Upload
others
View
2
Download
4
Embed Size (px)
Citation preview
Proceedings on International Conference on Disaster Risk Management,
Dhaka, Bangladesh, January 12-14, 2019
Page | 319
CLIMATE CHANGE EFFECT ON POTENTIAL EVAPOTRANSPIRATION IN
BANGLADESH
Jannatun Nahar Jerin1and A.R.M. Towfiqul Islam1
ABSTRACT
Potential evapotranspiration (ETo) is considered one of the key factors under changing climate which plays a
pivotal role in irrigation schedule and water resource management. However, how much ETo affected by
climate change has been less understood in Bangladesh. This study aimed to estimate monthly, annual and
decadal ETo using the FAO-56 Penman-Monteith (FAO-56 PM) model based on daily data of 25
meteorological stations across Bangladesh from 1975-2017. To detect ETo trends, the Mann-Kendall (MK)
technique was employed to compare trends with standard. The Sen’s slope estimator was adopted to calculate
the magnitude of trend lines. The results show that approximately 82.67% of the monthly ETo time series had
declined trends, out of which 39.67%, 16.33% and 31% of monthly ETo time series were shown statistically
significant at 0.10, 0.01 and 0.05 levels, respectively. Only 17.33% of the monthly ETo time series had
demonstrated a significant increasing trend. The dominant significant increased trend (p<0.01 level) was
found in February at the Chittagong station, while the dominant significant decreased trend (p<0.01) was
noticed at Mymensing station. Based on an annual and decadal timescale, over 92% and 73% of the stations
had the decreased trend lines; but the ascending trends were observed at Rangamati, Barisal and Bhola
stations, respectively. As a whole, ETo are moving on a decline tendency pattern for almost every station over
Bangladesh; suggesting a paradoxical shifting under background of the global warming.
Keywords: ETo trend, Water use, Bangladesh, Global warming, Penman-Monteith model
Introduction
Potential evapotranspiration study is crucial for irrigation and water resources development and management
in Bangladesh. A better assessment of potential evapotranspiration is important for efficient irrigation
management, crop production, environmental assessment, ecosystem modelers and solar energy system.
According to the fifth assessment report of the Intergovernmental Panel on Climate Change (IPCC), the global
warming trend, which is mainly caused by the increasing amount of greenhouse gas emissions, will increase
continue in future 2100 (IPCC 2014). Bangladesh is already experiencing the effects of climate variability
and climate change (Ali 1996; Mirza 2002; Karim and Mimura 2008; Climate Change Cell 2008,). Different
sectors of natural system such as agriculture, hydrology, and ecosystem have been affected by climate change.
Potential evapotranspiration is expected to increase due to temperature increases. However, the decrease of
observed ETo has been widely detected over recent decades in many areas (Yin et al. 2010;Limjirakan and
Limsakul2012; Darshana et al. 2013). This phenomenon of a discrepancy between expected and observed
trends in evaporation is known as the ‘‘evaporation paradox’ ’Evapotranspiration (ET), one of the primary
elements of the hydrologic cycle that is influenced by climate change. There are a number of climatic
parameters that have been identified to change in ETo. The variation of ETo not only influence by the increased
air temperature, but also other primary climatic factors such as relative humidity, vapor pressure, wind speed
and solar radiation. The changing of ETo at particular station may be influenced by these meteorological
parameters. Although different aspects of ETo in different parts of Bangladesh have been investigated to
some extent; however, no detailed study has yet been conducted on impact of ETo trend in Bangladesh. This
region is known as an agricultural region. Rain-fed cereal production is done most part of the Bangladesh.
Unfortunately, some area has suffered from prolonged droughts during summer season in recent years.
Moreover, over exploitation of groundwater has depleted underground water reservoirs. Drastic shrinkage of
major rivers has created serious problems in its ecosystem and hydrologic balance. In order to meet these
challenges, it seems that a study to detect trends in ETo in Bangladesh is needed.
The objective of this study was to detect monthly, annual and decadal trends of ETo using the FAO-56
Penman-Monteith (FAO-56 PM) model based on daily 25 meteorological stations data in Bangladesh in the
past 4 decades and estimate their magnitudes from 1975-2017 using non-parametric methods, such as MK
and Sen’s estimator.
1 Department of Disaster Management, Begum Rokeya University, Rangpur 5400, Bangladesh
Author:[email protected], *Corresponding author: [email protected]
Proceedings on International Conference on Disaster Risk Management,
Dhaka, Bangladesh, January 12-14, 2019
Page | 320
Methodology
Study area
Bangladesh Meteorological Department (BMD) has
34 weather stations. In this study, 25 stations were
selected (Fig.1) to calculate ETo.Data were checked
for quality. These data were used to estimate daily
ETo using the FAO-56 PM method.
Figure. 1: Location of the study area and the
meteorological stations.The dataset was provided by
BMD.
Methods
FAO-56 Penman-Monteith (PM) method is considered as a standard approach to calculate ET0, which reads:
𝐸𝑇𝑜 =0.408∆(𝑅𝑛−𝐺)+𝛾
900(𝑇+273)
𝑢2(𝑒𝑠−𝑒𝑎)
∆+𝛾(1+0.34𝑢2)…………………. (1)
where ET0: potential evapotranspiration [mm day−1]; Rn: net radiation at the crop surface[MJm−2
day−1];G:soil heat flux [MJ m−2 day−1]; T: daily mean air temperature at 2 m height [°C]; u2: wind speed
at 2 m height [m s−1]; es: saturation vapor pressure[kPa];ea: actual vapor pressure [kPa]; es −ea: saturation
vapor pressure deficit [kPa]; Δ: slope of the vapor pressure curve [kPa °C−1]; and γ: psychrometric constant
[kPa °C−1].
The detailed method of MK and Sen’s estimator can be found in the literature (Rahman et al. 2016). In order
to investigate the spatial variability of ET0, the inverse distance method (IDW) was used. This method
directly implements the assumption that a value of an attribute at a non-sampled location is a weighted average
of known data points occurring within a local neighborhood surrounding the non-sampled location. That is,
things close to one another are more alike than those that are far away. It is known as an exact interpolator
scheme (Burrough and McDonnell 1998).
Results
Preliminary observations and analysis
Table 1 represents descriptive statistics summary of monthly ET0 data obtained from historical climate of all
the stations along with their locations, data standard errors (SE), Range, standard deviation (SD) and
coefficient of variances.
Monthly ETo trends
The spatial distribution of monthly ETo values in the selected station represented in Figs.2 and 3.During the
study period from 1975 to 2017, the highest value of monthly ETo was 236 mm/month (in May), while the
lowest monthly ETo value was 41.2 mm/month (in December).The lowest value of Z in monthly time series
was observed in January at the Mymensing Station (Z=-5.46). On the other hand, some of the monthly ETo
times series had upward trends in which, the largest one belonged to the Chittagong station in February which
was equal to 3.27 (p<0.01) [Table-2]. This station is located in the south-eastern region of Bangladesh.
Annually ETo trends
By summing the monthly values of ETo at each of the selected stations, the annual ETo values obtained [Fig
4]. The overall average of annual ETo was found as 1374.1 mm. As can be seen from the last column of Table
2, above 92% of the stations exhibited downward trends (Table 2). However, only 8% of the stations showed
upward increasing trends. This increased up to 4 % at the 10% level. The largest and smallest values of Z
were equal to 3.14 (p < 0.01) and – 4.65 (p < 0.10), respectively. These two opposite trends belonged to the
Proceedings on International Conference on Disaster Risk Management,
Dhaka, Bangladesh, January 12-14, 2019
Page | 321
cox’s bazar and Hatia stations, respectively.
Table 1: Detailed the geographic and statistical characteristics of the selected stations across Bangladesh
Note that the values in the Table are statistical characteristics. Lat. Means Latitude, Long means Longitude,
Alt means altitude, mamsl meters above the mean sea level, N means north, E means east.
Figure 2. Spatial distribution of monthly ET0 (mm) in the 1st six months
Station
name
Lat.
(N)
Long.
(E)
Alt.,
m amsl
Mean
(m)
Median
(m) Skew Range
Standard
Deviation
Standard
Error Kurtosis Barisal 22.43 90.22 2.1 108.96 106.00 0.43 122.50 25.64 1.13 -0.54
Bogra 24.51 89.22 17.9 113.46 113.05 0.18 160.60 28.62 1.26 -0.50
Comilla 23.26 91.11 7.5 112.20 113.65 0.19 132.70 25.09 1.10 -0.30
Chandpur 23.14 90.42 4.88 113.55 113.20 0.18 129.10 26.05 1.15 -0.65
Feni 23.02 91.25 6.4 112.87 113.36 0.17 130.90 25.43 1.12 -0.51
Coxs bazaar 21.27 91.58 2.1 122.44 117.60 0.69 106.50 22.39 0.99 -0.38
Chittagong 22.13 91.48 5.5 125.74 121.60 0.52 117.50 22.91 1.01 -0.28
Swandip 22.29 91.26 2.1 124.09 118.80 0.69 98.55 21.87 0.96 -0.40
M.court 22.52 91.06 4.87 121.87 117.34 0.59 102.25 22.14 0.97 -0.39
Khepupara 23.59 90.41 1.83 117.99 113.31 0.63 108.10 21.87 0.96 -0.42
Faridpur 23.36 89.51 8.1 114.23 112.54 0.21 127.73 26.93 1.19 -0.73
Dhaka 23.46 90.23 8.45 114.90 112.55 0.26 129.40 28.05 1.23 -0.74
Hatia 22.27 91.06 2.44 111.89 108.70 0.53 124.20 22.80 1.00 -0.26
Khulna 22.47 89.34 2.1 120.58 114.36 0.59 155.48 33.31 1.47 -0.42
Jessore 23.12 89.2 6.1 124.45 117.80 0.63 167.90 36.21 1.59 -0.33
Satkhira 22.43 89.05 3.96 116.71 111.10 0.54 143.65 30.55 1.34 -0.49
Mymensing 24.44 90.25 18 106.27 106.95 0.17 150.20 26.05 1.15 -0.31
Patuakhali 22.2 90.2 1.5 109.04 105.30 0.50 113.20 23.69 1.04 -0.52
Bhola 22.41 90.39 4.3 109.00 105.88 0.46 116.40 24.41 1.07 -0.56
Rajshahi 24.22 88.42 19.5 115.76 113.90 0.42 183.00 32.30 1.42 -0.23
Ishurdi 24.09 89.02 12.9 114.61 114.00 0.28 171.80 30.18 1.33 -0.42
Rangamati 22.22 92.09 68.89 111.07 109.60 0.25 109.20 24.70 1.09 -0.65
Rangpur 25.44 89.16 32.61 107.72 110.00 0.00 136.20 27.92 1.23 -0.70
Srimongol 24.18 91.44 21.95 104.69 108.00 -0.12 145.00 29.03 1.28 -0.85
Sylhet 24.54 91.53 33.53 108.63 106.00 0.42 119.60 21.24 0.94 -0.18
Proceedings on International Conference on Disaster Risk Management,
Dhaka, Bangladesh, January 12-14, 2019
Page | 322
Figure 3. Spatial distribution of monthly ET0 (mm) in the 2nd six months
Figure 4. Spatial distribution of Annual ETo (mm) in Bangladesh
Figure 5. Spatial distribution of decadal ETo in Bangladesh
Proceedings on International Conference on Disaster Risk Management,
Dhaka, Bangladesh, January 12-14, 2019
Page | 323
Decadal ETo trend
The spatial distribution of decadal ETo values in the selected station represented in Fig 5. By summing the
10 years values of ETo at each of the selected stations, the decadal ETo values obtained. The overall average
of decadal ETo value was found as 13727.8 mm.The highest value was 15954.1 mm in Jessore station during
1st decade (1975-1984), whereas the lowest was 11936.6 mm located in Mymensing station during 4th decade
(2005-2014)..Results indicated that at the decadal timescale, about 73% of the stations exhibited decrease
trend. Among them, 14 and 19% showed decreasing ETo trends at 5 and 10% significance level respectively.
Meanwhile, only 27% of the decadal ETo time series had displayed an increasing trend (Table-2).
Table 2. The values of MK Z statistics for the ETo in monthly, annual and decadal timescales across
Bangladesh
Note that the values in the Table are Z statistics. Significant trends (at the p<0.10 level) indicated by bold
numbers, significant trends (at the p<0.05 level) indicated by an asterisk on the numbers, and significant
trends (at the p<0.01 level) indicated by italicized numbers
Station Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Annual D1 D2 D3 D4
Barisal -
3.30* -0.06 -1.89 -0.29 -0.33 0.49 1.85 -0.07 -1.10 -0.74 -1.77 -3.77* -1.65* -1.61 -1.43 -0.18 -0.89
Bogra -5.12 -
2.02*
-
3.06* -1.88 -0.47 -0.47 1.85 -1.32 -0.24 -1.59 -2.37* -3.45* -4.05*
-
2.15* -0.18 -1.43 -0.36
Comilla -4.27 -1.49 -
2.22* -0.47 -1.97* 0.49 1.75 -0.33 -0.38 -2.14* -0.86 -3.60* -1.61
-
1.97*
-
2.15* 1.43 -0.72
Chadpur -4.68 -1.11 -1.51 -1.35 -1.25 -0.32 1.87 -1.37 -1.43 -2.73* -1.79 -3.91 -2.28 -
2.15* -0.72 1.07 -1.07
Feni -4.43 -1.38 -1.81 -1.00 -1.44 -0.07 1.64 -0.67 -1.16 -2.59* -1.77 -3.76* -1.80* -
2.15* -1.43 1.25 -0.72
Coxsbazar -1.12 0.85 -1.25 1.25 0.06 1.84 1.19 1.06 -0.63 -0.95 -1.04 -1.65 3.14 -0.54 -0.36 -1.25 -
1.79*
Chittagong 3.12* 3.27* -0.02 -2.00* -5.42 -1.13 -
0.38
-
2.65* -2.41* -4.94 -3.39* -0.97 -2.53 0.36 -1.43 -0.54 -0.72
Swandip -1.76 0.79 -1.51 0.03 -1.11 1.40 0.45 -0.27 -1.89 -1.92 -1.22 -1.65 -1.80 -0.18 -1.25 -0.89 -1.61
M.court -
2.18* -0.17
-
2.41* -1.40 -2.20* 0.21
-
0.18 -1.42 -2.38* -2.43* -1.42 -1.85 -3.10 -0.36 -1.25 -0.72 -1.07
Khepupara -
3.09* -0.90
-
2.83* -1.17 -2.30* 0.61 0.36 -0.86 -1.99* -2.74* -2.39* -2.69* -3.50* -0.36 -1.61 -1.07 -1.61
Faridpur -4.17 -0.90 -1.32 -1.66 -1.02 -0.43 1.66 -
2.38* -1.96 -2.68* -2.21* -3.75* -2.51* -1.25 -0.54 1.07 -1.07
Dhaka -
3.49* -0.27 -0.93 -1.66 -0.68 -0.69 1.37
-
2.56* -2.20* -2.64* -1.93 -2.55* -2.22* -1.25 -0.18 1.25 -1.07
Hatiya -
3.31*
-
2.56*
-
3.34* -2.30* -2.48* -0.90 0.39 -1.06 -2.11* -3.41* -2.77* -3.67* -4.65* -0.72
-
2.15* -0.72 -1.25
Khulna -4.72 -1.92 -
2.30* -1.92 -0.36 0.96 1.85 -0.36 -0.86 -2.96* -3.86* -4.85 -3.39
-
2.50*
-
1.97* 0.01 1.07
Jessore -4.61 -
2.04*
-
2.30* -2.05* -0.69 1.25 1.80 -0.74 -0.97 -3.33* -4.10 -4.77 -3.58
-
2.50*
-
1.97* 0.18 1.43
Sathkhira -4.39 -1.45 -
2.46* -1.98* -0.52 0.64 1.65 -0.42 -1.38 -2.71* -3.59* -5.14 -3.08 -1.79
-
1.79* 0.18 0.72
Mymensing -5.46 -
3.20*
-
2.46* -1.98* -0.52 0.64 1.65 -0.42 -1.38 -2.71* -3.59* -5.14 -4.20 0.01 -1.35 -1.61 -1.07
Patuakhali -
3.61*
-
2.01*
-
2.23* -1.55 -1.55 -1.28
-
0.37
-
2.01* -1.94 -1.50 -1.35 -4.03* -1.40 0.18
-
1.97* 1.07 -0.36
Bhula -
3.88* -1.41
-
2.39* -1.28 -0.95 -0.71 0.26 -1.55 -1.88 -1.79 -1.77 -4.66* -1.78* -1.25
-
1.79* 0.72 -0.54
Rajshahi -
5.00* -1.85
-
2.08* -2.42* -1.79 -0.12 1.49 -1.00 -0.89 -2.91* -3.22* -5.09* -3.67* 1.07 -1.25 0.18 0.72
Ishurdi -
5.07*
-
2.52*
-
2.67* -2.45* -0.93 -0.51 1.62 -1.18 -0.93 -2.49* -3.24* -4.50* -4.04* -0.36 -0.72 0.01 0.54
Rangamati -1.66 1.06 -0.98 -0.98 -1.55 0.45 1.49 -0.87 -0.25 -2.94* -2.73* -3.04* -1.64* -
2.15* -0.18 0.36 -0.72
Rangpur -
4.62*
-
2.16*
-
3.69* -3.18* -1.05 -1.59 1.55 -0.76 -0.08 -1.04 -1.52 -1.32 -3.99 0.72 0.01
-
2.15* -0.72
Srimonggol 0.86 1.75 0.63 -0.50 -1.98* -0.76 1.11 -0.28 0.09 -0.15 0.79 0.51 3.14 1.53 -
1.79* -0.18 0.01
Sylhet -
2.51* 0.86 0.46 0.50 -0.43 -0.45 1.84 -0.65 0.99 -0.96 -1.75 -0.91 -0.31
-
2.33* -1.61 1.43 -0.18
Proceedings on International Conference on Disaster Risk Management,
Dhaka, Bangladesh, January 12-14, 2019
Page | 324
Discussion
ETo trend analysis and its driving factors
all climatic factors don’t influence the ETo change equally. ETo is positively related with temperature, solar
radiation, wind speed and negatively correlated with relative humidity and rainfall.
Impact on ecology and vegetation restorations
The change in ETo trends would affect regional ecology. We found that monthly, annual and decadal ETo
had a decreasing trend which represents a decline in evaporative demand. Decreases in wind speed may be
responsible for weak atmospheric circulation. Increasing
drought would hinder the growth of vegetation and may
even lead to increase soil erosion in this fragile ecosystem
in the study area.
Influence on water resources and agricultural
production
The change in ETo trends would affect regional
agricultural production and food security et al.2018.The
quality of groundwater is repo. Rising ETo trends in the
upcoming years will adversely affect the agricultural
production of the country (Rahman rted to have become
poor in the catchment area located in the study area. It is
mentioned that Chola Lake, which is known as the Bay of
Bengal in the world, would vanish in foreseeable future.
Conclusion
Possible impact of ETo in Bangladesh due to climate change in past four decades are observed in this study.
The study shows that a significant decreasing ETo trend most of the selected station.ET0 times series is
changing from positive to negative in upcoming years, which significantly influenced the change in ETo
trends in future.The findings of the study would contribute in irrigation water management and planning of
the country and also in furthering the climate change study using modelled data in the context of Bangladesh.
In order to conserve available fresh water and save the sustainability of water-related activities in the study
area, efficient practical decisions should immediately be made by decision-makers.
Reference
Ali A (1996) Vulnerability of Bangladesh to climate change and sea level rise through tropical cyclones and
storm surges. Water Air Soil Pollut 92:171–179
Ayub R, Miah MM (2011) Effects of change in temperature on reference crop evapotranspiration (ETo) in
the northwest region of Bangladesh. In: The fourth annual paper meet and 1st civil engineering
congress, December, 2011, Dhaka, pp 978–984
Chauhan S, Srivastava RK (2008) Performance Evaluation of Reference Evapotranspiration Estimation Using
Climate Based Methods and Artificial Neural Networks. Water Resour Manage (2009) 23:825–837.
DOI 10.1007/s11269-008-9301-5
Dinpashoh Y, Asl SJ, Rasouli AA, Foroughi M, Singh VP (2018) Impact of climate change on potential
evapotranspiration (case study: west and NW of Iran). Theoretical and Applied
Climatology.https://doi.org/10.1007/s00704-018-2462-0
Karim MF, Mimura N (2008) Impacts of climate change and sea-level rise on cyclonic storm surge floods in
Bangladesh. Glob Environ Chang 18:490–500. https ://doi.org/10.1016/j.gloen vcha.2008.05.002
Limjirakan S, Limsakul A (2012) Trends in Thailand pan evaporation from 1970 to 2007. Atmos Res
108:122–127
Mirza MMQ (2002) Global warming and changes in the probability of occurrence of floods in Bangladesh
and implications. Glob Environ Chang 12:127–138. https ://doi.org/10.1016/S0959-3780(02)00002
-X
Mojid MA, Rannu RP, Karim NN (2015) Climate change impacts on reference crop evapotranspiration in
northwest hydrological region of Bangladesh. Int J Climatol 35:4041–4046. https ://doi.
org/10.1002/joc.4260
Figure 6: Shrinkage of the Kholpatua river
in southwestern Bangladesh
Proceedings on International Conference on Disaster Risk Management,
Dhaka, Bangladesh, January 12-14, 2019
Page | 325
Rahman MA, Yunsheng L, Sultana N, Ongoma V (2018) Analysis of reference evapotranspiration (ET0)
trends under climate change in Bangladesh using observed and CMIP5 data sets. Meteorology and
Atmospheric Physics.https://doi.org/10.1007/s00703-018-0596-3