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The US is a major supplier of food and fiber for the world,
accounting
for more than 25% of the total global trade in wheat, corn,
soybeans, and
cotton. Cropland currently occupies about 400 million acres, or
17% of the
total US land area. In addition, grasslands, and permanent grazing
and
pasturelands, occupy almost 600 million acres, another 26% of US
land
area. The value of agricultural commodities (food and fiber)
exceeds $165
billion at the farm level and over $500 billion, 10% of GDP, after
processing and marketing.
Economic viability and competitiveness are major concerns for
producers
trying to maintain profitability as real commodity prices have
fallen by
about two-thirds over the last 50 years. Agricultural productivity
has
improved at over 1% per year since 1950, resulting in a decline in
both
production costs and prices. This trend maintains intense pressure
on
individual producers to continue to increase the productivity of
their
farms and to reduce costs of production. In this competitive
economic
environment, producers see anything that might increase costs or
limit
their markets as a threat to their viability. Issues of concern
include
regulatory actions that might increase costs, such as efforts to
control
the off-site consequences of soil erosion, agricultural chemicals,
and
livestock wastes; growing resistance to and restrictions on the
use of
genetically modified crops; extreme weather or climate events such
as
droughts and floods; new pests; and the development of pest
resistance to
existing pest control strategies. Future changes in climate will
interact
with all of these factors.
The agriculture sector Assessment considered crop agriculture,
grazing,
livestock, and environmental effects of agriculture. The focus in
this
document is primarily on crop agriculture which was studied most
intensively in this Assessment. Although extensive, the analysis
of crop
yields did not fully consider all of the consequences of possible
changes
in pests, diseases, insects, and extreme events resulting from
climate
change. This analysis assumes continued technological advances and
no
changes in federal policies or international trade.
Crop Yield Changes and Associated Economic Consequences
It is likely that climate change, as defined by the scenarios
examined
in this Assessment, will not imperil the ability of the US to feed
its
population and to export foodstuffs. Results of this Assessment
suggest
that, at the national level, productivity of many major crops will
likely
increase under the climate scenarios used in these crop models.
Crops
showing generally positive results include cotton, corn for grain
and
silage, soybeans, sorghum, barley, sugar beets, and citrus fruits.
Pastures also show positive results.
For other crops, including wheat, rice, oats, hay, sugar cane,
potatoes, and tomatoes, yields are projected to increase under
some
conditions and decrease under others. The crop models assume that
the CO2
fertilization effect will be considerable (see box).
CO2
Effects on Crops
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The actual response to increased CO2
differs among crops. Most commercial crops in the US,
including
wheat, rice, barley, oats, potatoes, and most vegetable
crops, tend
to respond favorably to increased CO2, with a doubling of
atmospheric CO2 concentration leading to yield increases in
the
range of 15-20%. The crop models used in this Assessment
assume a
CO2 fertilization effect in this range, and also assume that
sufficient nutrients and water will be available to support
these
increases. Other crops including corn, sorghum, sugar cane,
and many
tropical grasses, are less responsive to increases in CO2,
with a
doubling of its concentration leading to yield increases of
about
5%.
In situations where crop yields are
severely limited by factors such as nutrient availability,
an
enduring CO2 fertilization effect is very likely to be of
only minor
importance.
Greater concentrations of CO2
generally result in higher photosynthesis rates and may also
reduce
water losses from plants. Photosynthesis is enhanced when
additional
carbon is available for assimilation and so crop yields
generally
rise.
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In the crop yield models, a limited set of on-farm adaptation options
are considered, including changes in planting dates and changes in
varieties. These contribute small additional gains in yields of
dryland
crops and greater gains in yields of irrigated crops. The economic
models
consider a far wider range of adaptations in response to changing
productivity, prices, and resource use, including changes in crops
and the
location of cropping, irrigation, use of fertilizer and
pesticides, and a
variety of other farm management options.
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Model simulations of average
changes in crop yields for 16 crops. The yield changes are
given
as percentages and represent the differences between
current
yields and those projected for two time periods, 2030 and
2090.
Two scenarios of future climate, the Canadian and Hadley,
were
used. The results consider physiological responses of the
crops to
climate under either dryland or irrigated cultivation. |

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They also
consider either "no adaptation" or
"adaptation" responses by producers to climate change.
Adaptations included changes in planting dates and crop
varieties.
Only 11 of the 16 crops were actually modeled: cotton,
wheat
(winter and summer), corn, hay, potato, orange, soybean,
sorghum,
rice, pasture grass. Results for the other crops are based
on
extrapolations from the modeled crops. |
All agricultural regions of the US are not affected to the same
degree
by the climate scenarios studied in this Assessment. In general,
this
study finds that climate change favors northern areas. The
Midwest, West,
and Pacific Northwest exhibit large gains in yields with both
climate
scenarios in the 2030 and 2090 time frames. Crop yield changes in
other
regions vary more widely depending on the climate scenario and
time
period. For example, projected wheat yields in western Kansas
decline
under the Canadian scenario.
Model simulations suggest that the net effects of the climate
scenarios
studied on the agricultural segment of the US economy over the
21st
century are generally positive. The exceptions are simulations
under the
Canadian scenario in the 2030 time period, particularly in the
absence of
adaptation.
Economically, consumers benefit from lower prices while
producers'
profits decline. Under the Canadian scenario, these opposing
economic
effects are nearly balanced, resulting in a small net effect on
the
national economy. The estimated $4-5 billion reduction in
producers'
profits represents a 13-17% loss of income, while the savings of
$3-6
billion to consumers represent less than a 1% reduction in the
consumers'
food and fiber expenditures. This large difference exists because
much of
the final cost of agricultural goods to consumers reflects
processing,
transportation, and retailing costs that the models used here
assume are
not affected by climate. Under the Hadley scenario, producers'
profits
decline by up to $3 billion (10%), while consumers save $9-12
billion (in
the range of 1%).
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Economic Impacts of climate change under the Canadian and Hadley
climates. The economic index is change in welfare expressed
as the
sum of producer and consumer surplus in billions of dollars.
US
(light blue bar above) includes sales and purchases in the
US, while
Total Surplus (dark blue bar) also includes overseas sales
by US
producers. |

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The major difference between the model outputs is that under the
Hadley
scenario, productivity increases are substantially greater than
under the
Canadian, resulting in lower food prices, to the consumers'
greater
benefit. The smaller producer losses in the Hadley scenario,
despite
greater productivity gains and price changes, reflect the fact
that the US
farmers' advantage over foreign competitors grows and they are
thus able
to significantly increase export volume. Analyses show that
producer
versus consumer effects depend on how climate change affects
production
elsewhere in the world. The sector Assessment was not able to
extend its
estimates on crop and livestock production to other regions of the
world
but used worldwide shifts in crop and livestock production
projected in
previous studies.
Regional production change, the total value of crop and
livestock
production, is positive for all regions in both the 2030 and 2090
time
frames under the Hadley scenario. Adaptation measures have a small
additional positive effect. In contrast, this economic index
differs among
regions under the Canadian scenario in both the 2030s and 2090s.
It is
positive for most northern regions, mixed for the northern Plains,
and
negative for Appalachia, the Southeast, the Delta states, and the
southern
Plains. Adaptation measures help somewhat for the southern
regions, but
the value of production is lower in these regions under both the
2030 and
2090 climates considered.
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Regional production change (crop
and livestock production weighted by prices) from a year
2000
baseline was positive for all regions in both the 2030 and
2090
timeframes under the Hadley scenario. In contrast this
index
differed among regions under the Canadian scenario in both
the
2030s and 2090s.
It was positive for most northern
regions, mixed
for the northern Plains, and negative for Appalachia, the
Southeast, the Delta states and the southern Plains. |
Changing Water Demands for Irrigation
At the national level, the models used in this Assessment find
that
irrigated agriculture's need for water declines approximately
5-10% for
2030, and 30-40% for 2090 in the context of the two primary
climate
scenarios. At least two factors are responsible for this possible
reduction. One is increased precipitation in some agricultural
areas. The
other is that faster development of crops due to higher
temperatures
results in a reduced growing period and thereby reduced water
demand. In
the crop modeling analyses done for this Assessment, shortening of
the
growing period reduces plant water-use enough to more than
compensate for
the increased water losses from plants and soils due to higher
temperatures.
The picture for future agricultural water demands at the
regional scale
is less clear and it is possible that it will differ substantially
from
the national picture. At the regional level, there is the
possibility that
overall water use will increase in response to climate change.
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Without adaptation, predicted irrigated yields from 2030 to 2090 offer a less unified prediction for some crops, notably barely and corn. |
With adaptation, predicted irrigated yields from 2030 to 2090 offer a more unified prediction for virtually all crops. |
Surface Water Quality
A case study of agriculture in the drainage basin of the
Chesapeake Bay
was undertaken to analyze the effects of climate change on
surface-water
quality. The Bay is a highly valuable natural resource that has
been
severely degraded in recent decades. Soil erosion and excess
nutrient
runoff from crop and livestock production have played a major role
in the
decline of the Bay's health.
In simulations for this Assessment, under the two climate
scenarios for
2030, loading of excess nitrogen into the Chesapeake Bay due to
corn
production increases by 17-31% compared with the current
situation. These
projected effects may not fully represent the effects of extreme
weather
events such as floods or heavy downpours that wash large amounts
of
fertilizers and animal manure into surface waters. Changes in
future farm
practices, such as better matching of the timing of plant need for
fertilizer with the timing of application, could possibly help to
reduce
the projected impacts. Because efforts are already underway to
protect the
Bay, many of these practices may be required and in use before
2030.
Pesticide Use
The Assessment investigates the relationship between pesticide
use and
climate for crops that require relatively large amounts of
pesticide.
Pesticide use is projected to increase for most crops studied and
in most
states, under the climate scenarios considered. Increased need for
pesticide application on corn is generally in the range of 10-20%,
on
potatoes, 5-15%, and on soybeans and cotton, 2-5%. The results for
wheat
vary widely by state and climate scenario showing changes in
pesticide
application ranging from approximately -- 15 to +15%.
The increase in pesticide use results in slightly poorer
overall
economic performance, but this effect is quite small because
pesticide
expenditures are a relatively small share of production costs.
This
Assessment approach does not consider increased crop losses due to
pests,
implicitly assuming that all additional losses are eliminated
through
increased pest control measures. This may underestimate losses due
to
pests associated with climate change.
In addition, this Assessment does not consider the
environmental
consequences of increased pesticide use and it is possible that
these
would be substantial. In a complete economic analysis, the costs
of
negative impacts of pesticides on the environment would be
considered.
Climate Variability
The consequences of climate change for US agriculture are very
likely
to be affected by changes in climate variability and extreme
events.
Agricultural systems are vulnerable to climate extremes, with
effects
varying from place to place because of differences in soils,
production
systems, and other factors. Changes in precipitation type (rain,
snow, or
hail), timing, frequency, and intensity, along with changes in
wind
(windstorms, hurricanes, and tornadoes), are likely to have
significant
consequences. Heavy precipitation events cause erosion,
waterlogging, and
leaching of animal wastes, pesticides, fertilizers, and other
chemicals
into surface and groundwater.
A major source of weather variability is the El Niño Southern
Oscillation (ENSO). ENSO effects vary widely across the country.
Better
prediction of these events would likely allow farmers to plan
ahead,
altering their choices of which crops to plant and when to plant
them. The
value of improved forecasts of ENSO events under their current
intensity
and frequency has been estimated at approximately $500 million per
year.
As climate warms, ENSO is likely to be affected. Some models
project that
more frequent El Niños and stronger La Niñas will have increasing
impacts on US weather. The potential impacts of changes in
frequency and
strength of ENSO conditions on agriculture were modeled in this
Assessment. An increase in these conditions is found to cost the
US $320
million per year if accurate forecasts of these events are
available and
farmers use them as they plan for the growing season. The increase
in cost
is projected to be greater if accurate forecasts are not available
or not
used.
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Reductions in corn yields often correspond to extreme climate
events including droughts and floods. The record Midwest
floods of
1993 resulted from this being the wettest year on record,
washing
out and flooding many corn fields and resulting in late
replanting.
In 1995, declines in yields resulted from a
sequence
of unusual climate events; a cool wet spring delayed
planting, and
a hot, dry summer affected pollination, and ultimately,
yield. |

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Adaptation Strategies
Adaptations such as changing planting dates and choosing longer
season
varieties are likely to offset losses or further increase yields.
Adaptive
measures are likely to be particularly critical for the Southeast
because
of the large reductions in yields projected for some crops under
the more
severe climate scenarios examined. Breeding for response to CO2
will
likely be necessary to achieve the strong fertilization effect
assumed in
the crop studies. This is an unexploited opportunity and the
prospects for
selecting for CO2 response are good. However, attempts to breed
for a
single characteristic are often not successful, unless other
traits and
interactions are considered. Breeding for tolerance to climatic
stress has
already been heavily exploited and varieties that do best under
ideal
conditions usually also outperform other varieties under stress
conditions. Breeding specific varieties for specific conditions of
climate
stress is therefore less likely to encounter success.
Some adaptations to climate change and its impacts can have
negative
secondary effects. For example, an examination of use of water
from the
Edward's aquifer region around San Antonio, Texas found increased
pressure on groundwater resources that would threaten endangered
species
dependent on spring flows supported by the aquifer. Another
example
relates to agricultural chemical use. An increase in the use of
pesticides
and herbicides is one adaptation to increased insects, weeds, and
diseases
associated with warming. Runoff of these chemicals into prairie
wetlands,
groundwater, and rivers and lakes could threaten drinking water
supplies,
coastal waters, recreation areas, and waterfowl habitat.
The wide uncertainties in climate scenarios, regional variation
in
climate effects, and interactions of environment, economics, and
farm
policy suggest that there are no simple and widely applicable
adaptation
prescriptions. Farmers will need to adapt broadly to changing
conditions
in agriculture, of which changing climate is only one factor. Some
of the
possible adaptations more directly related to climate include:
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Sowing dates and other seasonal changes: Plant two
crops
instead of one or a spring and fall crop with a short fallow
period to
avoid excessive heat and drought in mid-summer. For already
warm
growing areas, winter cropping could possibly become more
productive
than summer cropping.
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New crop varieties: The genetic base is very broad
for many
crops, and biotechnology offers new potential for introducing
salt
tolerance, pest resistance, and general improvements in crop
yield and
quality.
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Water supply, irrigation, and drainage systems: Technologies
and management methods exist to increase irrigation efficiency
and
reduce problems of soil degradation, but in many areas, the
economic
incentives to reduce wasteful practices do not exist.
Increased
precipitation and more intense precipitation will likely mean
that
some areas will need to increase their use of drainage systems
to
avoid flooding and water-logging of soils.
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Tillage practices: A warmer climate will speed the
decay of
soil organic matter by bacteria and fungi. Loss of organic
matter
reduces the capacity of soils to store water and nutrients
essential
for plant growth. Tillage practices that incorporate crop
residues in
the soils would likely combat this loss and improve soil
quality.
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Use near-term climate predictions: Accurate six-month
to
one-year forecasts could possibly reduce losses due to weather
variability. For example, predictions of El Niño events have
proven
useful in regions where El Niño strongly affects weather.
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Other management adjustments: Virtually all
components of the
farming system from planting to harvesting to selling might be
modified to adjust to climate change.
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