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Rice is central to nutrition in Asia. In 1997, rice provided about 700 kilocalories
per person per day or more for approximately 2.9 billion people, most of whom
live in developing countries of Asia and Africa. During the 1990s, rice production
and productivity in Asia grew at a much slower rate than did population. Yield
deceleration of rice (the annual growth rate declined from 2.8% in the 1980s
to 1.1% in the 1990s) in Asia has been attributed to water scarcity, indiscriminate
addition and inefficient use of inputs such as inorganic fertilizers and pesticides,
and policy issues and the reliance on a narrower genetic material base with
impacts on variability (Hazell, 1985; Matson et al., 1997; Naylor et al., 1997).
Several other factors also have contributed to productivity stagnation and the
decline of rice (lower output/input ratio) in the intensive cropping system
(two to three rice crops per year). Key factors currently contributing to the
yield gap in different countries of Asia include biophysical, technical/management,
socioeconomic, institutional/policy, technology transfer, and adoption/linkage
problems.
Urbanization in Asia has accentuated increased demand for fresh vegetables;
this demand is to be met by new production areas combined with more intensified
horticulture crop management to raise the productivity per unit of land and
water. In most cases, urban and peri-urban agriculture initiatives with uncontrolled
use of agrochemicals are a high-risk activity. Adequate steps need to be taken
at regional and local levels to safeguard specialized and diversified urban
production systems (vegetables, fruits, and root crops) through sustainable
intensification of natural resource use and strengthening of decision support
systems. Increased productivity and sustained production of food grains and
legumes, industrial crops (oil, gum and resins, beverage, fiber, medicines,
aromatic plants), and horticultural crops through crop diversification is critical
for food and nutritional security in Asia.
Even minor deviations outside the "normal" weather range seriously impair the
efficiency of externally applied inputs and food production. Moisture stress
from prolonged dry spells or thermal stress resulting from heat-wave conditions
significantly affect the agricultural productivity when they occur in critical
life stages of the crop (Rounsevell et al., 1999). As reported in IPCC (1998),
stress on water availability in Asia is likely to be exacerbated by climate
change. Several studies aimed at understanding the nature and magnitude of gains
or losses in yield of particular crops at selected sites in Asia under elevated
CO2 conditions and associated climatic change have been reported
in the literature (e.g., Lou and Lin, 1999). These studies suggest that, in
general, areas in mid- and high latitudes will experience increases in crop
yield, whereas yields in areas in the lower latitudes generally will decrease
(see also Chapter 5). Climatic variability and change
will seriously endanger sustained agricultural production in Asia in coming
decades. The scheduling of the cropping season as well as the duration of the
growing period of the crop also would be affected.
In general, increased CO2 levels and a longer frost-free growing
season are expected to enhance agricultural productivity in north Asia. The
area under wheat cultivation is likely to expand in the north and west. The
increase in surface temperature also may increase the growing season in temperate
Asia, thereby prolonging the grain-filling period, which may result in higher
yields (Rosenzweig and Hillel, 1998). In Japan, for example, simulation studies
and field experiments indicate that enhanced CO2 levels in a warmer
atmosphere will substantially increase rice yields and yield stability in northern
and north-central Japan (Horie et al, 1995a). In south central and southwestern
Japan, however, rice yields are expected to decline by at least 30% because
of spikelet sterility and shorter rice growing duration (Matsui and Horie, 1992).
Climate change should be advantageous to wheat yield in northeast China. Because
of an increase in respiration in a warmer atmosphere demanding more water availability,
rice yield in China is expected to decline (Wang, 1996a). In central and north
China, higher temperatures during teaseling and drawing stages and low soil
moisture could result in reduced wheat yield. Increases in precipitation should
be favorable for pests, diseases, and weeds in the south (Wang, 1996b; Dai,
1997). In tropical Asia, although wheat crops are likely to be sensitive to
an increase in maximum temperature, rice crops would be vulnerable to an increase
in minimum temperature. The adverse impacts of likely water shortage on wheat
productivity in India could be minimized to a certain extent under elevated
CO2 levels; these impacts, however, would be largely maintained for
rice crops, resulting in a net decline in rice yields (Aggarwal and Sinha, 1993;
Rao and Sinha, 1994; Lal et al., 1998d). Acute water shortage conditions combined
with thermal stress should adversely affect wheat and, more severely, rice productivity
in India even under the positive effects of elevated CO2 in the future.
Key findings on the impacts of an increase in surface temperature and elevated
CO2 on rice production in Asiabased on a study carried out
for Bangladesh, China, India, Indonesia, Japan, Malaysia, Myanmar, the Philippines,
South Korea, and Thailand under the Simulation and System Analysis for Rice
Production Project at the International Rice Research Instituteare summarized
in Table 11-5. Two process-based crop simulation modelsthe
ORYZA1 model (Kropff et al., 1995) and the SIMRIW model (Horie et al., 1995b)suggest
that the positive effects of enhanced photosynthesis resulting from doubling
of CO2 are more than offset by increases in temperature greater than
2°C (Matthews et al., 1995a).
Table 11-5: Model-simulated mean change (%) in potential
yields of rice in Asia under fixed increments of air temperature and ambient
CO2 level (Matthews et al., 1995b). |
|
Model Used and Ambient CO2 Levels |
Percent Change in Mean Potential Rice Yield in Asia
resulting from Surface Air Temperature Increment of
|
0°C
|
+1°C
|
+2°C
|
+4°C
|
|
ORYZA1 Model |
|
|
|
|
340 ppm |
0.00
|
-7.25
|
-14.18
|
-31.00
|
1.5xCO2 |
23.31
|
12.29
|
5.60
|
-15.66
|
2xCO2 |
36.39
|
26.42
|
16.76
|
-6.99
|
|
|
|
|
|
SIMRIW Model |
|
|
|
|
340 ppm |
0.00
|
-4.58
|
-9.81
|
-26.15
|
1.5xCO2 |
12.99
|
7.81
|
1.89
|
-16.58
|
2xCO2 |
23.92
|
18.23
|
11.74
|
-8.54
|
|
More than 10,000 different species of insect pest are found in the tropics,
90% of which are active in the humid tropics. The occurrence, development, and
spread of crop diseases depend on integrated effects of pathogen, host, and
environmental conditions. The survival rate of pathogens in winter or summer
could vary with an increase in surface temperature (Patterson et al., 1999).
Higher temperatures in winter will not only result in higher pathogen survival
rates but also lead to extension of cropping area, which could provide more
host plants for pathogens. Thus, the overall impact of climate change is likely
to be an enlargement of the source, population, and size of pathogenic bacteria.
Damage from diseases may be more serious because heat-stress conditions will
weaken the disease-resistance of host plants and provide pathogenic bacteria
with more favorable growth conditions. The growth, reproduction, and spread
of disease bacteria also depend on air humidity; some diseasessuch as
wheat scab, rice blast, and sheath and culm blight of ricewill be more
widespread in temperate and tropical regions of Asia if the climate becomes
warmer and wetter.
|