changes in moisture or heat
availability, this method enables evaluation of both changes in yield at any
given place in combination with changes in extent of suitability 36. These
broadly mirror the estimates on the point-based modelling of a decade
arlier, showing decreases in cereal output in developing countries and
increases in developed countries. Increases in potential occur in northern
parts of North America and Europe, in contrast to decreases in Africa and
South America. These geographical differences are reflected in the
additional numbers estimated to be at risk of undernourishment due to
climate, which for 2080 range from 40 (for the smallest amount of
warming, B2) to 170 million (for the highest, A1FI) (Figure 14).
The two different analyses ( crop model and crop zone suitability)
give broadly similar estimates of global numbers additional at risk from
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hunger or under-nourishment. While both use the BLS the two approaches
adopt quite different methods in modelling altered crop yields; and this
gives greater confidence to estimates of ultimate effects on hunger.
Comparing the range of analyses
Other studies have either used a macro-economic approach, or yield
estimates from previous crop modelling as inputs to different economic
models. One 37 uses six broad land classes around the world and analyses
the change in extent of these due to altered moisture and temperature, the
yield results from which are very similar to the analyses from crop
models. But the economic assumptions in the approach, especially theland-use changes, eliminate three-quarters of the climate-induced
reductions in production, at least until high levels of warming (above 3
deg C) start to reduce land suitability markedly. A summary of the
different approaches by the IPCC 38 indicates that all conclude a decrease
in output and consequent increase in prices, but vary in their conclusion
regarding when (along a pathway of increasing global temperature) this
decrease will occur. The crop modelling and agro-ecological analyses
conclude that prices will rise with even small amounts of warming ( 1 to 2
deg C), while the other analyses suggest that they will first decrease (due
to increased potential with extended growing seasons at higher latitudes)
before decreasing when temperature increases exceed 2 or 3 deg C . This
point of inflection from a positive to a negative effect on global food
output, and whether it occurs at 1 or 2 or 3 degrees C increase in global
temperature, is central to the current debate as to whether global warming
may, for the first few decades, have a beneficial effect. However, as we
have seen, such a point of inflection is dependent on the very uncertain
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mix of the positive effects from higher CO2 and the negative effective
from higher temperature.
Reducing impacts by stabilising CO2 concentrations at lower levels
The final section of this paper explores the implications of the
stabilisation of CO2 concentrations at defined levels39. These
stabilisation scenarios are among the set defined by the Intergovernmental
Panel on Climate Change 40.
Scenarios
Two stabilisation scenarios (stabilising at CO2 concentrations of 550ppmv and 750 ppmv) are considered, and compared with the IS92a
unmitigated emissions scenario41. There is little difference in
concentrations between the two scenariosup to the 2020s, but thereafter
they begin to diverge. The S750 scenario stabilises CO2 concentrations by
2250, whilst the S550 scenario assumes stabilisation occurs by 2150.
Achieving stabilisation at 750 ppmv and 550 ppmv, under the pathways
assumed here, requires cuts in annual CO2 emissions of around 13% and
30% respectively by 2025, relative to the 2025 emissions assumed under
IS92a. We interpret these stabilisation scenarios as representing actual
CO2 concentrations for the purposes of crop and vegetation modelling
(e.g. actual CO2 concentration reaches 750 ppmv by 2250), because there
are no accepted stabilisation scenarios for the other radiatively-significant
trace gases. We therefore assume that all other greenhouse gas
concentrations remain constant at 1990 values.
Effects on yield potential
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The estimated changes in national potential grain yield by the
2080s, assuming no changes in crop cultivars, under the three emissions
scenarios39. Under unmitigated emissions, positive changes in mid and
high latitudes are overshadowed by reductions in yield in the lower
latitudes. These reductions are particularly substantial in Africa and the
Indian subcontinent. However, many of the mapped changes in yield are
small and indistinguishable from the effects of natural climate variability.
Stabilisation at 550 ppmv produces far fewer reductions in yield, although
there would still be reductions in the Indian subcontinent, most of the
Pacific Islands, central America and the majority of African nations.
Stabilisation at 750 ppmv to a large extent produces intermediate changes.However, there are some interesting anomalies. Significant increases in
yields are seen in the mid-latitudes of both hemispheres under S750 which
are not replicated under S550.
The Impact of Climate Change on Agriculture
Climate change would strongly affect agriculture, but scientists still
dont know exactly how.
Most agricultural impacts studies are based on the results of general
circulation models (GCMs). These climate models indicate that rising
levels of greenhouse gases are likely to increase the global average
surface temperature by 1.5-4.5 C over the next 100 years, raise sea-levels
(thus inundating farmland and making coastal groundwater saltier),
amplify extreme weather events such as storms and hot spells, shift
climate zones poleward, and reduce soil moisture. Impacts studies
consider how these general trends would affect agricultural production in
specific regions. To date, most studies have assumed that agricultural
technology and management will not improve and adapt. New studies are
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becoming increasingly sophisticated, however, and "adjustments
experiments" now incorporate assumptions about the human response to
climate change.
Increased concentrations of CO2 may boost crop productivity. In
principle, higher levels of CO2 should stimulate photosynthesis in certain
plants; a doubling of CO2 may increase photosynthesis rates by as much
as 30-100%. Laboratory experiments confirm that when plants absorb
more carbon they grow bigger and more quickly. This is particularly true
for C3 plants (so called because the product of their first biochemical
reactions during photosynthesis has three carbon atoms). Increased carbondioxide tends to suppress photo-respiration in these plants, making them
more water-efficient. C3 plants include such major mid-latitude food
staples as wheat, rice, and soya bean. The response of C4 plants, on the
other hand, would not be as dramatic (although at current CO2 levels these
plants photosynthesize more efficiently than do C3 plants). C4 plants
include such low-latitude crops as maize, sorghum, sugar-cane, and millet,
plus many pastures and forage grasses.
Climate and agricultural zones would tend to shift towards the
poles. Because average temperatures are expected to increase more near
the poles than near the equator, the shift in climate zones will be more
pronounced in the higher latitudes. In the mid-latitude regions (45 to 60
latitude), the shift is expected to be about 200-300 kilometers for every
degree Celsius of warming. Since todays latitudinal climate belts are each
optimal for particular crops, such shifts could have a powerful impact on
agricultural and livestock production. Crops for which temperature is the
limiting factor may experience longer growing seasons.
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While some species would benefit from higher temperatures, others
might not. A warmer climate might, for example, interfere with
germination or with other key stages in their life cycle. It might also
reduce soil moisture; evaporation rates increase in mid-latitudes by about
5% for each 10C rise in average annual temperature. Another potentially
limiting factor is that soil types in a new climate zone may be unable to
support intensive agriculture as practiced today in the main producer
countries. For example, even if sub-Arctic Canada experiences climatic
conditions similar to those now existing in the countrys southern grain-
producing regions, its poor soil may be unable to sustain crop growth.
Mid-latitude yields may be reduced by 10-30% due to increased
summer dryness. Climate models suggest that todays leading grain-
producing areas - in Asia and Africa may experience more frequent
droughts and heat waves by the year 2030. Extended periods of extreme
weather conditions would destroy certain crops, negating completely the
potential for greater productivity through "CO2 fertilization". The
poleward edges of the mid-latitude agricultural zones - northern Canada,
Scandinavia, Russia, and Japan in the northern hemisphere, and southern
Chile and Argentina in the southern one - may benefit from the combined
effects of higher temperatures and CO2 fertilization. But the problems of
rugged terrain and poor soil suggest that this would not be enough to
compensate for reduced yields in the more productive areas.
The impact on yields of low-latitude crops is more difficult to
predict. While scientists are relatively confident that climate change will
lead to higher temperatures, they are less sure of how it will affect
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precipitation - the key constraint on low-latitude and tropical agriculture.
Climate models do suggest, however, that the inter-tropical convergence
zones may migrate poleward, bringing the monsoon rains with them. The
greatest risks for low-latitude countries, then, are that reduced rainfall and
soil moisture will damage crops in semi-arid regions, and that additional
heat stress will damage crops and especially livestock in humid tropical
regions.
The impact on net global agricultural productivity is also difficult to
assess. Higher yields in some areas may compensate for decreases in
others - but again they may not, particularly if todays major foodexporters suffer serious losses. In addition, it is difficult to forecast to
what extent farmers and governments will be able to adopt new
techniques and management approaches to compensate for the negative
impacts of climate change. It is also hard to predict how relationships
between crops and pests will evolve.
Adaptation
A wide variety of adaptive actions may be taken to lessen or
overcome adverse effects of climate change on agriculture. At the level of
farms, adjustments may include the introduction of later- maturing crop
varieties or species, switching cropping sequences, sowing earlier,
adjusting timing of field operations, conserving soil moisture through
appropriate tillage methods, and improving irrigation efficiency. Some
options such as switching crop varieties may be inexpensive while others,
such as introducing irrigation (especially high-efficiency, water-
conserving technologies), involve major investments. Economic
adjustments include shifts in regional production centers and adjustments
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of capital, labor, and land allocations. For example, trade adjustments
should help to shift commodity production to regions where comparative
advantage improves; in areas where comparative advantage declines,
labor and capital may move out of agriculture into more productive
sectors. Studies combining biophysical and economic impacts show that,
in general, market adjustments can indeed moderate the impacts of
reduced yields. A major adaptive response will be the breeding of heat-
and drought-resistant crop varieties by utilizing genetic resources that may
be better adapted to new climatic and atmospheric conditions. Collections
of such genetic resources are maintained in germ-plasm banks; these may
be screened to find sources of resistance to changing diseases and insects,as well as tolerances to heat and water stress and better compatibility to
new agricultural technologies. Crop varieties with a higher harvest index
(the fraction of total plant matter that is marketable) will help to keep
irrigated production efficient under conditions of reduced water supplies
or enhanced demands. Genetic manipulation may also help to exploit the
beneficial effects of CO2 enhancement on crop growth and water use.
Agriculture may decline due to climate change
The note has listed several ways by which these harmful emissions from the
agriculture sector can be reduced. These include better management of water and
fertilizers in the paddy fields and changes in the diet of livestock herds. Such
measures will cut down generation of both nitrous oxide and methane.
Besides, changes in land use patterns by expanding the area under agro-forestryand bio-fuel plantations could also mitigate GHG emissions. But these measures
may, however, lower land availability for food crops.
EFFECT OF CLIMAT CHANGE ON RURAL INDIA
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The study indicates that there will be substantial reduction in water
availability in large parts of north India as roughly 80 percent of water resource
needs are met primarily by Himalayas snow-pack melt during the dry summer
months. With retreating glaciers in the Himalayas and subsequent loss of fossil
water supply to the region is likely to be affected seriously. Global warming is one
of the important consequences of climate change and this will adversely affect
agriculture and rural life, A study c0ndycted at the India Institute of Technology,
Madras, indicates that a major aspect of climate change is sea-level rise and India
is vulnerable to rising sea levels due to a variety of reasons. India has the longest
coastline; India has the low-elevation coastal zones in India will be affected. The
report also suggests that global warming will affect the monsoon patterns in India,causing a significant damage to the health of Indias agricultural sector, which
plays a dominant role in the countrys economy. This report is prepared
independently and the study is based on the existing data provided by Inter-
governmental panel on Climate Change (IPCC), a global body that evaluates the
risk of climate change caused by human activity.
The study further indicates that there will be substantial reduction in water
availability in large parts of north India as roughly 80 per cent of whose water
resource needs are met primarily by Himalayan snow-pack melt during the dry
summer months. With retreating glaciers in the Himalayas and subsequent loss of
fossil water, the water supply to the region is likely to be affected seriously.
Himalayan glaciers and other global ice sheets have contributed more to the global
sea level over the past 80 years than was previously estimated. Similarly, a study
commissioned by Greenpeace India, on climate change notes that rising sea levels
could force about 50 million from Indias densely populated coastal regions to
migrate to interior towns and cities. His may generate severe tensions urban
resources. Climate change is likely to hit India hard in the coming decades. The
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Impact could increased water Scarcity, decreased crop yields, increased risk of
disease, and flooding of coastal areas. Climate change as a result of global a
warming will significantly impact on conditions of food supply and food security.
Since the 1960s,90 per cent of the excess heat due to higher greenhouse gas levels
has gone into the Oceans,7 per cent into warming the atmosphere does not warm
in the ext few year ,that is no reason for comfort so long as the strong warming
trend on the Oceans continues. The Oceans are crucial because they store so much
heat .It takes more than 1000 times more energy to heat a cubic meter of water by
1 degree0 C as it does the same volume of air .Globally, this means that if the
oceans transfer just a tiny fraction of their heat energy to the lower temperature
from year to year is due to heat sloshing back and forth between the oceans andatmosphere, rather tan any overall loss or gain of heat by the entire plant. The state
of the sea surface determines both air temperatures and rainfall. Solar radiation,
temperature, and precipitation are the main drivers of crop growth; therefore
agriculture has always been highly dependent on climate patterns and variations.
Overall, climate change could result in a variety of impacts on agriculture
.Changes in production patterns will occur due to higher temperatures and
changing precipitation patterns.
Meaning of climate change
Climate change refers to statistically significant variation in either the mean
state of the climate or in its variability, persisting for an extended period (typically
decades or longer). Climate change may be due to natural internal processes or
external forcing or to persistent anthropogenic change in the composition of the
atmosphere or in land use. The amount and speed of future climate change will
ultimately depend on:
*Whether greenhouse gases and aerosol concentrations increase, stay the same
or decrease.
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* How strongly features of the climate (e.g. temperature, precipitation and sea
level) respond to changes in greenhouse gas and aerosol concentrations.
* How much the climate varies as a result of natural influences (e.g. form
volcanic activity and changes in the suns intensity) and its internal variability
(referring to random changes in the circulation of the atmosphere and oceans).
Climate changes Impact on Agriculture
Climate change and agriculture are interrelated processes, both of which
take place on a global scale. Global warming is projected to have significant
impacts on conditions affecting agriculture, including temperature,
precipitation and glacial run-of. These conditions determine the carryingcapacity of the biosphere to produce enough food for the human population and
domesticated animals. Rising carbon dioxide levels would also have effects,
both detrimental and beneficial, on crop yields. The overall effect of climate
change on agriculture will depend on the of global climate changes on
agriculture might help to properly anticipate and adapt farming to maximize
agricultural production. Despite technological advances, such as improved
varieties, genetically modified organisms, and irrigation systems, weather is
still a key factor in agricultural productivity, as well as a soil properties and
natural communities. The effect of climate on agriculture is related to
variability in local climate patterns. The earths average surface temperature
has increased by 1degree F in just over the last century.
On the other hand, Agricultural trade has grown in recent years, and
know provides significant amounts of food, on a national level to major
importing countries, as well as comfortable income to exporting ones. The
international aspect of trade and security in terms of food implies the need to
also consider the effects of climate change on a global scale. More favorable
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effects on yield tend to depend to a large extent on realization of the
potentially beneficial effects of carbon dioxide on crop growth and potential
yields is likely to be caused by shortening of the growing period, decreases in
water availability and poor vernalization. In the long run, the climate change
could affect agriculture in the following ways:
1. Productivity, in terms of quantity and quality of crops.
2. Agricultural practices, through changes of water use (irrigation) and
agricultural inputs such as herbicides, insecticides and fertilization.
3. Environmental effects, in particular in relation of frequency and intensity of
soil drainage(leading to nitrogen leaching), soil erosion, reduction of
crop diversity
4. Rural space, through the loss and gain of cultivated lands, land speculation,
land renunciation, and hydraulic amenities.
5. Adaptation, organisms may become more or less competitive, as well as
humans may develop urgency to develop more competitive organisms,
such as flood resistant or salt resistant varieties of rice.
Agriculture and Food Supply
Agriculture is highly sensitive to climate variability and weather extremes,
such as droughts, floods and severe storms. The forces that shape our climate
are also critical to farm productivity; Human activity has already changed
atmospheric characteristics such as temperature, rainfall, levels of carbon
dioxide and ground level ozone. The scientific community expects such trends
to continue. While food production may benefit from a warmer climate, the
increased potential for drought, floods. Additionally, the enduring changes in
climate, water supply and soil moisture could make it less feasible to continue
crop production in certain regions.
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International Policy Issues
The development of climate change policy in India is occurring largely as
response to international developments, particularly the development of
international policies to manage greenhouse gas loadings in the atmosphere being
promoted by the Nations. In order to understand how India policy is likely to
develop an the background to Ministry for the Environment initiatives, it will be
helpful to review the current status of international policies. This is done most
easily by considering the Framework Convention on Climate Change (FCCC).
India along with 176 other countries has endorsed the FCCC which was
finalise at the United Nations Conference on Environment and Development in
Rio de Janeir in June 1992. This convention will go for-ward for approval by the
United Nations General Assembly and become legally binding on its signatories
once there is 50 c more of these.
The primary objective of the FCCC (INC, 1992) is to "achieve . . .
stabilization of greenhouse gas concentrations in the atmosphere at a level that
would prevent dangerous anthropogenic interference with the climate system."
The timing for achieving this objective is specified only as within a time
frame sufficient to allow ecosystems to adapt naturally to climate change, to
ensure that food production is not threatened and to enable economic development
to proceed in a sustainable manner".
The FCCC reaffirms a principle of international law that, while states have
authority within their own boundaries they have a responsibility to avoid
damaging the interests of other states. This pre-empts a -winners and losers"
approach to global climate change For example several studies indicate that highly
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developed countries, such as the USA might be able to adapt to anticipated climate
change under "business as usual" scenario: However, their endorsement of the
FCCC recognizes a responsibility to potential ''Losers under climate change, and
accepts at least an implicit commitment to reduce an ultimately prevent further
climate change.
The general form of commitment accepted by all signatories to the FCCC is
spelled out in article 4 of the convention through which they undertake, among
other things, to make available national inventories of anthropogenic emissions by
sources and removals by sinks of all greenhouse gases not covered by the
Montreal Protocol; and to cooperate in the development and transfer of technologyfor control of greenhouse gases in all sectors including energy, transport, industry,
agriculture, forestry and waste management sectors; and to cooperate in
adaptation to climate change and develop integrated plans for coastal zone
management, water resources and agriculture; Under article 4 of the FCCC
developed countries (including India) undertake rather more specific commitments
to adopt national policies for "modifying longer term trends in anthropogenic
emissions .... recognizing that the return by the end of the present decade to earlier
levels of anthropogenic emissions of carbon dioxide and other greenhouse gases ...
would contribute to such modification". And "each of these parties shall
communicate . . . detailed information on its policies .... as well as on its resulting
projected anthropogenic emissions by sources and removals by sinks of
greenhouse gases . . . . with the aim Of returning individually or jointly to their
1990 levels of these anthropogenic emissions".
This last commitment is the one that will cause the most pressure in the
near term for nations to limit greenhouse gas emissions. In particular compilation
and publication of national greenhouse gas emission inventories, in an
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international environment that is placing higher values on conservation and
sustainability ethics, will provide the strongest political pressure to act on climate
change issues in the next 5 years. Article 12 of the MCC gives more details of
procedures for submission of emission inventories and plans for reducing
emissions. A methodology for preparing national emission inventories has already
been well developed by study Groups operating under the auspices of the OECD
and the Intergovernmental Panel on Climate Change (IPCC), e.g. see OECD 1991,
and it seems clear that this will be used by the United Nations as a basis for
obligations under the FCCC.
The present methodology for preparing and submitting greenhouse gasemission inventories treats each greenhouse gas, e.g. CO, methane, or nitrous
oxide, separately. Emissions for each of the major Greenhouse gases are
categorized by the type of activity that produces the emission. This includes a
category for agriculture.
A significant amount of work has been carried out to develop a measure of
the total Greenhouse gas climate forcing from a single nation or technology. This
means that emissions from different greenhouse gases have to be combined. The
IPCC 1990 report endorsed the concept of a "Global Warming Potential" (GWP)
for this purpose. The GWP is different for each greenhouse gas and measures the
greenhouse effect forcing of that gas relative to the same mass Of CO2 -i.e., it
enables emissions of each gas to be expressed in C02 equivalents. The GWP
concept is discussed in more detail in the following subsection, 2.1.4., but for themoment it is important to recognise that the GWPs for different greenhouse gases
are subject to considerable uncertainty, both conceptual and numerical. Despite
these difficulties there is clearly a desire within the international science and
environmental communities to use GWPs or some similar weighting factor to
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combine emissions and thus establish protocols for monitoring a the total
greenhouse gas forcing from each nation. Even before there is agreement on this
use, we expect GWPs to be used in assessing the environmental value of trading
emissions in one greenhouse gas for emissions in another. Thus it is widely
recognized that burning methane at an emission source such as a landfill reduces
greenhouse effect forcing (and thence emissions of CO2 equivalents) and is
therefore a desirable goal.
The short-term obligations under the FCCC are for each developed nation
separately to reduce its greenhouse gas emissions. Clearly governments have the
authority to choose different ways of achieving this, ranging from "command
control" philosophies to targeted "market intervention" with intermediate policies
available. The implications of government policies on agriculture in this regard are
the main subject of this report.
In addition to controlling greenhouse gas emissions country by country,
consideration is also being given to controlling emissions internationally through
partnership arrangements. In particular proponents of "tradeable emission permits"
see this as a way of allowing some countries, for which the cost of greenhouse gas
reduction might be relatively high, to in effect purchase greenhouse gas reductions
made in countries where the costs were relatively low. This would be done in such
a way that the combined emissions of all countries involved was kept to an agreedlevel. This system could obviously be developed into an international market in
greenhouse gas emission quotas
To summarize the international policy issues from a India perspective:
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The main political pressure to act on climate change in the short term will
come through compilation and publication of greenhouse gas emission
inventories, broken down by economic sectors;
India is free to choose its own approach to limiting greenhouse gas
emissions, the only external pressure being that these should be seen to be
effective. There is still a debate over the relative merits of a "carbon tax" or
"tradeable emission permits" both nationally and internationally;
We should anticipate international agreement on a methodology for
combining emissions of different greenhouse gases to arrive at a total
greenhouse forcing figure for each economic sector, including agriculture.
This will weight methane emissions about 15 to 20 times more heavily thanemissions of the same mass of CO2;
There may become an international market in greenhouse gas emission
quotas which will provide export potential for greenhouse gas "sinks"
particularly to heavily industrialised countries.
Combining Greenhouse Gases - The Global Warming Potential Issue
It is known that incremental additions to the atmosphere of many of the non-
CO2 greenhouse gases, such as methane or nitrous oxide, are much more potent
greenhouse effect forcers than an increment of CO2 itself. This is principally
because each is much more effective, molecule for molecule, at trapping long-
wave radiation that would otherwise escape to space. This is partially offset in
some cases, notably methane, by the much shorter lifetime (e.g. methane about 10
years) than CO2 (about 120 years). A measure of the relative potency is the 'Global
Warming Potential' (GWP) for each gas.
The GWP for a greenhouse gas is a measure of the impact of that gas on
the greenhouse effect relative to the same amount of CO2. IPCC (1990) defines the
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GWP as: "the time integrated commitment to climate forcing from the
instantaneous release of 1 kg of a trace gas expressed relative to that from 1 kg of
carbon dioxide". The 1992 Supplement Report of the IPCC (IPCC 1992)
essentially continues with this definition. In fact this definition is incomplete
(Manning, 1991) and practical calculations implicitly use slightly different
definitions. The simplest calculations of GWP (e.g. Rodhe, 1990) are based on the
direct radiative forcing, that is the additional infra-red radiation absorbed, due to 1
kg of the greenhouse gas and integrated over time, expressed relative to the
corresponding value for 1 kg of CO2. If this is taken over a very long time then in
effect the GWP is the product of two terms, one being the additional infra-red
radiation absorbed and the other the average residence time of an increment of the
gas in the atmosphere, divided by the same two terms evaluated for CO2.
One complication in the definition of GWPs is that it is not possible to
calculate the "time integrated commitment" unless some fixed horizon is set
limiting the period being considered. A GWP will depend upon the 'time horizon'
over which the commitment is accumulated. The 'time horizon' refers to future
time after emission during which the greenhouse effect forcing of the gas is
considered and beyond which it is ignored. A GWP will depend quite strongly
upon the time horizon if the atmospheric lifetime of the gas in question is
comparatively short. An increment of CO2 to the atmosphere has an extremely
long residence time there, and in most mathematical models this is strictly infinite.
But for methane in particular, the residence time is much shorter, at about 10
vents. The effect of this is that when GWPs are calculated over time horizons of a
few decades only part of the long-term effect of CO2 is taken into account and the
GWP is correspondingly larger than for a several-century horizon.
The IPCC (1990) definition of GWP and most recent calculations
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include additional "indirect effects" due to chemical interactions of the gas in the
atmosphere. While CO2 does not have such indirect effects methane in particular
does: methane emissions lead to additional water vapour in the lower stratosphere,
increases in tropospheric ozone, and reduction of the oxidising power of the
atmosphere (Manning, 1991; Lelieveld and Crutzen, 1992). The IPCC (1990)
report had included an estimate of indirect effects in its methane GWP. IPCC
(1992) adjudged that the calculation of these indirect effects was not yet
sufficiently understood to be incorporated in GWPs. The value of 11 is quoted for
the "direct" component of the methane GWP over a time period of 100 years, and
the statement made that the indirect effect is positive "possibly as large as thedirect effect". Thus there is no agreed number for the GWP of methane at this
stage. Lelieveld and Crutzen (1992) using different atmospheric chemistry
scenarios calculate full GWPs of 15 and 20. Manning (1991) has estimated similar
values of 16 and 21 considering additional unpublished work.
Table 1. Reports the GWPs for the important agriculturally sourced greenhouse
gases methane (CH4) and nitrous oxide (N20), for time horizons of 20, 100 and
500 Years, taken from IPCC (1992).
Table 1 Direct GWPs for agriculturally important greenhouse gases
(from IPCC, 1992)
Gas Residence Time Direct GWP for Time Horizons of:
20 year 100 year 500 year
CO2 approx 120 yr 1 1 1
CH4 10.5 yr 35 11 4
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N2O 132 yr 260 270 170
Despite these potential ambiguities in how GWPs are defined, one should
anticipate general agreement to use GWPs for about 100 year horizons. In this
report we have weighted emissions of methane simply by the direct GWP 11, toproduce CO2 equivalent emission. This is done on the basis that there are many
other uncertainties in the calculations involved, and in the face of the lack of any
internationally accepted GWP for methane. However, we expect that if final
GWPs for methane are agreed internationally, and the 100 time horizon is used,
then these will be around 15 to 20 and the greenhouse impact of methane will be
taken to be proportionally larger. On the other hand, there may be a trade off
between the increase due to indirect effects and a decrease due to adapting a
longer time horizon eg. 150 to 200 years.
Agriculture and Climate Change Mitigation
Regardless of the projected or actual impacts of climate change,
agriculture is also likely to be directly or indirectly involved in climate change
mitigation efforts. Greenhouse gas emissions (GHGE) constitute a globalproduction externality which is likely to adversely affect climate. The UNFCCC is
trying to negotiate net GHGE emission reductions. Actions under that convention
yielded the Kyoto Protocol which represents the first significant international
agreement towards GHGE reduction. Agriculture (using a definition including
forestry) is mentioned as both an emitter and a sink in the protocol. Annex lists
agriculture as an emission sources from enteric fermentation, manure
management, rice cultivation, soil management, field burning, and deforestation.
The protocol also lists agriculturally related sinks of afforestation and
reforestation. Additional sources and sinks are under consideration including
agricultural soil carbon.
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Ways Agriculture would be Affected by Climate Change Mitigation
Following the arguments in McCarl and Schneider (1999,2000a), there are at least
four ways agriculture may participate in or be influenced by greenhouse gas
mitigation efforts.
! Agriculture may need to reduce emissions because it releases substantial
amounts of methane, nitrous oxide, and carbon dioxide.
! Agriculture may enhance its absorption of GHGE by creating or expanding
sinks.
! Agriculture may provide products which substitute for GHGE intensive products
displacing emissions.
! Agriculture may find itself operating in a world where commodity and inputprices have been altered by GHGE related policies.
Each of these are discussed briefly in the following section
Agriculture - A source of greenhouse gases
The IPCC (1996) estimates that globally agriculture emits about 50% of total
methane, 70% of nitrous oxide, and 20% of carbon dioxide. Sources of methane
emissions include rice, ruminants and manure. Nitrous oxide emissions come from
manure, legumes, and fertilizer use. Carbon dioxide emissions arise from fossil
fuel usage, soil tillage, deforestation, biomass burning, and land degradation.
Contributions across countries vary substantially, with the greatest differences
between developing and developed countries. Deforestation and land degradation
mainly occurs in developing countries. Agriculture in developed countries uses
more energy, more intensive tillage systems, and more fertilizer, resulting in
fossil-fuel based emissions, reductions in soil carbon, and emissions of nitrous
oxides. In addition, animal herds emit high methane from ruminants and manure
(IPCC (1996) and McCarl and Schneider (1999,2000a) elaborate).
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Agriculture - A sink for greenhouse gases
The Kyoto Protocol allows credits for emission sinks through afforestation
and reforestation. Provisions allow for consideration of additional sources and
sinks. Agriculture can serve as an emission sink in mainly offsetting CO2
emissions. Management practices can increase soil carbon retention (commonly
called carbon sequestration). Such practices include land retirement (conversion to
native vegetation), residue management, less-intensive tillage, land use conversion
to pasture or forest, and restoration of degraded soils. While each of these can
increase the carbon-holding potential of the soil, some issues are worth noting.
Soils can only increase carbon sequestration up to a point. Retained carbon
increases until it reaches a new equilibrium state that reflects the new managementenvironment. As the soil carbon level increases, soil absorption of carbon
decreases and soil potential to become a future emission source since subsequent
alteration of the management regime can lead to carbon releases. Third, enhanced
carbon management can reduce agricultural productivity. (IPCC 1996, 2000,
Marland, McCarl and Schneider (1998) and McCarl and Schneider (1999,2000a)
elaborate).
Agriculture - A way of offsetting net greenhouse gas emissions
Agriculture may provide substitute products which replace fossil fuel
intensive products. One such product is biomass for fuel usage or production.
Biomass can directly be used in fueling electrical power plants or maybe
processed into liquid fuels. Burning biomass reduces net CO2 emissions because
the photosynthetic process of biomass growth removes about 95 percent of CO2
emitted when burning the biomass. Fossil fuel use, on the other hand, releases 100
percentof the contained CO2. Substitute building products can be drawn from
forestry reducing fossil fuel intensive use of steel and concrete. (Marland and
Schmalinger(1997) elaborate). Cotton and other fibers also substitute for
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petroleum based synthetics.
Agriculture - Operating under fuel taxes
The need to reduce emissions and the implementation of emissions
trading will likely affect fossil fuel prices. For example, diesel fuel distributors
might need to purchase an emissions permit, effectively raising fuel prices.
Similarly, the US might implement some sort of fuel tax. The tax and
corresponding transportation cost increases might influence the cost of petrol-
based agricultural chemicals and fertilizers as well as on-farm fuel prices and off-
farm commodity prices.( McCarl, Gowen and Yeats(1999), USDA(1999), Antle et
al (1999), and Konyar and Howitt(2000) elaborate)
Economic Appraisal of Agricultural Effects of Climate Change Mitigation
Actions
A number of climate change mitigation impact studies have been done
although this is very much an emerging literature. McCarl and Schneider
(1999,2000a) provide a review. Across that literature a number of general findings
have emerged.
Agricultural emission reductions and offsets can be cost effective strategies
for GHGE offsets at relatively lower carbon prices. McCarl and Schneider(2000a)
amass substantial evidence for the aforementioned emission reductions and
sequestration options. Recent studies by Pautsch et al (2000), Antle et al (2000)
and McCarl and Schneider (2000b) show low cost potential for agricultural soil
carbon sequestration. The literature cited by D.M. Adams et al(1999) as well as
their numerical results show low cost potential in forest soils and standing timber.
Agriculture can operate in the face of carbon induced fuel price increases
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without great dislocation as shown in the studies by McCarl et al (1999),
USDA(1999) and Antle et al (1999). Konyar and Howitt (2000) show greater
sensitivity but use a $348 per ton carbon price. Francl (1997) shows large net
income losses but used an analytic framework which embodied assumptions
precluding adjustments in either market consumption behavior or production
patterns.
Agricultural emission offsets are competitive with food production. For
example McCarl and Schneider (2000b) find substantial decreases in food
production and increases in food prices at higher carbon prices. Similarly, Konyar
and Howitt(2000) show consumers effects at high carbon price induced fuel taxes.Agricultural soil and forestry based carbon sequestration can be competitive at low
carbon prices. Thus, there is real potential that management and the allocation of
land between forestry and agriculture may be affected by climate change
mitigation efforts. However, while Lal et al (1998) and others provide large
estimates for the potential of carbon sequestration based on land potential in both
of these arenas, studies have shown that at lower carbon prices the realized
sequestration acreage is substantially lower than the total estimated potential. (See
D.M. Adams et al (1999), McCarl and Schneider(2000b), Babcock and
Pautsch(1999) and Antle et al (2000) in contrast with Lal et al 1998 for evidence).
Across the array of potential agricultural emission reduction, substitution
and offset alternatives, there are alternatives with substantially different economic
potential. In particular in the study by McCarl and Schneider(2000b) the
replacement of power plant coal fired electricity generation with biofuels plays a
substantial role but only at carbon prices above $60 per ton while at low prices
agriculturally based soil carbon sequestration, afforestation and fertilization
modifications dominate the set of best strategies. In that study methane and
ethanol strategies exhibited low potential.
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Mitigation activity stimulated by carbon price increases generally improves
producers welfare and decreases consumers welfare (See the results in McCarl
and Schneider(2000b