Estimating reference evapotranspiration (ETo) at 24 h timesteps has been considered sufficiently accurate for a long time. However, recent advances in weather data acquisition have made it feasible to apply hourly procedures in ETo computation. Hourly timesteps can improve the accuracy of ETo estimates, as data averaged daily may misrepresent evaporative power during parts of the day. This study investigates the differences between daily ETo computations performed at 24 h (ETo,d) and sum of hourly (ETo,h) for rice–wheat cropping systems in the Ganga Basin, India. The meteorological data were collected from an automatic weather station located in an experimental plot at IIT Kanpur, India. Daily and sum-of-hourly ETo computations were performed according to the FAO-PM equation for rice and wheat cropping seasons. Diurnal variations of meteorological variables resulted in an underestimation of ETo when the daily timestep was considered. No significant difference was observed during wet periods. The sum-of-hourly estimates of ETo were able to capture the abrupt changes in climate variables, while the daily ETo failed to represent it as it considered the average values only. As a result, the sums of hourly ETo estimates are more reliable in the Ganga Plains.

  • Diurnal variation of meteorological parameters results in an underestimation of daily ETo in Ganga Basin.

  • The hourly estimates of ETo are able to capture the abrupt changes in climate variables.

  • Hourly sum ETo is smaller than daily estimates when daily evaporation is low in high atmospheric demand periods.

  • The difference between hourly sum and daily ETo methods is low in monsoon months.

Water moves from the land surface and vegetation to the atmosphere through a physical process called evapotranspiration (ET). It is a key part of the hydrological cycle, has a significant impact on the regional water balance, and is directly related to ecosystem productivity (Lu et al. 2011). ET is an important variable in numerical weather forecasting and simulation of global climate models since it is a measure of the rate of change in the global water cycle (Sun & Wu 2001; Jiang et al. 2009; Wang & Dickinson 2012).

In recent years, much attention has been given to the precise and consistent determination of ET in irrigated agriculture, especially in dry or semiarid regions. In these regions, lack of precipitation typically restricts crop growth and output; therefore, it becomes important to reliably estimate ET for better planning and more effective use of the limited water resources (Allen et al. 1998; Irmak et al. 2005; Maestre-Valero et al. 2017).

As direct measurement of ET is a costly and time-consuming process (Bakhtiari et al. 2017), indirect methods that consider the factors that affect ET including meteorological variables such as solar radiation, air temperature, humidity, and wind speed, and crop factors such as crop type, variety, density, and growth stage, are widely used. However, this increases the sensitivity of ET towards these variables and any uncertainty in these will propagate to estimates of ET as well. Various sensitivity and trend analysis studies have been performed to understand the effect of meteorological variables on ET (Ndiaye et al. 2020; Kejna et al. 2021; Fan et al. 2022; Yonaba et al. 2023; Al Mamun et al. 2024). The ET process is also governed by managerial and environmental factors such as soil characteristics, salinity, fertility, crop diseases, and pests (Allen et al. 1998). Different methods may be used to compute reference evapotranspiration (ETo) for different regions according to suitability to local conditions (Allen et al. 1989; Katul et al. 1992; Berengena & Gavilán 2005). While most ETo estimation techniques are empirical and typically rely on statistical correlations between ETo and one or more meteorological variables, some are based on sound physical principles regulating the process (Sharma 1985).

The Penman–Monteith (PM) equation is recommended by the Food and Agriculture Organization (FAO) for calculating the reference evapotranspiration (Allen et al. 1998). Due to its physical basis, the FAO-PM equation offers an advantage over many other equations and can be applied globally without any local calibrations (Wang & Dickinson 2012). A 24 h period is the basic timestep for this type of calculation (Treder & Klamkowski 2017). However, as more electronic weather stations are being developed and installed around the world, weather data are becoming more and more accessible for computing ETo at hourly and even more precise timesteps (Allen et al. 2006). Moreover, the information on plant water, a requirement that is determined at hourly timesteps, might help to manage the watering of shallow-rooted plants and plants cultivated in small containers (Treder & Klamkowski 2017).

It is possible to estimate ET from weather data for different time intervals in the range of sub-hour to a month (Suleiman & Hoogenboom 2009; Trajkovic 2010). The timestep choice depends on the available data and the purpose of the study. The computation of ET obtained using different timesteps may not be similar, especially monthly ET computed from monthly average weather data relative to daily or hourly estimates. It is caused by nonlinearities in the equations that are utilized as well as in the algorithms used to calculate meteorological variables like vapor pressure and the slope of the saturation vapor pressure curve (Trajkovic 2010). In areas where hourly weather data are available and when there are considerable diurnal changes in vapor pressure, wind speed, or cloudiness, the calculation of evapotranspiration at an hourly timestep is more accurate (Ortega-Farias et al. 1995; Allen et al. 2000; Irmak et al. 2005; Wang et al. 2012; Treder & Klamkowski 2017). Additionally, some research suggests that hourly estimates of reference evapotranspiration provide more accurate results and provide better planning and management options for water and soil resources (Treder & Klamkowski 2017; Althoff et al. 2019; Nolz & Rodný 2019).

The advent of networks of automatic weather stations has increased the availability of weather data on a sub-hourly basis. This has triggered debate on the appropriate expression and parameterization for the surface resistance (rs) parameter of the PM equation and the associated coefficient for the reduced form of the FAO-PM equation when applied hourly (Allen et al. 2006). FAO-56 (Allen et al. 1998) recommended a constant surface resistance (rs) 70 s/m for hourly timesteps as it is used for 24-h timesteps. Due to this constant resistance, hourly ETo may occasionally be overestimated during the daytime when actual rs may be somewhat higher and underestimated during the evening when actual rs may be slightly lower. Following some studies (Walter et al. 2000; Irmak et al. 2005) which showed better agreement between ETo,d and ETo,h when hourly ETo uses a lower value for rs than that used for the 24-h timestep, Allen et al. (2006) came up with a recommendation to use rs = 50 s/m during daytime and 200 s/m during night time for hourly ETo computations.

Meteorological variables like solar radiation, air temperature, vapor pressure deficit, and aerodynamic variables are synced in time during ETo,h computation. The mean values used for ETo,d estimation may misrepresent the evaporative power of the environment during parts of the day and may introduce errors in the calculations. These may worsen under conditions where there are significant changes in solar radiation, wind speed, or vapor pressure deficit during the day (Allen et al. 1994; Allen et al. 1998; Bakhtiari et al. 2017; Ji et al. 2017).

Many studies have looked at daily and hourly variation of ETo using the PM method under different climatic conditions (e.g. abrupt diurnal changes, wet and hot in monsoon and cold in winter, semiarid dry and arid conditions, Sahelian climate, etc.) (Itenfisu et al. 2003; Irmak et al. 2005; Ji et al. 2017; Djaman et al. 2018a, 2018b), land use/landcover (e.g. agricultural areas, grass or natural vegetation) (Gavilán et al. 2008; Perera et al. 2015; dos Santos et al. 2021), and small and large study areas (ranging from point scale to continental scale) (Perera et al. 2015; Bakhtiari et al. 2017; Djaman et al. 2018a, 2018b; Althoff et al. 2019) in different parts of the world including Australia, Brazil, Iran, Spain, Turkey, USA, and Western Africa. These studies have shown that ETo computed using both daily and the sum-of-hourly calculation methods varies in season, according to the geographical location and climatic conditions. For example, Perera et al. (2015) compared hourly sum and daily ETo using FAO-PM and ASCE-PM equations for 40 locations across 23 agricultural irrigation areas from nine diverse climate zones over the Australian continent. They observed that ETo,d is always higher than ETo,h when it is computed using FAO-PM, and the ratio between ETo,h and ETo,d is between 0.96 and 1.04 when the ASCE-PM method is used and this variation depends on location, climatic condition, and season. Bakhtiari et al. (2017) computed ETo by both methods using meteorological data collected at 10 min intervals from the Kerman branch agrometeorology station, in Iran. They observed that directly computed daily ETo was consistently greater than ETo,h for some months. Djaman et al. (2018a) did the comparison between semiarid dry conditions (Senegal) and semiarid humid conditions (the Gambia and Guinea). They reported that the daily timestep overestimated the daily ETo relative to the sum-of-hourly ETo by 1.3%–8% for the whole study period. Using datasets collected from 25 automatic meteorological stations across Paraná State, South Region of Brazil, dos Santos et al. (2021) compared hourly sum and daily ETo. They found a 5.1%–7.4% average difference between daily ETo and the sum-of-hourly ETo. They recommended that the hourly sum has a good potential to be used in planning and management in the field of soil and water engineering, in Paraná State.

While these studies offer insightful information on the reliability of using the FAO-PM (Allen et al. 1998) under hourly and daily timesteps in several parts of the world, little is known about the Ganga Plains where irrigated and rainfed rice and wheat productions are predominant. The Ganga Plains account for 50% of India's irrigated areas, but at the same time have the lowest irrigation efficiency (35%–40%). As food security and population growth have increased the demand for water resources, efforts are being made to improve the irrigation efficiency to the maximum achievable (55%–60%) (Central Water Commission, Ministry of Water Resources, River Development and Ganga Rejuvenation 2008). In the Ganga Plains, the variations between the hourly and daily timestep ETo computations are not known. The prime objective of this study is to quantify differences associated with using 24 h timestep ETo, as compared with the sum-of-hourly ETo computations, with the FAO-PM equation in the Ganga Plains. More specifically, it intends to: (i) compare hourly (ETo,h) and daily (ETo,d) computed reference evapotranspiration, (ii) examine the seasonal impact on the hourly sum and daily ETo values, (iii) compare monthly mean hourly sum and daily computed ETo, and (iv) investigate the effect of diurnal changes in meteorological variables on reference evapotranspiration distribution.

Study area

Field experiments were conducted in a 20 m × 30 m experimental agricultural field under rice and wheat crop covers located at the Indian Institute of Technology Kanpur (26.5168° N, 80.2314° E; altitude 126 m above mean sea-level) in the Upper Gangetic Plains of Uttar Pradesh, India (see Figure 1) for the period August 2018–March 2019. Rice and wheat crops were grown in the monsoon (August–November 2018) and winter (December 2018 to March 2019) seasons, respectively.
Figure 1

The geographical location of the study area.

Figure 1

The geographical location of the study area.

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The average farm size on the Indo-Gangetic Plain is less than 0.6 ha and it is decreasing as landholdings increase (Sandhu et al. 2016). Marginal farmers frequently further divide the lands of these farms to support multiple crops during a growing season, which results in farms of a size equivalent to that considered in our study (Monchuk et al. 2010; Deininger et al. 2017). The mean annual precipitation is 801.5 mm, the mean annual temperature is 32.2 °C, and the warmest and coolest months are May and January with a mean temperature of 41.3 and 8.5 °C, respectively (Panwar et al. 2019).

Data collection and ET computation

The wheat crop was irrigated five times in varying quantities, and the rice paddy was kept in ponded water at a depth of 5 cm. In consultation with the local farmers, the amount of irrigation water used for the wheat crop was chosen based on local wheat-growing traditions.

Weather data were collected from the Automatic Weather Station (Virtual Hydromet, India) installed at the IIT Kanpur study site at 15-min intervals. Air temperature and relative humidity were measured using digital sensors with an accuracy of ±0.5 °C and ±2%, respectively. A three-cup anemometer was used to measure the wind speed with accuracy better than 0.5 m/s at 3.3 m height. To find wind direction, a smart position pot having accuracy ±3o was used. A tipping-bucket-type rain gauge was used to measure rainfall with an accuracy of 5% at 25 mm/h rate. The solar radiation sensor, pyranometer, conforming to ISO classification second-class was employed to measure global radiation. The sensor had a nominal sensitivity of 15 μV/W·m−2 and temperature dependence <0.1%/oC. A piezo-resistive silicon membrane barometer was used to measure air pressure. A pressure-type sensor was used to measure evaporation having a resolution of 1 mm. The pan was 1,220 mm in diameter and made of non-corrosive material mounted on a timber frame with pan bird gauge (square steel mesh). The instruments were calibrated, and manual inspection of sensors was regularly done at the field site to ensure a good-quality meteorological dataset.

The daily and hourly reference evapotranspiration for the hypothetical grass reference surface in both wheat and rice crop covers was calculated using the FAO 56 PM (Allen et al. 1998) method from automatically collected weather data with a 15-min interval at the same field. The equation calculates the reference evapotranspiration from the hypothetical grass reference surface using data on temperature, relative humidity, wind speed, and solar radiation.
(1)
where is the daily computed ET; is the net radiation at the crop surface ; G is the soil heat flux density ; is the mean daily air temperature at 2 m height (°C); is the wind speed at 2 m height ; is the saturation vapor pressure ; is the actual vapor pressure (kPa); is the saturation vapor pressure deficit ; Δ is the slope of the vapor pressure curve ; and γ is the psychrometric constant .
The FAO PM equation for hourly timesteps is:
(2)
where Th = mean hourly air temperature (°C); and e°(Th) is the saturation vapor pressure at air temperature Th (kPa).

The steps involved in the computation of daily and hourly reference evapotranspiration are provided in the Supplementary Material and have been taken from the FAO-56 manual.

Evaluation criteria

Comparisons were made using simple linear regression. The linear regressions were forced through the origin so that the resulting equations produce zero ETo when there is no evapotranspiration. Slopes, coefficient of determination (R2), root mean square error (RMSE), and mean bias deviation (MBD) were used to compare ETo values estimated by the different procedures.
(3)
(4)
(5)
where ETo,d is the ETo calculated at the daily timestep; and ETo,h is the sum of 24 h ETo calculated at an hourly timestep and considered as the standard or measured ETo. The overbar indicates the mean of the corresponding variable.

Comparison of hourly sum (ETo,h) and daily (ETo,d) computed reference evapotranspiration

Figure 2(a) and 2(b) show the temporal distribution of ETo,d and ETo,h estimates during the rice (monsoon) and wheat (winter) cropping seasons. There was no significant difference between the two in August but ETo,d is slightly higher than ETo,h when ETo is low. It is because August is the peak-monsoon season; therefore, diurnal variability of meteorological variables is less due to humidity and other dominant factors. In September, ETo,h is lower than daily estimates when evaporation is low and higher when evaporation is high. ETo,h is visibly higher than daily estimates starting from October. Seasonal differences in ETo distribution are clearly visible in the figure. It starts to decrease in October, it is low in December and January, and it increases again in February. Generally, it is observed that ETo,h is smaller than daily estimates when daily evaporation is low in the high atmospheric demand periods as evidenced by lower values observed in August, September, and February.
Figure 2

Temporal distribution of daily (ETo,d) and sum-of-hourly (ETo,h) estimates.

Figure 2

Temporal distribution of daily (ETo,d) and sum-of-hourly (ETo,h) estimates.

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In principle, daily ETo calculated using the ETo,d equation and sum-of-hour basis should be equal to that calculated using the respective daily ETo equation (Perera et al. 2015). However, the scatterplot between the two ETo,d estimations reflects a fundamental difference, where the former method focuses on diurnal changes and the latter method focuses on average conditions for a given day. A comparison between ETo,h and ETo,d calculations considering the entire study period is presented in Figure 3. ETo,h has higher values most of the time as evidenced by the parallel regression line which is laid above the reference line. The slope and intercept of the linear regression line are indicators of systematic bias. In general, ETo,h and ETo,d have a good agreement, with R2 = 0.88 and slope of the regression line close to 1; the positive intercept and slope just above 1 indicate that ETo,d tends to underestimate reference ETo. It thus becomes apparent that the hourly PM model produces higher daily values of evapotranspiration by an average of 10.91% in relation to the values determined with the daily model. There is a significant diurnal variation in meteorological variables in the Ganga Plains (Nair et al. 2007). For example, the air temperature dropped to 10.82 °C at 5 AM and increased to 29.04 °C at 1 PM on 9 November at Kanpur. Therefore, the hourly estimates of ETo were able to capture the abrupt changes in climate variables, while the ETo,d fails to do so as it considers the average values only. As a result, the sums of hourly values are more reliable for ETo estimates in the Ganga Plains.
Figure 3

Scatterplot between daily (ETo,d) and sum-of-hourly (ETo,h) reference evapotranspiration. The red line represents the fitted linear model.

Figure 3

Scatterplot between daily (ETo,d) and sum-of-hourly (ETo,h) reference evapotranspiration. The red line represents the fitted linear model.

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The results obtained agree with observations across the world. Treder & Klamkowski (2017) examined the usefulness of estimating hourly reference evapotranspiration for assessing the water requirements of plants in Skierniewice, Poland. They observed that the hourly PM model produces an average of 11% higher evapotranspiration values than the daily model. Further, they found that the ETo,h estimates are closer to values measured by lysimeter at the study site. Djaman et al. (2018a) reported up to 16.6% higher annual ETo estimation by ETo,h as compared with the daily average approach. The daily timestep overestimated the daily ETo relative to the sum of hourly by 1.3%–8% for the whole study period in selected semiarid dry and humid regions of West Africa. On the other hand, Irmak et al. (2005) used the standardized ASCE Penman–Monteith (ASCE-PM) model and observed 2%–9% higher ETo values in daily timesteps than in hourly sum estimates in a range of climates at six out of seven locations in the United States. They observed that the greatest differences between the two approaches were in locations where strong, dry, hot winds cause an advective increase in ETo, and agreement between the computational timesteps was best in humid regions. Perera et al. (2015) observed that the FAO-PM version of ETo,h shows a consistent underestimation of ETo,d across sites, whereas the ASCE-PM hourly equation did not. The diurnal variation in surface resistance (50 and 200 s/m) for the hourly ASCE-PM equation compared with the constant value of surface resistance (70 s/m) used for the FAO-PM hourly equation is the greatest contributor to their difference. A few studies also showed that the difference between the two approaches is not always significant. Ji et al. (2017) assessed ETo computations in Chinese arid climatic conditions, dry and hot in monsoon and cold in winter, and found that ETo,d was 5%–7% overestimated when compared with the corresponding ETo,h. Gavilán et al. (2008) observed an average 2% underestimation in daily timestep in Andalusia, southern Spain. Generally, as Howell et al. (2000) explained, the reference evapotranspiration obtained with the PM method by using hourly climate data provided better results than the values obtained with the same method by using daily data as it keeps solar radiation, air temperature, vapor pressure deficit, and aerodynamic parameters synchronized in time, in contrast to daily calculation. In this case, with the availability of automatic weather stations, the sum-of-hourly evapotranspiration may be more reliable to estimate water consumption values.

In the present study, RMSE and MBD have relatively high values, equal to 0.45 and −0.31 mm/day, respectively. As shown in the figure, a few data points are located between the regression line and the reference line when ETo is greater than 2 mm/day. This may be related to seasonal or month-wise differences in climatic variables which are reflected in the evaporation estimates. It might be this variation that resulted in higher RMSE and MBD values. The negative MBD tells that daily timestep calculations are underestimating the actual water loss.

Seasonal impact on the hourly sum and daily ETo values

Figure 4 shows the comparison of the ETo,h and ETo,d in the winter and monsoon seasons. There was a slight difference between the ETo,h and ETo,d in both seasons. The regression slopes were 1.02 and 1.26 for the monsoon and winter seasons, respectively, and coefficients of determination of the relationships were as high as 0.84 and 0.97 for the respective seasons. The magnitude of the slope which is close to unity in the monsoon season when it is combined with higher R2 shows a good correlation between the ETo,h and ETo,d estimations. Although very high R2 was observed in the winter season, its slope is far from unity. RMSE values also indicate that good R2 is not a guarantee of a good relation between ETo,h and ETo,d, because R2 explains only the proportion of the variance in the ETo,d that can be explained by the variance in the ETo,h.
Figure 4

Scatterplot between daily (ETo,d) and sum-of-hourly (ETo,h) reference evapotranspiration for (a) monsoon and (b) winter seasons.

Figure 4

Scatterplot between daily (ETo,d) and sum-of-hourly (ETo,h) reference evapotranspiration for (a) monsoon and (b) winter seasons.

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There was a good agreement between ETo,h and ETo,d at small ETo values in both seasons. Overestimation of ETo in daily timestep is observed when evaporation is small in the winter season and it underestimates otherwise and the underestimation increases with increasing evaporation in the monsoon season. The seasonal difference between ETo estimates in both approaches is 5.04% and 14.94% in the monsoon and winter seasons, respectively.

To compare the values of reference evapotranspiration calculated with hourly and daily timesteps, the hourly values for individual days were added up. The statistical analysis was carried out separately for each month (August–March) and shows a high correlation between the values of evapotranspiration determined with the hourly and daily models (Figure 5). There is a very good correlation between the two estimates in August with an R2 of 0.97 and RMSE of 0.20 mm/day. The regression line is almost identical to the reference 1:1 line with a slope of 1.03 and an intercept of −0.23. A slope close to 1 implies that there is a positive linear relationship between both estimates and the negative intercept tells us the daily timestep is underestimating lower ETo. In September, slight overestimation can be observed by the daily estimation at lower evaporation, overestimation at higher evaporation, and their relationship is very good when ETo is inbetween as shown in Figure 5(b). Even though it has a higher R2 and slope of 1.05, daily timestep ETo is underestimated on all the days in October as evidenced by the higher RMSE, i.e. 0.70 mm/day. In November, the agreement is good at lower ETo and the use of daily timestep underestimates higher ETo. In the study area, the winter season starts in December, and obviously, evaporation is low in this month. Similar to what was observed in October, ETo,d underestimated evaporation on all the days. The variability in the daily timestep explains only 22% of the variability in ETo,h. It is much lower than the R2 values observed in the other months in both seasons. Similar trends were observed in January and February, i.e. good agreement between the two at lower ETo and the underestimation increases as ETo increases. In March, the use of the daily timestep underestimates ETo on all the days. However, it shows a very high R2 and a very small intercept.
Figure 5

Scatterplot between daily (ETo,d) and sum-of-hourly (ETo,h) reference evapotranspiration for each month.

Figure 5

Scatterplot between daily (ETo,d) and sum-of-hourly (ETo,h) reference evapotranspiration for each month.

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As shown in Figures 4 and 5, the difference between the two approaches varies monthly and seasonally. The difference ranges from 1.23% to 25.02% which were observed in September and February, respectively. It is quite high but far less than that reported by Bakhtiari et al. (2017) in Iran. They observed that the hourly sum method is 5.8%–44.6% higher than the daily timestep when ETo is computed using the FAO-56 PM equation and it was 7.6%–47.6% higher when they used the ASCE-PM equation in different months. Generally, RMSE increases as we progress in the winter season, ranging between 0.31 and 0.68 mm/day. It may be related to increasing ETo. The difference between ETo,d, and ETo,h estimates is small when evaporation is low and it increases with increasing evaporation. A general trend is observed in Figure 5. The length of the regression line decreases with time during the months of the monsoon season and increases in the months of the winter season. For example, Figure 5(a) and 5(d) show the maximum and minimum stretches of the regression line, respectively, in the monsoon season. Figure 5(e) and 5(h) show the minimum and maximum stretches, respectively, in the winter season.

Figure 6 presents the influence of the daily standard deviation of meteorological hourly values on possible differences between ETo estimates. The observed standard deviations in meteorological variables such as solar radiation, temperature, humidity, precipitation, and wind speed provide valuable information about the seasonal variability of an area. Regions showing high standard deviation in meteorological variables are more susceptible to extreme weather events and this has a crucial impact on agricultural planning (Vogel et al. 2019; Tamoffo et al. 2023; Al Mamun et al. 2024). Solar radiation is a key driver of ET. High standard deviations in solar radiation would lead to unreliable ET estimates which could affect the timing and frequency of crop water requirements (Trnka et al. 2007; Garcia y Garcia et al. 2008). High standard deviation in temperature and precipitation can significantly impact irrigation scheduling, which would lead to over- or under-irrigation and reduced yield (Rahman et al. 2017; Fan et al. 2022). Humidity affects the vapor pressure deficit, which drives the rate of transpiration from plants. This would ultimately influence the evapotranspiration rate. The high standard deviation in wind speed suggests a possibility of strong winds that might damage crops or irrigation systems. Ultimately, a better understanding of the variability in climate variables allows more informed decisions about appropriate crop selection, watering needs, and implementation strategies for extreme events. This will lead to efficient use of resources, better agriculture planning, and improved productivity (Döll 2002; Islam et al. 2019; Jiang et al. 2019).
Figure 6

Influence of daily standard deviation of meteorological variables on the difference between ETo estimates (ETo,d − ETo,h). The red line represents the fitted linear model.

Figure 6

Influence of daily standard deviation of meteorological variables on the difference between ETo estimates (ETo,d − ETo,h). The red line represents the fitted linear model.

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The daily standard deviation of temperature, relative humidity, and solar radiation had a positive correlation to the difference between ETo computed at daily and hourly timesteps in both seasons. However, the standard deviation of wind speed exhibited a negative correlation in the monsoon season and a positive correlation in winter. In monsoon, small standard deviation of temperature is correlated to negative ETo difference. It is related to the underestimation of ETo,h. But in the monsoon season, the standard deviation is high and it is correlated to high ETo differences. Jia et al. (2008) examined the sensitivity of meteorological variables and quantified their impact on reference evapotranspiration of alfalfa (ETr). They found that a 10%, 10%, and 20% increase/decrease in incoming temperature, relative humidity, and solar radiation, respectively, produces a 10%, 4%, and 14% increase/decrease in ETr. However, a ±50% change in wind speed results in only a ±5% change in ETr. They concluded that solar radiation was the most sensitive parameter introducing the largest error in ETo estimation followed by temperature and relative humidity. Similar observations have been reported by Xing et al. (2016), Poddar et al. (2021), and Yonaba et al. (2023). We did a similar analysis and found 5.67%, 0.58%, and 13.27% increase or decrease in computed ETo in the monsoon season and a 4.85%, 0.37%, and 9.91% change in that of the winter season for incoming temperature, relative humidity, and solar radiation changes of 10%, 10%, and 20%, respectively. A ±50% change in wind speed results in only a ±1.89% change in ETo in monsoon and a relatively higher ±4.41% change in the winter season. Similar to seasonal computations, slight changes in computed ETo values were observed when all months were considered. A 5.25%, 0.47%, and 11.53% increase/decrease in ETo was observed for 10%, 10%, and 20% changes in incoming temperature, relative humidity, and solar radiation, respectively. A ±3.20% change in ETo was observed for a ±50% change in wind speed.

It is to be noted that various potential sources of error can be identified in ETo estimations. Properties of measuring instruments/sensors and their accuracy are one of the major factors influencing the observed data (Beven 1979; Meyer et al. 1989; Ritchie et al. 1996). Another source of error could be due to the estimation of climatic variables from other, less accurate, available meteorological data, like estimation of solar radiation from percent sunshine hours or percent sky cover (Lindsey & Farnsworth 1997). An often overlooked and major source of variation in ETo estimation is the temporal sampling frequency of the climatic data. Within the framework of agronomical experiments, for instance, the temporal sampling frequency is often less intensive, sometimes reduced to 30 min, hourly or even daily timesteps (Al-Ghobari 2000) based on the available data-logging equipment. However, climatic variables are often prone to large fluctuations at the smaller timescale. The sampling frequency in this study is kept the same at 15 min for both hourly and daily data computations and it was observed that hourly estimates were better able to capture diurnal variations.

Comparison of monthly mean hourly sum and daily computed ETo

Figure 7 shows the comparison of mean monthly reference evapotranspiration computed by hourly and daily timesteps. There is good agreement between the two methods with a regression slope of 1.22 and a high coefficient of determination R2 of 0.86. However, the values of all metrics are lower than what was observed in daily estimates when the entire study period was considered (Figure 3). The less negative MBD observed in monthly data indicates that the daily timestep method is still underestimating evapotranspiration, but the difference is not significant.
Figure 7

Scatterplot between monthly mean hourly sum and daily computed ETo.

Figure 7

Scatterplot between monthly mean hourly sum and daily computed ETo.

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The magnitude of monthly average ETo computed using both methods and ETo calculated from mean monthly meteorological variables is presented in Figure 8. The three methods showed similar ETo estimates in August and September where diurnal variations are high due to high humidity. Variations are observed in all three methods. ETo increased from August to September in the daily method and it further increased in October in the hourly sum method. It decreased thereafter until December and increased again to March in both methods. ETo computed from mean monthly meteorological variables, ETo,month follows a similar trend as ETo,d. The monthly average of the daily timestep ETo values are higher than the monthly average of the ETo,h values in August, equal in September, and lower in the other months. The percentage difference between ETo estimates of the two methods is temporally variable. For example, the ETo,d is 4.33% and 0.22% higher than the ETo,h in August and September, respectively. The maximum difference was observed in October and March when ETo,h is 18.65% and 17.45% higher than ETo,d, respectively. ETo,month is observed to be higher than ETo,h and ETo,d when there is low atmospheric demand (November, December, January, and February) and it is inbetween when there is higher atmospheric demand (August, October, and March).
Figure 8

Comparison of the monthly average ETo using the three different methods.

Figure 8

Comparison of the monthly average ETo using the three different methods.

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It is possible to compare the total daily ETo for the crop-growing season over the course of a year, which could have some implications for water management in agricultural, hydrological, and environmental studies (Djaman et al. 2018a). For agricultural water management, especially in the Ganga Plains where rainfed crop production is commonly used, the variations in timestep ETo values during the period from March to November are particularly important. Perera et al. (2015) reported seasonal variation in the agreement between the ETo,h and ETo,d techniques in Australia's tropical and arid climates. It is in contrast to what is observed in our study. For example, the ratio of monthly mean ETo computed with daily time to the hourly sum varies from 1.05 in August to 0.81 in October, i.e. the ETo,d estimated is 5% higher than ETo,h in August and 19% lower in October. It is a huge difference considering the climate, farming tradition, and size of the Ganga Plains. Studies showed that the ratio of ETo,d to ETo,h varies with climatic conditions, season, and location. For example, Djaman et al. (2018a) found that the differences in estimates by the two approaches on a seasonal basis were 46 and 69 mm for the March–November period at Sapu and Kankan, respectively, while at Fanaye and Ndiaye, it was 104 and 124 mm. It demonstrates that while the seasonal changes at the Fanaye and Ndiaye stations were high, they were very moderate at the Sapu and Kankan stations. According to Itenfisu et al. (2003), during the course of 76 site years, the average ratio for various Penman-type combination equations ranged from a low of 0.81 to a maximum of 1.14. Djaman et al. (2018a) observed that it ranged from 1.01 to 1.08. Walter et al. (2000) also reported 1.07 at Bushland and 1.04 at Champion, and Irmak et al. (2005) as 1.08 at North Platte and 1.05 at Bushland under a semiarid climate when calculations for the April–October (growing season) period were considered.

Effect of diurnal changes in meteorological variables on ETo distribution

The ensemble hourly distribution of reference evapotranspiration was computed for all months to see how it is distributed in the day and to examine the seasonal and monthly variation in the distribution. Though there is a difference in magnitude, the maximum ETo is observed at midday in all the months. The standard deviation also shows a difference with month and hour of the day: it is high in months where atmospheric demand is high and at midday except in September. Since there is no or near-zero ETo at night the variability is small in this period except in December when there is significant variability even if the evaporation is near-zero. As shown in Figure 9, ETo is small at night. This might be one reason why ETo,h is higher than the daily timestep in this study, because ETo,d estimation ignores any evapotranspiration occurring during nighttime, and assumes that the soil heat flow is zero for the 24 h timestep (Djaman et al. 2018a). Although earlier studies have indicated that nighttime ETo can be assumed as negligible as stomata are closed at night (Jarvis & Mansfield 1981), recently many studies have reported significant stomatal conductance and transpiration at night (Snyder et al. 2003; Mutiibwa & Irmak 2011). According to Tolk et al. (2006), in semiarid and arid regions, the nighttime ETo can be up to 15% of the total ETo. Caird et al. (2007) reported that nighttime transpiration rates are normally 5%–15% of ETo,d and may occasionally reach 30% of daily ETo. According to Irmak et al. (2011), seasonal nighttime evaporative losses in Nebraska ranged between 0.11 and 0.19 mm/night for two years, with a maximum of 0.50 mm/night.
Figure 9

Diurnal patterns of the ensemble mean hourly reference evapotranspiration for each month. Error bars represent one standard deviation.

Figure 9

Diurnal patterns of the ensemble mean hourly reference evapotranspiration for each month. Error bars represent one standard deviation.

Close modal
The ensemble hourly distribution of solar radiation, relative humidity, wind speed, and temperature is shown in Figure 10. The effect of solar radiation on hourly ETo distribution is significant as shown in their similar profiles (Figures 9 and 10(d)). The influence of temperature is also high, but it is limited to certain months. For example, ETo and solar radiation are highest and relative humidity is lowest between 9 AM and 3 PM in March, but the temperature distribution within this range is not the highest as it was in the ETo distribution. Relative humidity has an inverse correlation with ETo, because the lower the relative humidity, the drier the air, and the higher the evaporation. Unlike the other variables, wind speed does not show a well-defined profile and the standard deviation is high. The relatively higher wind speed at night may be the reason why low ETo is observed at nighttime. Though there is a high standard deviation in wind speed, its effect on ETo is small and it agrees with Jia et al. (2008), who reported only a 5% change in ETo for a ± 50% change in wind speed.
Figure 10

Diurnal patterns of the ensemble mean hourly meteorological variables. Error bars represent one standard deviation.

Figure 10

Diurnal patterns of the ensemble mean hourly meteorological variables. Error bars represent one standard deviation.

Close modal

This study analyses the effects of determining reference evapotranspiration using hourly or daily average meteorological variables. The standard deviation of hourly values for meteorological data has a significant impact on the agreement between ETo estimates derived under various timesteps. Larger standard deviations relate to abrupt diurnal changes and are likely to result in underestimation of ETo based on daily averages when compared with hourly timesteps. ETo,d better agrees with ETo,h in periods where the standard deviation in hourly meteorological variables is moderate.

There is a good agreement between ETo,h and ETo,d for small ETo values during monsoon and winter seasons. Underestimation of ETo in daily timesteps is observed in the winter season, and the difference progresses from December to March. During the peak-monsoon season (August and September months), when the standard deviation in meteorological variables at an hourly scale is less, ETo,h and ETo,d have very similar estimates; the difference increases during the monsoon withdrawal phase and reduces with the onset of the winter season. The maximum difference between ETo estimates in both approaches is observed in the winter season. The sensitivity of meteorological variables and their impact on reference evapotranspiration is also quantified. It is observed that the ETo estimates are more sensitive to changes in solar radiation followed by changes in temperature and relative humidity. Further, the ETo estimates are more sensitive to changes in these variables in the monsoon months in comparison with winter months. A ±50% variation in wind speed had a very small effect on the estimates of ETo at the field site, and it was more in the winter season. Unlike the other variables, wind speed did not show a well-defined profile and the standard deviation is high.

The magnitude of monthly average ETo computed using hourly and daily average meteorological variables and ETo calculated from mean monthly meteorological variables are compared. The three estimation methods show similar ETo values in August and September where diurnal variations are low due to high humidity. In addition, the ensemble hourly distribution of reference evapotranspiration is computed for all months to see how it is distributed in the day and to examine the seasonal and monthly variation in the distribution. Though there is a difference in magnitude, the minimum ETo is observed around midday in all the months. The standard deviation also shows a difference with month and hour of the day, and it is high in months where atmospheric demand is high and at midday except in September. Since there is no or near-zero ETo at night, the variability is small in this period except in December when there is significant variability even if the evaporation is near zero.

In the end, we would like to emphasize that the findings of this study may lack generality as the analysis is based on data collected at a single station for two seasons. Further, reference ETo was computed using the FAO-PM equation. It could be of interest to observe how ETo changes when other methods of estimation are used. The variation of crop evapotranspiration for different crops can help in understanding irrigation requirements and aid in better crop planning. In addition, long-term climatic study of different meteorological variables and their influence on ETo can give a better understanding of environmental and climatic changes in an area. The sampling frequency and its ensembles are other points toward future research. With the availability of remotely sensed data and advancements in soft computing techniques, the possibilities of exploration are endless.

In India, where irrigation efficiency is low, the use of the hourly approach can help increase the accuracy of estimated ETo and better planning of irrigation water management. Therefore, it is essential to invest in automated weather stations to guarantee adequate and dependable availability of the necessary meteorological data at the hourly timestep.

E. Y. conceptualized the article, rendered support in data curation, arranged the software, did the formal analysis, validated the data, developed the methodology, and wrote the original draft. N. V. arranged the software, investigated the data, rendered support in formal analysis, wrote the review and edited the article. R. O. conceptualized the article, supervised the article, wrote the review and edited the article, administered the project, and rendered support in funding acquisition.

This research was funded by the Science and Engineering Research Board, Government of India grant number, ECR/2016/000378.

Data cannot be made publicly available; readers should contact the corresponding author for details.

The authors declare there is no conflict.

Allen
R. G.
,
Jensen
M. E.
,
Wright
J. L.
&
Burman
R. D.
1989
Operational estimates of reference evapotranspiration
.
Agronomy Journal
81
,
650
662
.
Allen
R. G.
,
Smith
M.
,
Perrier
A.
&
Pereira
L. S.
1994
An update for the definition of reference evapotranspiration
.
ICID Bulletin
43
(
2
),
1
34
.
Allen
R. G.
,
Pereira
L. S.
,
Raes
D.
&
Smith
M.
1998
Crop Evapotranspiration: Guidelines for Computing Crop Water Requirements. Irrigation and Drainage Paper No. 56
,
Food and Agricultural Organization of the United Nations
,
Rome, Italy
.
Allen
R. G.
,
Walter
I. A.
,
Elliott
R.
,
Mecham
B.
,
Jensen
M. E.
,
Itenfisu, D., Howell, T. A., Snyder, R., Brown, P., Echings, S., Spofford, T., Hattendorf, M., Cuenca, R. H., Wright, J. L. & Martin, D
.
2000
Issues, requirements and challenges in selecting and specifying a standardized ET equation
. In:
National Irrigation Symposium: Proceedings of the 4th Decennial Symposium
(Evans, R. G., Benham, B. L. & Trooien, T. P., eds), American Society of Agricultural Engineers, Saint Joseph, MI, USA
, pp.
201
208
.
Allen
R. G.
,
Pruitt
W. O.
,
Wright
J. L.
,
Howell
T. A.
,
Ventura
F.
,
Snyder
R.
,
Itenfisu
D.
,
Steduto
P.
,
Berengena
J.
,
Yrisarry
J. B.
,
Smith
M.
,
Pereira
L. S.
,
Raes
D.
,
Perrier
A.
,
Alves
I.
,
Walter
I.
&
Elliott
R.
2006
A recommendation on standardized surface resistance for hourly calculation of reference ETo by the FAO56 Penman–Monteith method
.
Agricultural Water Management
81
,
1
22
.
https://doi.org/10.1016/j.agwat.2005.03.007
.
Al Mamun
M. A.
,
Sarker
M. R.
,
Sarkar
M. A. R.
,
Roy
S. K.
,
Nihad
S. A. I.
,
McKenzie
A. M.
,
Hossain
M. I.
&
Kabir
M. S.
2024
Identification of influential weather parameters and seasonal drought prediction in Bangladesh using machine learning algorithm
.
Scientific Reports
14
(
1
),
566
.
https://doi.org/10.1038/s41598-023-51111-2
.
Althoff
D.
,
Filgueiras
R.
,
Dias
S. H. B.
&
Rodrigues
L. N.
2019
Impact of sum-of-hourly and daily timesteps in the computations of reference evapotranspiration across the Brazilian territory
.
Agricultural Water Management
226
,
105785
.
Bakhtiari
B.
,
Khanjani
M. J.
&
Fadaei-Kermani
E.
2017
Differentiation of computed sum of hourly and daily reference evapotranspiration in a semi-arid climate
.
Journal of Applied Research in Water and Wastewater
4
(
2
),
358
362
.
Berengena
J.
&
Gavilán
P.
2005
Reference evapotranspiration estimation in a highly advective semiarid environment
.
Journal of Irrigation and Drainage Engineering
131
,
147
163
.
Beven
K.
1979
A sensitivity analysis of the Penman–Monteith actual evapotranspiration estimates
.
Journal of Hydrology
44
,
169
190
.
https://doi.org/10.1016/0022-1694(79)90130-6
.
Caird
M. A.
,
Richards
J. H.
&
Donovan
L. A.
2007
Nighttime stomatal conductance and transpiration in C3 and C4 plants
.
Plant Physiology
143
,
4
10
.
Central Water Commission, Ministry of Water Resources, River Development and Ganga Rejuvenation
2008
Theme Paper –Integrated Water Resources Development and Management. River Development and Ganga Rejuvenation, Central Water Commission, Ministry of Water Resources, New Delhi, India
.
Deininger
K.
,
Monchuk
D.
,
Nagarajan
H. K.
&
Singh
S. K.
2017
Does land fragmentation increase the cost of cultivation? Evidence from India
.
The Journal of Development Studies
53 (1), 82–98. http://dx.doi.org/10.1080/00220388.2016.1166210
.
Djaman
K.
,
Irmak
S.
,
Sall
M.
,
Sow
A.
&
Kabenge
I.
2018a
Comparison of sum-of-hourly and daily time step standardized ASCE Penman–Monteith reference evapotranspiration
.
Theoretical and Applied Climatology
134
,
533
543
.
https://doi.org/10.1007/s00704-017-2291-6
.
Djaman
K.
,
Koudahe
K.
,
Lombard
K.
&
O'Neil
M.
2018b
Sum of hourly vs. daily Penman–Monteith grass-reference evapotranspiration under semiarid and arid climate
.
Irrigation and Drainage Systems Engineering
7
,
202
.
https://doi.org/10.4172/2168-9768.1000202
.
Döll
P.
2002
Impact of climate change and variability on irrigation requirements: a global perspective
.
Climatic Change
54
(
3
),
269
293
.
https://doi.org/10.1023/A:1016124032231
.
dos Santos
A.
,
de Souza
J. L. M.
&
Rosa
S. L. K.
2021
Hourly and daily reference evapotranspiration with ASCE-PM model for Paraná State, Brazil
.
Revista Brasileira de Meteorologia
36
(2), 197–209. doi:10.1590/0102-77863610009
.
Fan
X.
,
Zhu
D.
,
Sun
X.
,
Wang
J.
,
Wang
M.
,
Wang
S.
&
Watson
A. E.
2022
Impacts of extreme temperature and precipitation on crops during the growing season in South Asia
.
Remote Sensing
14
(
23
),
6093
.
https://doi.org/10.3390/rs14236093
.
Garcia y Garcia
A.
,
Guerra
L. C.
&
Hoogenboom
G.
2008
Impact of generated solar radiation on simulated crop growth and yield
.
Ecological Modelling
210
(
3
),
312
326
.
https://doi.org/10.1016/j.ecolmodel.2007.08.003
.
Gavilán
P.
,
Estévez
J.
&
Berengena
J.
2008
Comparison of standardized reference evapotranspiration equations in Southern Spain
.
Journal of Irrigation and Drainage Engineering
134
,
1
12
.
https://doi.org/10.1061/(ASCE)0733-9437(2008)134:1(1)
.
Howell
T. A.
,
Evett
S. R.
,
Schneider
A. D.
,
Dusek
D. A.
&
Copeland
K. S.
2000
Irrigated fescue grass ET compared with calculated reference ET
. In:
National Irrigation Symposium: Proceedings of the 4th Decennial Symposium
,
(Evans, R. G., Benham, B. L. & Trooien, T. P., eds), American Society of Agricultural Engineers, Saint Joseph, MI, USA, pp. 228–242
.
Irmak
S.
,
Howell
T. A.
,
Allen
R. G.
,
Payero
J. O.
&
Martin
D. L.
2005
Standardized ASCE Penman–Monteith: impact of sum-of-hourly vs. 24-hour timestep computations at reference weather station sites
.
Transactions of the ASCE
48
,
1063
1077
.
Islam
A. R. M. T.
,
Shen
S.
,
Yang
S.
,
Hu
Z.
&
Chu
R.
2019
Assessing recent impacts of climate change on design water requirement of Boro rice season in Bangladesh
.
Theoretical and Applied Climatology
138
(
1–2
),
97
113
.
https://doi.org/10.1007/s00704-019-02818-8
.
Itenfisu
D.
,
Elliott
R. L.
,
Allen
R. G.
&
Walter
I. A.
2003
Comparison of reference evapotranspiration calculations as part of the ASCE standardization effort
.
Journal of Irrigation and Drainage Engineering
129
,
440
448
.
Jarvis
P. G.
&
Mansfield
T. A.
1981
Stomatal Physiology
.
Cambridge University Press
,
Cambridge, UK
.
Ji
X. B.
,
Chen
J. M.
,
Zhao
W. Z.
,
Kang
E. S.
,
Jin
B. W.
&
Xu
S. Q.
2017
Comparison of hourly and daily Penman–Monteith grass- and alfalfa-reference evapotranspiration equations and crop coefficients for maize under arid climatic conditions
.
Agricultural Water Management
192
,
1
11
.
https://doi.org/10.1016/j.agwat.2017.06.019
.
Jia
X.
,
Steele
D. D.
&
Hopkins
D.
2008
Hourly reference evapotranspiration estimates for alfalfa in North Dakota
. In:
World Environmental and Water Resources Congress 2008
(Babcock, R. W. & Walton, R., eds), ASCE, Reston, VA, USA
2008
,
1
10
.
https://doi.org/10.1061/40976(316)89
.
Jiang
L.
,
Islam
S.
,
Guo
W.
,
Jutla
A. S.
,
Senarath
S. U. S.
,
Ramsay
B. H.
&
Eltahir
E.
2009
A satellite-based Daily Actual Evapotranspiration estimation algorithm over South Florida
.
Global and Planetary Change
67
,
62
77
.
Jiang
S.
,
Liang
C.
,
Cui
N.
,
Zhao
L.
,
Du
T.
,
Hu
X.
,
Feng
Y.
,
Guan
J.
&
Feng
Y.
2019
Impacts of climatic variables on reference evapotranspiration during growing season in Southwest China
.
Agricultural Water Management
216
,
365
378
.
https://doi.org/10.1016/j.agwat.2019.02.014
.
Katul
G. G.
,
Cuenca
R. H.
,
Grebet
P.
,
Wright
J. L.
&
Pruitt
W. O.
1992
Analysis of evaporative flux data for various climates
.
Journal of Irrigation and Drainage Engineering
118
,
601
618
.
Kejna
M.
,
Uscka-Kowalkowska
J.
&
Kejna
P.
2021
The influence of cloudiness and atmospheric circulation on radiation balance and its components
.
Theoretical and Applied Climatology
144
(
3–4
),
823
838
.
https://doi.org/10.1007/s00704-021-03570-8
.
Lindsey
S. D.
&
Farnsworth
R. K.
1997
Sources of solar radiation estimates and their effect on daily potential evaporation for use in streamflow modeling
.
Journal of Hydrology
201
,
348
366
.
https://doi.org/10.1016/S0022-1694(97)00046-2
.
Lu
N.
,
Chen
S.
,
Wilske
B.
,
Sun
G.
&
Chen
J.
2011
Evapotranspiration and soil water relationships in a range of disturbed and undisturbed ecosystems in the semi-arid Inner Mongolia, China
.
Journal of Plant Ecology
4
(
1–2
),
49
60
.
https://doi.org/10.1093/jpe/rtq035
.
Maestre-Valero
J. F.
,
Testi
L.
,
Jiménez-Bello
M. A.
,
Castel
J. R.
&
Intrigliolo
D. S.
2017
Evapotranspiration and carbon exchange in a citrus orchard using eddy covariance
.
Irrigation Science
35
,
397
408
.
Meyer
S. J.
,
Hubbard
K. G.
&
Wilhite
D. A.
1989
Estimating potential evapotranspiration: the effect of random and systematic errors
Agricultural and Forest Meteorology
46 (4), 285–296. https://doi.org/10.1016/0168-1923(89)90032-4
.
Monchuk
D.
,
Deininger
K.
&
Nagarajan
H.
2010
Does land fragmentation reduce efficiency: micro evidence from India
. In:
Paper Prepared for Presentation at the Agricultural & Applied Economics Association 2010 AAEA, CAES, & WAEA Joint Annual Meeting
,
25–27 July, Denver, CO, USA
.
Nair
V. S.
,
Moorthy, K. K., Alappattu, D. P., Kunhikrishnan, P. K., George, S., Nair, P. R., Babu, S. S., Abish, B., Satheesh, S. K., Tripathi, S. N., Niranjan, K., Madhavan, B. L., Srikant, V., Dutt, C. B. S., Badarinath, K. V. S. & Reddy, R. R.
2007
Wintertime aerosol characteristics over the Indo-Gangetic Plain (IGP): impacts of local boundary layer processes and long-range transport
.
Journal of Geophysical Research: Atmospheres
112
,
D13205
.
doi:10.1029/2006JD008099
.
Ndiaye
P. M.
,
Bodian
A.
,
Diop
L.
,
Deme
A.
,
Dezetter
A.
,
Djaman
K.
&
Ogilvie
A.
2020
Trend and sensitivity analysis of reference evapotranspiration in the Senegal River basin using NASA meteorological data
.
Water
12
(
7
),
1957
.
Ortega-Farias
S. O.
,
Cuenca
R. H.
&
English
M.
1995
Hourly grass evapotranspiration in modified maritime environment
.
Journal of Irrigation and Drainage Engineering
121
,
369
373
.
Panwar
A. S.
,
Shamim
M.
,
Babu
S.
,
Ravishankar
N.
,
Prusty
A. K.
,
Alam
N. M.
,
Singh, D. K., Bindhu, J. S., Kaur, J., Dashora, L. N., Latheef Pasha, M. D., Chaterjee, S., Sanjay, M. T. & Desai, L. J.
2019
Enhancement in productivity, nutrients use efficiency, and economics of rice–wheat cropping systems in India through farmer's participatory approach
.
Sustainability
11
,
122
.
doi:10.3390/su11010122
.
Perera
K. C.
,
Western
A. W.
,
Nawarathna
B.
&
George
B.
2015
Comparison of hourly and daily reference crop evapotranspiration equations across seasons and climate zones in Australia
.
Agricultural Water Management
148
,
84
96
.
https://doi.org/10.1016/j.agwat.2014.09.016
.
Poddar
A.
,
Gupta
P.
,
Kumar
N.
,
Shankar
V.
&
Ojha
C. S. P.
2021
Evaluation of reference evapotranspiration methods and sensitivity analysis of climatic parameters for sub-humid sub-tropical locations in western Himalayas (India)
.
ISH Journal of Hydraulic Engineering
27
(
3
),
336
346
.
https://doi.org/10.1080/09715010.2018.1551731
.
Rahman
M. A.
,
Kang
S. C.
,
Nagabhatla
N.
&
Macnee
R.
2017
Impacts of temperature and rainfall variation on rice productivity in major ecosystems of Bangladesh
.
Agriculture and Food Security
6
(
1
),
10
.
https://doi.org/10.1186/s40066-017-0089-5
.
Ritchie
J. T.
,
Howell
T. A.
,
Meyer
W. S.
&
Wright
J. L.
1996
Sources of biased errors in evaluating evapotranspiration equations
. In:
Evapotranspiration and Irrigation Scheduling: Proceedings of the International Conference, November 3–6, 1996, San Antonio Convention Center, San Antonio, Texas
(Camp, C. R., Sadler, E. J. & Yoder, R. E., eds), American Society of Agricultural Engineers, St Joseph, MI, USA, pp. 147–157
.
Sandhu
J. S.
,
Bhatt
B. P.
&
Mishra
J. S.
2016
Production and Technological Gaps in Middle Indo-Gangetic Plains
.
ICAR Research Complex for Eastern Region
,
Patna, Bihar, India
.
Sharma
M. L.
1985
Estimating evapotranspiration
.
Advances in Irrigation
3
,
213
281
.
Snyder
K. A.
,
Richards
J. H.
&
Donovan
L. A.
2003
Night-time conductance in C3 and C4 species: do plants lose water at night?
Journal of Experimental Botany
54
(
383
),
861
865
.
Suleiman
A. A.
&
Hoogenboom
G.
2009
A comparison of ASCE and FAO-56 reference evapotranspiration for a 15-min time step in humid climate conditions
.
Journal of Hydrology
375
,
326
333
.
https://doi.org/10.1016/j.jhydrol.2009.06.020
.
Sun
L.
&
Wu
G.
2001
Influence of land evapotranspiration on climate variations
.
Science in China Series D: Earth Sciences
44
,
838
846
.
Tamoffo
A. T.
,
Weber
T.
,
Akinsanola
A. A.
&
Vondou
D. A.
2023
Projected changes in extreme rainfall and temperature events and possible implications for Cameroon's socio-economic sectors
.
Meteorological Applications
30
(
2
),
e2119
.
https://doi.org/10.1002/met.2119
.
Tolk
J. A.
,
Howell
T. A.
&
Evett
S. R.
2006
Nighttime evapotranspiration from alfalfa and cotton in a semiarid climate
.
Agronomy Journal
98
,
730
736
.
Treder
W.
&
Klamkowski
K.
2017
An hourly reference evapotranspiration model as a tool for estimating plant water requirements
.
Infrastruktura i Ekologia Terenów Wiejskich (Infrastructure and Ecology of Rural Areas)
.
2008 II
(
1
),
469
481
.
Trnka
M.
,
Eitzinger
J.
,
Kapler
P.
,
Dubrovský
M.
,
Semerádová
D.
,
Žalud
Z. Ě.
&
Formayer
H.
2007
Effect of estimated daily global solar radiation data on the results of crop growth models
.
Sensors
7
(
10
),
2330
2362
.
Vogel
E.
,
Donat
M. G.
,
Alexander
L. V.
,
Meinshausen
M.
,
Ray
D. K.
,
Karoly
D.
,
Meinshausen
N.
&
Frieler
K.
2019
The effects of climate extremes on global agricultural yields
.
Environmental Research Letters
14
(
5
),
054010
.
http://dx.doi.org/10.1088/1748-9326/ab154b
.
Walter
I. A.
,
Allen
R. G.
,
Elliott
R.
,
Jensen
M. E.
,
Itenfisu
D.
,
Mecham
B.
,
Howell
T. A.
,
Snyder
R.
,
Brown
P.
,
Echings
S.
,
Spofford
T.
, Hattendorf, M., Cuenca, R. H., Wright, J. L. & Martin, D.
2000
ASCE's standardized reference evapotranspiration equation
. In:
Watershed Management and Operations Management
2000 (Flug, M., Frevert, D. & Watkins, D. W., eds), ASCE, Reston, VA, USA. doi:10.1061/40499(2000)126
.
Wang
W.
,
Shao
Q.
,
Peng
S.
,
Xing
W.
,
Yang
T.
,
Luo
Y.
,
Yong
B.
&
Xu
J.
2012
Reference evapotranspiration change and the causes across the Yellow River Basin during 1957–2008 and their spatial and seasonal differences
.
Water Resources Research
48
(
5
),
W05530
.
https://doi.org/10.1029/2011WR010724
.
Xing
X.
,
Liu
Y.
,
Zhao
W.
,
Kang
D.
,
Yu
M.
&
Ma
X.
2016
Determination of dominant weather parameters on reference evapotranspiration by path analysis theory
.
Computers and Electronics in Agriculture
120
,
10
16
.
https://doi.org/10.1016/j.compag.2015.11.001
.
Yonaba
R.
,
Tazen
F.
,
Cissé
M.
,
Mounirou
L. A.
,
Belemtougri
A.
,
Ouedraogo
V. A.
,
Koïta
M.
,
Niang
D.
,
Karambiri
H.
&
Yacouba
H.
2023
Trends, sensitivity and estimation of daily reference evapotranspiration ET0 using limited climate data: regional focus on Burkina Faso in the West African Sahel
.
Theoretical and Applied Climatology
153
(
1–2
),
947
974
.
https://doi.org/10.1007/s00704-023-04507-z
.
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