Trong bài báo này, yêu cầu nước tưới cho lúa chiêm xuân tại thành phố Hà Nội và các tỉnh Hưng
Yên, Hà Nam và Nam Định ở miền Bắc của Việt Nam được dự báo dựa trên dữ liệu khí tượng của 6
mô hình khí tượng toàn cầu với kịch bản biến đổi khí hậu A1B. Mô hình CROPWAT 8.0 được sử
dụng để tính toán yêu cầu nước. Kết quả tính toán cho thấy dưới ảnh hưởng của biến đổi khí hậu, hầu
hết các mô hình đều cho kết quả của sự gia tăng yêu cầu nước trong các thời kỳ 2050-2069 và 2080-
2099 khi so sánh với kết quả tính toán từ giữ liệu khí tượng tham khảo giai đoạn 1980-1999. Ngoại
trừ kết quả tính từ mô hình CCCMA_CGCM3_1, yêu cầu nước giảm nhẹ so với thời điểm hiện tại.
Yêu cầu nước tưới tăng lớn nhất đến từ các mô hình MIROC3_2_MEDRES và MRI_CGCM2_3_2a.
Kết quả tính toán với số liệu của trạm Hà Nam, yêu cầu nước tưới tăng đáng kể, vượt 360 mm khi so
sánh với giá trị 260 mm trong giai đoạn 1980-1999. Tiếp đến là tại Hà Nội và Nam Định với giá trị
sấp xỉ 300 mm trong 5 mô hình. Xu hướng gia tăng trong giai đoạn 2080-2099 của yêu cầu nước tiếp
tục xuất hiện trong tất cả các mô hình dưới tác động của biến đổi khí hậu
                
              
                                            
                                
            
 
            
                
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KHOA HC K THUT THuhoahoiY LI VÀ MÔI TRuchoaNG uhoahoiuhoahoiuhoahoi - S 62 (9/2018) 111
BÀI BÁO KHOA H
C 
THE IMPACTS OF CLIMATE CHANGE ON IRRIGATION WATER 
REQUIREMENT FOR SPRING SEASON PADDY IN HA NOI CITY, HA 
NAM, HUNG YEN AND NAM DINH PROVINCES 
Tran Quoc Lap and Nguyen Luong Bang1 
Abstract: In this paper, irrigation water requirement of spring season paddy with the 
meteorological data at Lang, Ha Nam, Hung Yen, and Nam Dinh rain gauge stations of Vietnam 
are forecasted, based on the projected meteorological data of 6 global climate models under A1B 
climate change scenario after using the bias correction and spatial downscaling to increase the 
horizontal resolution. The irrigation water requirements are simulated by CROPWAT model 
version 8.0. The calculation results show an increasing trend under the climate change in the most 
models when compared with present result, except the results of the CCCMA_CGCM3_1 model. 
The results of MIROC3_2_MEDRES, and MRI_CGCM2_3_2a models gives the highest increasing 
values. In Ha Nam province, the irrigation water requirement increases significantly to over 360 
mm compared with 260 mm of referent period. Next increase value is in Ha Noi and Nam Dinh 
provinces, around 300 mm in 5 models. The irrigation water requirement would continue 
increasing trend in the far future from 2080-2099 when compared with the year 2050-2069 and 
reference period (1980-1999) in all models. It means that the increment/decrement of irrigation 
requirement has a strong relationship with the climate variable such as temperature and rainfall 
under the impacts of climate change. 
Keywords: spring season paddy, irrigation water requirement, Global climate models, 
1. INTRODUCTION* 
Climate change is now one of the serious 
problems of human society and the threats of the 
planet. Under the global warming, the rainfall and 
temperature would significantly change and caused 
many of the economic and human losses. 
Especially, in recent decades, the climate change is 
one of the challenges that humanity has to face. 
Climate change impacts on most of the sectors such 
as agriculture, industry, services. Global Warming 
and changes significantly when the temperature 
series throughout the world as the most important 
aspects of climate change in the twenty-first 
century are assessed. Several studies, increasing the 
average surface temperature have been confirmed. 
Calculations based International Institute for 
(IPCC) land and ocean temperatures average 
between 0.3-0.6 degree Celsius between the years 
1900 to 1995 and have an upward trend in 
1Division of Water Resources Engineering, Thuy loi 
University 
temperature about 0.2 to 0.3 degree Celsius in 40 
years (IPCC, 2001). Daily and night temperatures 
in the Centre, South, and East Europe have reviews 
(Neidzweidz, 2012). For hundreds of years, the 
global climate is gradually warming as the main 
characteristic of the significant change; average 
temperature has increased 0.74°C. 
The water demand for all sectors such as 
industrial and municipal uses in developing 
countries would be expected to exceed water 
demand for agriculture purpose between 1995 
and 2020 (Rosegrant and Ringler, 1997). The 
requirement of food in the world will increase 
significantly in the future. An estimated results of 
Lee et al show an increase to 35% in 2020 in 
global rice demand when compared to the 
demand in 1995. Due to the upward trend in the 
rice production, so constraints on water resources 
for agriculture would be more aggravated not 
only in the developed countries but also in the 
developing countries (Lee and Haque, 2005). 
 KHOA HC K THUT THuhoahoiY LI VÀ MÔI TRuchoaNG uhoahoiuhoahoiuhoahoi - S 62 (9/2018) 112
In the past decade, the impact of climate 
change has been particularly evident in Vietnam 
with the repeated occurrence of extreme events 
such as typhoons, heavy rain, droughts, and 
floods. Global warming is the significant 
influence in agricultural and food security. Every 
year, Viet Nam is the second export rice country 
in the world. The northern region of Vietnam, 
one of the biggest region of rice production, is 
heavily affected by climate change. Crop water 
and irrigation water requirements should be 
changed under the background that the 
relationship of precipitation and soil moisture has 
been influenced by the global climate change. 
General Circulation Model (GCM) from the 
IPCC was used to assess the impact of climate 
change. Using the climate variable data from the 
output of GCM, the change trends of crop water 
and irrigation water requirements are analyzed in 
the future. Serious water shortages are being 
occurred in many countries in the world, 
especially in Vietnam and water requirement for 
agriculture is becoming increasingly more and 
scarcer because of the water demands from 
different sectors increase too. The agricultural 
sector is the largest water consumer in Vietnam 
with near 80% of total water demand, so the 
more efficient use of water in agriculture needs 
to be the topmost priority. 
The objective of this research is to study the 
variation of irrigation water requirement for spring 
season paddy using the CROPWAT model under 
the climate change with A1B scenario, with two 
periods 2050-2069 and 2080-2099 at Lang, Ha 
Nam, Hung Yen, and Nam Dinh stations of 
Vietnam. The location of research area showed in 
Figure 1. This paper has been organized in the 
sections, In Section 2, an overview of the dataset 
and methods is presented. Section 3 gives the 
discussion of the variation of irrigation water 
requirement for spring season paddy. Finally, a 
summary is given in Section 4. 
2. DATA AND METHODS 
2.1 Overview of General Climate Models 
(GCMs) and the selection of GCM models for 
this research. 
General Circulation Models predicts the 
variation of climate parameters in the future 100 
years by using the motion equation. Every GCM 
has its unique grid resolution and global area 
coverage. The selection of a particular GCM model 
is based on the grid resolution that is required for 
modelling and the purpose for which the researcher 
is modelling the climatic scenario. For example, if 
the purpose is to estimate the irrigation requirement 
in the watershed over the time period, then the 
GCM has to be selected based on which GCM is 
considering the vegetation characteristics is 
aclimatic variable prediction. However, the GCMs 
models have very coarse in the horizontal 
resolution, usually from 1.5o to 4.5oC (200 km to 
450 km in resolution). So that, in this research, to 
improve the spatial resolution, the author used 
Global climate model output, from the World 
Climate Research Programme's (WCRP's) Coupled 
Model Intercomparison Project phase 3 (CMIP3) 
multi-model dataset (Meehl GA Covey C, 2007), 
were obtained from www.engr.scu.edu/~emaurer 
/global_data/. These data were downscaled as 
described by (Maurer, 2009) using the bias-
correction/spatial downscaling method (Wood, 
2004) to a 0.5-degree grid, based on the 1950-1999 
gridded observations of (Adam, 2003). The number 
of models listed in Table 1 as below. 
Figure 1. The location of study area and four 
meteorological stations 
KHOA HC K THUT THuhoahoiY LI VÀ MÔI TRuchoaNG uhoahoiuhoahoiuhoahoi - S 62 (9/2018) 113
2.2 Materials and methodology 
First of all, daily meteorological data such as 
rainfall and temperature either from observation 
or projection are needed for estimating the 
evapotranspiration of crops. Second, the effective 
rainfall and irrigation water on paddy fields could 
be estimated by simulation method based on the 
water balance 
In addition, data concerning the crop 
coefficient, percolation rate, conveyance loss 
rate, and farming area are collected. In this study, 
the present and future are represented by the 
periods 1980 ÷1999, 2050 ÷ 2069 and 2080 ÷ 
2099 respectively 
Figure 2. Methodology used in the study 
Table 1. GCM models used in this study 
Name of models Resolution (Lat/Lon) Country Primary Reference 
bccr_bcm2_0 2.81ox2.81o 
Bjerknes Centre for Climate 
Research (BCCR), Univ. of 
Bergen, Norway 
Furevik et al., 2003 
cccma_cgcm3_1 3.75o x 3.75o 
Canadian Centre for Climate 
Modelling and Analysis, 
Canada 
Flato and Boer, 2001 
miroc3_2_medres 2.81o x 2.81o 
Frontier Research Center for 
Global Change (JAMSTEC), 
Japan 
K-1 model developers, 
2004 
mpi_echam5 1.875o x 1.875o Max Planck Institute for Meteorology, Germany Jungclaus et al., 2006 
mri_cgcm2_3_2a 2.81o x 2.81o Meteorological Research Institute, Japan Yukimoto et al., 2001 
ukmo_hadcm3 2.50o x 3.75o 
Hadley Centre for Climate 
Prediction and Research/Met 
Office, UK 
Gordon et al., 2000 
For studying the impacts of climatic change 
such as temperature, wind speed, rainfall and 
humidity on the irrigation water requirement on a 
temporal scale, climate crop water requirement 
integrated framework has been developed. 
The Climate Crop Water Requirement 
(CCWR) framework integrates the crop water 
requirement model (CROPWAT) and spatial 
climate variable downscaling technique 
developed by Maurer et al. (Maurer, 2009) using 
the bias-correction/spatial downscaling method 
(Wood, 2004) is used in this study. 
Figure 2 describes the methodology using in 
this paper, in the first step, the author used 6 
GCM models listed in Table 1, because GCM 
models have too coarse in resolution, so the bias 
correction/spatial downscaling method is used 
following the results of Maurer et al 2009 
(Maurer, 2009) to increase the resolution up to 
0.5 degree. The climate variables from GCM 
models include mean air temperature and 
rainfall from 1950 to 2099. Next step, the author 
 KHOA HC K THUT THuhoahoiY LI VÀ MÔI TRuchoaNG uhoahoiuhoahoiuhoahoi - S 62 (9/2018) 114
used the Cropwat model’s version 8.0 for 
calculation the irrigation water requirement for 
spring season paddy with different future mean 
temperature, future rainfall, and compared the 
computed value between future and present to 
find the variations of irrigation water 
requirement for paddy. Finally, some discussion 
and conclusion about the effect of climate 
change on the crop in this region. 
3. RESULTS AND DISCUSSIONS 
3.1 Model calibration and validation 
Model calibration and validation are one of the 
most important steps of the process. The objective 
was to assess the performance of the model in 
simulating climate at the chosen site to 
determinate whether or not it is suitable for using. 
In this study, the spatial climate variable 
downscaling technique developed by Maurer et al. 
(Maurer, 2009) using the bias-correction/spatial 
downscaling method (Wood, 2004) is used. The 
rainfall for calibration and validation used in-situ 
rainfall observed data from 1980 to 1999 at Nam 
Dinh rain gauge station. 
For evaluation of the suitable of the simulation 
results, Nash - Sutcliffe coefficient and correlation 
coefficient were used. In general, the simulation 
model can be judged as a satisfactory if Nash > 
0.5 and correlation > 0.70 for rainfall. 
Table 2. The results of calibration and validation of model parameters for rainfall 
Process Models Index Value Simulation level 
C
a
lib
ra
tio
n
(19
80
-
19
89
) 
BCCR_BCM2_0 NASH 0.52 medium COR 0.74 good 
CCCMA_CGCM3_1 NASH 0.48 poor COR 0.73 good 
MPI_ECHAM5 NASH 0.60 medium COR 0.79 good 
MIROC3_2_MEDRES NASH 0.56 medium COR 0.76 good 
MRI_CGCM2_3_2a NASH 0.51 medium COR 0.72 good 
UKMO_HadCM3 NASH 0.55 medium COR 0.75 good 
V
a
lid
a
tio
n
(19
90
-
19
99
) 
BCCR_BCM2_0 NASH 0.60 medium COR 0.78 good 
CCCMA_CGCM3_1 NASH 0.62 medium COR 0.79 good 
MPI_ECHAM5 NASH 0.72 good COR 0.85 good 
MIROC3_2_MEDRES NASH 0.61 medium COR 0.80 good 
MRI_CGCM2_3_2a NASH 0.69 medium COR 0.84 good 
UKMO_HadCM3 NASH 0.63 medium COR 0.82 good 
Table 2 shows the results of calibration and 
validation of 6 model parameters for rainfall. 
The results showed that in both calibration and 
validation process for rainfall, the most models 
show the values of Nash and correlation indexes 
were with the simulation level from the medium 
KHOA HC K THUT THuhoahoiY LI VÀ MÔI TRuchoaNG uhoahoiuhoahoiuhoahoi - S 62 (9/2018) 115
to good (excepted the CCCMA_CGCM3 model 
in calibration process, Nash coefficient simulation 
level was poor). These were considered to be 
acceptable for simulated and predicted future 
rainfall and irrigation water requirement for spring 
season paddy. 
0
100
200
300
400
500
600
700
800
19
80
19
81
19
82
19
83
19
84
19
85
19
86
19
87
19
88
19
89
R
a
in
fa
ll 
(m
m
)
NAM DINH
OBS BCCR_BCM2 CCCMA_CGCM3
ECHAM5 MIROC3_2_ MRI_CGCM2_3a
UKMO_HadCM3.1
0
100
200
300
400
500
600
700
800
19
90
19
91
19
92
19
93
19
94
19
95
19
96
19
97
19
98
19
99
R
a
in
fa
ll 
(m
m
)
NAM DINH
OBS BCCR_BCM2 CCCMA_CGCM3
ECHAM5 MIROC3_2_ MRI_CGCM2_3a
UKMO_HadCM3.1
(a) (b) 
Figure 3. The observated and simulated precipitation of 6 models at Nam Dinh station for 
(a) Calibration process; (b) Validation process 
Figure 3 shows the results of obseved and 
simulated rainfall at Nam Dinh station for both 
two processes (calibration and validation). 
3.2 The variation of climate variables 
under the global warming. 
a. Variation of temperature 
Figure 4 indicated the temperature of the 
respective scenario A1B extracted from 6 GCM 
models after using downscaling technic. In term 
of seasonality, all the outputs of temperature 
from GCM models suggest that there are likely 
to be higher temperature in all season. As shown 
in Figure 5, the highest increases in temperature 
are estimated from MPI_ECHAM5, 
UKMO_HADCM3 models with near 2.5oC and 
3oC in the year 2050-2069 and 2080-2099 
higher than referent period (1980-1999) 
respectively from April to August at all four 
meteorological stations. The lowest increase for 
the winter period usually from December to 
March with approximately 0.5oC to 1oC in all 
models.
Figure 4. The temperature at four stations: a) Lang, b) Nam Dinh, c) Hung Yen, and 
d) Ha Nam stations from 6 GCM models at present and in the future. 
 KHOA HC K THUT THuhoahoiY LI VÀ MÔI TRuchoaNG uhoahoiuhoahoiuhoahoi - S 62 (9/2018) 116
Figure 5. Total annual rainfall for the year 
1980-1999, 2050-2069, and 2080-2099 at four 
rainfall stations in the northern regions of 
Vietnam. 
b. Total annual rainfall pattern 
In the future, the average pattern of rainfall is 
expected to increase with a small difference 
from the historical data. From Figure 5, except 
the results of MIROC3_2_MEDRES model 
show the total rainfall slightly decrease in the 
future, the computed results of 5 other models 
give an increasing trend in total annual rainfall 
at four rain gauge stations. Precipitation would 
increase from 1800 mm in 1980-1999 to over 
1850 mm from 2050-2069, and at the end of the 
21stcentury, the annual rainfall is increasing 
continuously reaching to near 2000 mm/year at 
Nam Dinh station. The highest increase in total 
rainfall is the simulation resutl of 
CCCMA_CGCM3 model. 
c. Variations of spatial distribution of 
average rainfall in three months January, 
February, and March. 
Figures 6 and 7 show the different mean 
spatial distribution of rainfall in three 
months, January, February, and March in the 
northern region of Vietnam during 2050-
2069, 2080-2099 and 1980-1999. It is clear 
that annual total rainfall under the climate 
change would increase slightly in most 
models, however, the distribution of heavy 
rain during the year would concentrate in the 
rainy season, and the rainfall may have the 
decreasing trend in the northern region of 
Vietnam in the dry season. It means that, 
under the climate change, the water supply 
for crop may be affected. 
3.3 Future irrigation water requirement 
for spring season paddy 
The reference evapotranspiration ETo was 
calculated by FAO Penman-Monteith method, 
ETo is multiplied by an empirical crop 
coefficient (Kc) to produce an estimate of 
crop evapotranspiration (ETc). The irrigation 
water requirement (IWR) for spring season 
paddy in four provinces of the northern 
regions of Vietnam, Ha Noi city, Ha Nam, 
Hung Yen, and Nam Dinh provinces is using 
decision support software –CROPWAT 8.0 
developed by FAO. The caculation results of 
ETc and IWR showed in Figure 8 and Figure 
9 as below. 
Figure 6. The different mean spatial distribution 
of rainfall in January, February, and March 
between duration 2050-2069 and 1980-1999 in 
the Northern regions of Vietnam. 
Figure 7. The different mean spatial distribution 
of rainfall in January, February, and March 
between duration 2080-2099 and 1980-1999 in 
the Northern regions of Vietnam 
KHOA HC K THUT THuhoahoiY LI VÀ MÔI TRuchoaNG uhoahoiuhoahoiuhoahoi - S 62 (9/2018) 117
Figure 8. Evapotranspiration of spring season 
paddy at Lang, Hung Yen, Ha Nam, and Nam Dinh 
stations of Vietnam calculated by 6 GCM models. 
The calculation results indicated that the 
total evapotranspiration crop (Etc) value 
(Figure 8) at 4 meteorological station increase 
in all 6 GCM models. The highest increase 
value is from Ha Nam station. The total average 
ETc rises from 400 mm at reference data (from 
January to June) to near 490 mm in 
MIROC3_2_MEDRES, MPI_ECHAM5, 
MRI_CGCM2_3_2a, and UKMO_Hadcm3 
models in theyear (2050-2069) and over 500 
mm in theyear (2080-2099), and results from 
two models BCCR_BCM2_0 and 
CCCMA_CGCM3_1 show slight increase in 
ETc. The values of ETc would increase if the 
future temperature rise. 
Figure 9. The average irrigation water 
requirement for spring season paddy in Ha Noi, 
Hung Yen, Ha Nam, and Nam Dinh provinces of 
Vietnam calculated by 6 GCM models. 
Figure 9 shows the predicted results of 
irrigation water requirement for spring season 
paddy in Ha Noi, Hung Yen, Ha Nam, and Nam 
Dinh provinces calculated by CROPWAT model 
for the historical period (1980-1999) and in the 
future with different climate variables of 6 GCM 
models. The results of IWR of referent period 
(1980-1999) gives from 250 to near 300 mm in 
four provinces. From Figure 9, except the results 
of CCCM_CGCM3_1, the irrigation water 
requirement for spring paddy slightly decrease 
for the future period from 2050-2069, other 
GCM models show an increase in IWR. The 
highest value comes from the results of 
MIROC3_2_MEDRES and MRI_CGCM2_3_2a 
models. In Ha Nam province, the irrigation water 
requirement increases significantly to over 360 
mm compared with 260 mm of referent period. 
Next increase in IWR is Ha Noi city and Nam 
Dinh province, with the values, is around 300 
mm in 5 models. The irrigation water 
requirement would continue increasing trend in 
the far future (at the end of the21st century) in all 
models. It means that the increment/decrement of 
irrigation need has astrong relationship with the 
temperature and rainfall. 
4. CONCLUSION 
The results of climate variables from CMIP3 
models with bias correction and downscaling 
method show that in the future, under the 
climate change, rainfall from 5 over 6 GCM 
models of four precipitation gauge stations 
would slightly decrease in the dry season (from 
January to March), The temperature will 
increase from 0.5oC to 3.2oC in all outputs of 6 
GCM models. Due to the increase in 
temperature and decrease in precipitation, the 
irrigation water requirement for spring season 
paddy would increase in the most of GCM 
models between the year 2050-2069 and 2080-
2099. This study would be very important 
implications for maker decision in the 
agricultural sector to give the strategies in 
adapting to climate variability under the global 
warming for the northern region of Vietnam. 
 KHOA HC K THUT THuhoahoiY LI VÀ MÔI TRuchoaNG uhoahoiuhoahoiuhoahoi - S 62 (9/2018) 118
REFERENCES 
Adam, J. A. (2003). Adjustment of global gridded precipitation for systematic bias. J. Geophys. 
Res. 108, 1-14. 
IPCC. (2001). Climate change. Cambridge University Press, Cambridge, NY, USA. 
Lee, T. S., and Haque, M. A. (2005). Scheduling the Cropping Calendar in Wet-seeded Ricce 
Schemes in Malaysia. Agricultural Water Management 71, 71-84. 
Maurer, E. A. (2009). Climate Model based consensus on the hydrologic impacts of climate change 
to the Rio Lempa basin of Central America. Hydrology and Enarth System Sciences 13, 183-194. 
Meehl GA Covey C., and Delworth T. (2007). The WCRP CMIP3 multi-model dataset: A new era 
in climate change research. Bulletin of the Amerrican Meteorological Society 88, 1383-1394. 
Neidzweidz, T. E. (2012). Evapotranspiration and crop coefficients from lysimeter measurements 
of mature 'Tempranillo' wine grapes. Agric. Water Manage 112, 13-20. 
Rosegrant M. W., and Ringler C. (1997). Water and land resources and global food supply.23rd 
International Conference of Agriculture Economist on Food Security, Diversification and 
Resource Management: Refocusing the role of Agriculture. Sacramento, California. 
Smith, M. (1992). CROPWAT. A Computer Program for Irrigation Planning and Management; 
Food and Agriculture Organization of the United Nations. Rome, Italy. 
Wood, A. W. (2004). Hydrologic implications of dynamical and statistical approaches to 
downscaling climate model outputs.Climate Change 62, 189-216. 
Maurer, E. A. (2009). Globally Downscaled Climate data. www.engr.scu.edu/ ~emaurer/ 
global_data/. (the data downloaded in February 15, 2018). 
Tóm tắt: 
TÁC ĐỘNG CỦA BIẾN ĐỔI KHÍ HẬU LÊN YÊU CẦU NƯỚC ĐỐI VỚI LÚA CHIÊM 
Ở THÀNH PHỐ HÀ NỘI VÀ CÁC TỈNH HÀ NAM, HƯNG YÊN VÀ NAM ĐỊNH 
Trong bài báo này, yêu cầu nước tưới cho lúa chiêm xuân tại thành phố Hà Nội và các tỉnh Hưng 
Yên, Hà Nam và Nam Định ở miền Bắc của Việt Nam được dự báo dựa trên dữ liệu khí tượng của 6 
mô hình khí tượng toàn cầu với kịch bản biến đổi khí hậu A1B. Mô hình CROPWAT 8.0 được sử 
dụng để tính toán yêu cầu nước. Kết quả tính toán cho thấy dưới ảnh hưởng của biến đổi khí hậu, hầu 
hết các mô hình đều cho kết quả của sự gia tăng yêu cầu nước trong các thời kỳ 2050-2069 và 2080-
2099 khi so sánh với kết quả tính toán từ giữ liệu khí tượng tham khảo giai đoạn 1980-1999. Ngoại 
trừ kết quả tính từ mô hình CCCMA_CGCM3_1, yêu cầu nước giảm nhẹ so với thời điểm hiện tại. 
Yêu cầu nước tưới tăng lớn nhất đến từ các mô hình MIROC3_2_MEDRES và MRI_CGCM2_3_2a. 
Kết quả tính toán với số liệu của trạm Hà Nam, yêu cầu nước tưới tăng đáng kể, vượt 360 mm khi so 
sánh với giá trị 260 mm trong giai đoạn 1980-1999. Tiếp đến là tại Hà Nội và Nam Định với giá trị 
sấp xỉ 300 mm trong 5 mô hình. Xu hướng gia tăng trong giai đoạn 2080-2099 của yêu cầu nước tiếp 
tục xuất hiện trong tất cả các mô hình dưới tác động của biến đổi khí hậu. 
Từ khoá: Biến đổi khí hậu, lúa vụ chiêm xuân, yêu cầu nước tưới, mô hình khí hậu toàn cầu 
Ngày nhận bài: 17/4/2018 
Ngày chấp nhận đăng: 16/8/2018 
            Các file đính kèm theo tài liệu này:
37938_121702_1_pb_9815_2092600.pdf