Introduction

Climate change, resulting from natural processes and anthropogenic forces, is negatively affecting the water resources (hydrology), crop water requirements, and therefore the agricultural production globally (Zhang et al. 2009; IPCC 2014). The extreme events such as floods and droughts are the example of negative impacts of climate change (IPCC 2014; Surendran et al. 2014; Akinsanola and Zhou 2019; Gbode et al. 2019). The continuous change in climate scenarios is resulting in increased temperature, particularly the minimum temperature (Singh 2016). The increase in average global temperature may significantly increase the evaporation and land-surface drying (IPCC 2014), subsequently increasing the probability of drought occurrence (Dai et al. 2004). FAO (2001) has reported about 15–35% reduction of crop yields in Africa and West Asia, with increase in mean temperature from 2.0 to 4.0 °C, whereas about 25–35% reduction in the Middle East. Thus, a continuous monitoring and trend analysis of climatic parameters such as temperature and evapotranspiration (ET) with change point detection becomes significant (Vincent et al. 2015) for better management of water resources. Trend analysis of hydrological and climatic variables is frequently carried out to quantify the effect of climate change on future agricultural production (Jain et al. 2013; Suryavanshi et al. 2014; Kishore et al. 2016; Malik et al. 2020; Saadi et al. 2019).

For carrying out trend analysis of time-series data and change point detection, non-parametric statistical approaches can be used, to investigate whether there exists a trend in a long-term dataset or it follows any distribution at a fixed significance level. The change detection test of time-series data is done for reduction in uncertainty in climate information (Jaiswal and Lohani 2015). The non-parametric tests such as Mann–Kendall trend test (Mann 1945; Kendall 1975), Sen’s slope test (Sen 1968), SNHT (Alexandersson 1986; Gonzalez-Rouco et al. 2001; Stepanek et al. 2009), Pettitt’s test (Pettitt 1979; Mauget 2003), and Buishand’s range test (Buishand 1982) are widely used for detection of trend and change-point in the time-series parameters such as temperature, humidity, rainfall, sunshine hours, wind speed, and ET (Salarijazi et al. 2012; Emmanuel et al. 2019; Ajayi and Ilori 2020). The recent studies involving trend analysis and change-point detection in long-term time series data using Mann Kendall’s test include Malik et al. (2019), Bannayan et al. (2020), Elzopy et al. (2020), Ilori and Ajayi (2020), and Sharma et al. (2020) for temperature and rainfall, Sharma et al. (2020) for relative humidity and solar radiation, and Mohsin and Lone (2021), Ndiaye et al. (2020), and Sharma et al. (2020) for reference evapotranspiration (ETo).

Any significant change in evapotranspiration (ETo or ETc) in relation to different meteorological parameters, mainly the temperature (Tmax and Tmin) and rainfall (Sharafi and Mir Karim 2020), is bound to have a significant impact on agricultural water management, crop growth, and the productivity. ET from agricultural fields (Penman 1948), which represents the water loss through evaporation from soil surface and transpiration from plant leaves (Chattopadhyay and Hulme 1997), significantly affects the crop productivity. On the basis of previous studies, it may be concluded that ET increases with increase in global temperature. However, numerous studies have reported decreasing trend of ET in some of the regions. In this context, Chattopadhyay and Hulme (1997) have reported decreased ETo with increased temperature in India, mainly due to increase in relative humidity (RH) and reduction in solar radiation. Moreover, Bandyopadhyay et al. (2009) have admitted a declining trend of ETo throughout India. ET is affected by several climatic variables, including temperature and rainfall distribution. Increasing temperature and decreasing rainfall may significantly enhance the ET (ETo and actual or crop ET, i.e., ETc) and reduce the yields of various crops (Lobell et al. 2008). Thus, precise estimation of ETo, followed by computation ETc, can play a great role in management of available water resources (Zhang, et al. 2015), crop planning (Shuttleworth and Wallace 2009), and therefore the agricultural water, particularly in the water scarce regions globally. Several methods (empirical, water balance-based, and physical approaches) are available for estimating ETo, which require temperature (max. and min.), relative humidity (max. and min.), sunshine hours, and wind velocity as inputs (Peterson et al. 1995; Irmak et al. 2012; Sun et al. 2016). Any significant change (decrease or increase) in these climatic parameters is likely to have a significant change (decrease or increase) in ETo. FAO-ETo calculator is one of the tools for accurate estimation of ETo, using the above listed climatic parameters as input.

Previously, Hundal and Kaur (2002a) have declared a steady increase of about of 0.07 °C per year in the minimum air temperature in the present studied region over of period of 30 years (between 1970 and 2002). Hundal et al. (1997) reported an increasing rainfall trend over normal for both annual and kharif season for the past 30 years at Ludhiana. Further, Gill et al. (2010) reported rainfall below normal for 24 years for Ludhiana being highest (1334 mm) during 1988 and lowest (379.6 mm) during 1974. Furthermore, Hundal and Kaur (2002b) have recorded about 150 mm increment in rainfall over a period of 30 years for the same region. Furthermore, the average decadal minimum and maximum temperatures are expected to increase by 29.1 and 12.8%, respectively, by the end of the twenty-first century in the region (Singh 2016), with a significant reduction (13.2%) in average decadal rainfall (Singh 2016).

At present, more than 85% area in the study region is under agriculture with net irrigated area of about 98% and having a cropping intensity of more than 190%. Out of the total area under irrigation, about 72.50% area is irrigated with groundwater (> 14 lakh tube wells in operation), whereas only 27.50% area is irrigated with surface water supplied through canals (Singh 2019). Due to the more reliance on groundwater, followed by its over-exploitation, the depth to water table in the region falls in the range of 20–40 mbgl (Singh 2019). Thus, the injudicious surface irrigation water policies and excessive ground water pumping are the key reasons for acute depletion of the groundwater resources in the region. Furthermore, the rice–wheat crop rotation in relation to uncontrolled water flooding has encouraged the water table depletion (about 70 cm/year) during few couple of decades (Gulati et al. 2017). Besides, the average annual rainfall in the region is decreasing and erratic in nature, which fails to contribute significantly to the crop water requirement. Thus, the water management particularly for major field crops of the region is highly needed in relation to irrigation scheduling and saving of water to be applied. This can be achieved by various techniques, one of which is the study of crop evapotranspiration, which is taken equivalent to crop water requirement. The trend analysis of ETo may help in better understanding of the crop water requirements in relation to climate change impacts (Dinpashoh and Babamiri 2020).

Keeping the this information in observance, the present study was undertaken to (1) estimate ETo using FAO-ETo calculator; (2) study and detect trend in long-term (1970–2019) recorded temperature (minimum and maximum), rainfall and estimated ETo using Mann–Kendall’s trend test, Sen’s slope test, standard normal homogeneity test (SNHT), and Pettitt’s test; (3) study correlation of ETo with Tmin, Tmax, and rainfall using correlation test in XLSTAT software; and (4) develop regression models for easy prediction of ETo on seasonal as well as annual basis for the present study region.

Materials and methods

Description of study area

The present investigation was carried out in the Department of Soil and Water Engineering, Punjab Agricultural University (PAU), Ludhiana. The study site is located between 30° 54′ N (latitude) and 75° 48′ E (longitude) at an elevation of 247.0 m above the mean sea level. Figure 1 demonstrates the study area map. The study region is characterized as semi-arid with sub-tropical climatic conditions, resulting in very hot summer (April to June) and cold winters (December to January). The mean temperatures (max. and min.) indicate variations throughout the year. The temperature during summer exceeds 38 °C, even touches 47 °C. During winter (December and January), frost is experienced, and the minimum temperature drops below 4.0 °C. North-Eastern winds dominate in the region during this period. The mean annual rainfall of the study region is 680 mm, and about 75–80% of it is received in the months of June to September. In winter, only a few showers of rains (cyclonic) are experienced through western disturbances. There are mainly four different seasons in the study region, viz., spring, March–May (pleasant); summer, June–August (warm); autumn, September–October (mild cold); and winter, November–February (extreme cold).

Fig. 1
figure 1

Study area map

Data collection

The daily climatic data for 50 years (1970–2019) was obtained from the meteorological observatory of Punjab Agricultural University (PAU), Ludhiana. The climatic data included temperature (minimum and maximum), relative humidity (minimum and maximum), wind speed, sunshine hours, and rainfall.

Methodology for trend analysis

Trend is a significant change (either positive or negative) in a random variable with respect to time, which can be measured using statistical tests (parametric or non-parametric). FAO-ETo calculator was used for estimation of daily reference evapotranspiration (ETo). Trend analysis (trend and change-point detection) was carried out for estimated daily ETo, temperature (minimum and maximum), and rainfall using non-parametric tests, viz., Mann–Kendall’s trend test (Kendall 1975), Sen’s slope test (Sen 1968), SNHT test (Alexandersson 1986), and Pettitt’s test (Pettitt 1979). The estimated ETo and recorded data was transformed to monthly basis. The resulting data then divided into four seasons, viz., spring (March–May), summer (June–August), autumn (September–November), and winter (December–February). The analysis was carried out on seasonal as well as annual basis using XLSTAT software. The estimated daily ETo was also converted to monthly and then seasonal basis. Correlation test was also performed for testing the relationship between estimated ETo, temperature (Tmax and Tmin), and rainfall.

Mann–Kendall test

The Mann–Kendall (Mann 1945; Kendall 1948) test is one of the most commonly used non-parametric tests for detection of trends in long-term hydro-meteorological time-series data of climate (Bandyopadhyay et al. 2009; Liang et al. 2010; Tabari et al. 2011; Azizzadeh and Javan 2015; Rahmani et al. 2015; Diop et al. 2018; Bodian et al. 2020), as it does not necessitate the data to follow any of the statistical distributions (Diop et al. 2015). Moreover, it is not sensitive to the extreme values (Shadmani et al. 2012). The test interpretation criteria is based on rejection or acceptance of two hypotheses, viz., null hypothesis (Ho), i.e., there is no trend in the series, and the alternate hypothesis (Ha), i.e., reject Ho, indicating existence of trend in the time series data. If p value is less than alpha (α), i.e., 0.05, one should accept Ha, which indicates existence of a trend in the time-series data (hydrological or climatic data). However, if the p value is more than α, one cannot reject Ho, which indicates that there exists no trend in the data series.

The formula for Mann–Kendall’s statistical S is expressed by Eq. 1. The mean of S is 0. The downward or upward trend is indicated by the sign of Z value (negative or positive), which can be obtained using the variance of S, as given below (Eq. 3). For n > 10, Z follows nearly a normal distribution and can be computed using Eq. 4(Hirsch and Slack 1984) as reported in Ndiaye et al. (2020).

$$S=\sum_{j=1}^{j=n-1}\sum_{i=j+1}^{i=n}sign ({x}_{i}-{x}_{j})$$
(1)

where xi = value of the variable at time i, xj = value of the variable at time j, n = length of the series, and sign () = a function as described below as expressed by Eq. 2.

$$sign \left({x}_{i}-{x}_{j}\right)=\left\{\begin{array}{c}1 if \left({x}_{i}-{x}_{j}\right)>0\\ o if \left({x}_{i}-{x}_{j}\right)=0\\ -1 if \left({x}_{i}-{x}_{j}\right)<0\end{array}\right.$$
(2)

The variance (\({\sigma }^{2}\)) can be expressed as reported in Pohlert (2020):

$$Var \left(S\right)={\sigma }^{2}=\frac{\left\{n(n-1)(2n+5)-\sum_{j=1}^{{p}^{*}}{t}_{j}({t}_{j}-1)(2{t}_{j}+5)\right\}}{18}$$
(3)

where p* = number of the tied groups in the dataset and tj = number of data points in jth tied group. The statistic S is distributed normally providing that Z-transformation is employed as given below:

$$Z=\left\{\begin{array}{c}\frac{S-1}{\sqrt{var\left(S\right)}} or \frac{S-1}{\sigma }, if S>0\\ 0 if S=0\\ \frac{S+1}{\sqrt{var\left(S\right)}}or \frac{S+1}{\sigma }, if S<0\end{array}\right.$$
(4)

\(\mathrm{where}\sigma =SD=\sqrt{\frac{\left\{n(n-1)(2n+5)-\sum_{j=1}^{{p}^{*}}{t}_{j}({t}_{j}-1)(2{t}_{j}+5)\right\}}{18}}\) 5).

The positive and negative Z values indicate increasing and decreasing trends, respectively. The critical values of Z are \(\pm 1.96\) at 5% level of significance. For |Z|> 1.96 at 5% level of significance, the null hypothesis can be rejected, and a trend can be recorded. In the present study, the hypothesis was tested at 5% level of significance (i.e., α = 0.05).

Kendall’s tau (\(\tau\)) is closely related to the statistic S as expressed in Pohlert (2020):

$$\tau =\frac{S}{\sqrt{\frac{n(n-1)}{2}}\times \sqrt{\frac{n\left(n-1\right)}{2}-\frac{\sum_{j=1}^{p}{t}_{j}({t}_{j}-1)}{2}}}$$
(6)

Sens’s slope estimator

Mann-Kendal test has a limitation that it only confirms the existence of a significant trend if any for a given level of significance, Thus, a non-parametric procedure developed by Theil (1950) and Sen (1968), known as Sen’s slope estimator (β), was used to calculate the magnitude of the trend (Eq. 7). Once the trend is detected in the time-series data, its magnitude or amplitude can also be determined by slope of the trend. The negative and positive β value indicates downward and upward trend, respectively. For a linear trend in the given time series data, β for n data pairs can be computed as

$$\beta =\mathrm{Median}\left(\frac{{x}_{i}-{x}_{j}}{i-j}\right)\forall i<j(1\le i<j\le n)$$
(7)

when n is even, median can be computed as

$$\mathrm{Median}={\beta }_{\frac{n+1}{2}}$$
(7a)

when n is odd, median can be computed as

$$\mathrm{Median}=\frac{1}{2}\left({\beta }_\frac{n}{2}+{\beta }_{\frac{n}{2}+1}\right)$$
(7b)

Change-point detection in time series data

Change-point detection in long-term time series data is important to examine the time period for a significant change. In the present case, standard normal homogeneity test (SNHT) and Pettitt’s test (Gallagher et al. 2012; Jaiswal and Lohani 2015) were applied using Monte Carlo method to check the homogeneity of data or to detect the change-point (Vezzoli et al. 2012), whether the time series data is homogeneous or not (when temporal changes or breaks are there). These two tests do not require any assumption related to the distribution of temperature (minimum and maximum), ETo, and rainfall data. The test interpretation criteria were based on two hypotheses, viz., null hypothesis (Ho), i.e., data are homogeneous, and alternate hypothesis (Ha), i.e., there exists a date at which there is a change in data.

Standard normal homogeneity test (SNHT)

Standard normal homogeneity (SNHT), a non-parametric test developed by Alexandersson (1986), was further improved (Alexandersson and Moberg 1997) for detecting a change in a time series data. Test statistic (Tk) can be utilized to compare the mean of first n observations, with the remaining mean of n − k observations having n number of data points (Stepanek et al. 2009; Vezzoli et al. 2012).

$${T}_{k}={kZ}_{a}^{2}+\left(n-k\right){Z}_{{b}^{\bullet }}^{2}$$
(8)

where,

$${Z}_{a}={k}^{-1}\sum_{i=1}^{k}\frac{{x}_{i}-\overline{x}}{{\sigma }_{x}}$$
(9)
$${Z}_{b}={\left(n-k\right)}^{-1}\sum_{i=k+1}^{k}\frac{{x}_{i}-\overline{x}}{{\sigma }_{x}}$$
(10)

where \(\overline{x }\) = mean, σx = standard deviation, and k = change point containing a break, at which the Tk value touches its maximum. For rejecting the Ho, the critical value must be smaller than a test statistic, which is further dependent on number of observations (n). The p value is calculated using Monte Carlo simulations.

Pettitt’s test

Pettitt’s test was developed by Pettitt (1979) and can be advantageous in detecting any single change in hydrological or climate series with continuous data (Mu et al. 2007; Gao et al. 2011). It is also a non-parametric test and used without considering any assumption related to distribution of the time-series data. It is widely adopted for change-point detection in time series data, due to its sensitivity to changes or breaks (Winingaard et al. 2003). Different authors (Kang and Yusof 2012; Ilori and Ajayi 2020) have applied the test statistics used in Pettitt's test. If t be the change point time in an observed data series of x1, x2, x3, … xn, such that the first distribution function (G1(x)) for the first part of the data series, i.e., x1, x2, x3, … xt, is different from the second distribution function (G2(x)) for the second part of the data series, i.e., xt+1, xt+2, xt+3, … xt+n. According to this test, the variables either follow at least one distribution having no change for same location (Ho) or do not follow any distributions, having change in data series (Ha). The non-parametric function test statistics (Ut) is expressed as reported in Ilori and Ajayi (2020):

$${U}_{t}=\sum_{i=1}^{t}\sum_{j=t+1}^{n}sign ({x}_{t}-{x}_{j})$$
(11)
$$sign \left({x}_{t}-{x}_{j}\right)=\left\{\begin{array}{c}1 if \left({x}_{i}-{x}_{j}\right)>0\\ o if \left({x}_{i}-{x}_{j}\right)=0\\ -1 if \left({x}_{i}-{x}_{j}\right)<0\end{array}\right.$$
(12)

If the length of the sample and confidence interval be n and ρ, respectively, the test statistics K can be described as indicated by Eq. 13.

$$K=Max\left|{U}_{t}\right|$$
(13)

If the change-point of the time-series data is located at K providing that the statistic is significant, p value can be estimated as

$$p\cong 2\times exp\left(\frac{-6{K}^{2}}{{n}^{2}+{n}^{3}}\right)$$
(14)

At change-point, the entire data series is separated into two sub-series. The probability at a change point (\({p}_{cp}\)) can be defined by Eq. 15.

$${p}_{cp}=1-p$$
(15)

Modeling of ETo

Linear regression technique (in XLSTAT software) was used to formulate models for predicting ETo on seasonal as well as annual basis in the present study region. The ETo data for first 30 years (1970–1999) were utilized for developing the regression models, and the data from the next 20 years (2000–2019) were used for validating the developed models. The followings models were developed:

$$\begin{array}{c}{ET}_{o}\left(Spring\right)=-0.35736+0.11549\times {T}_{max}-0.00884\times {T}_{min}-0.00849\times {RH}_{max}-0.01249\times {RH}_{min}+\\ 1.02396\times {v}_{w}+0.16160\times SSH\end{array}$$
(16)
$$\begin{array}{c}{ET}_{o}\left(Summer\right)=-1.52235+0.13108\times {T}_{max}+0.03936\times {T}_{min}-0.01611\times {RH}_{max}-0.00643\times \\ {RH}_{min}+0.64846\times {v}_{w}+0.25178\times SSH\end{array}$$
(17)
$$\begin{array}{c}{ET}_{o}\left(Autumn\right)=-0.64190+0.06707\times {T}_{max}+0.01361\times {T}_{min}-0.00752\times {RH}_{max}+0.00303\times \\ {RH}_{min}+0.94177\times {v}_{w}+0.15548\times SSH\end{array}$$
(18)
$$\begin{array}{c}{ET}_{o}\left(Winter\right)=1.37131+0.05079\times {T}_{max}+0.01057\times {T}_{min}-0.00575\times {RH}_{max}-0.01210\times {RH}_{min}+\\ 0.40747\times {v}_{w}+0.01372\times SSH\end{array}$$
(19)
$$\begin{array}{c}{ET}_{o}\left(Annual\right)=-0.95870+0.08887\times {T}_{max}+0.02275\times {T}_{min}-0.00922\times {RH}_{max}+0.00039\times \\ {RH}_{min}+0.87735\times {v}_{w}+0.18867\times SSH\end{array}$$
(20)

where Tmax = maximum temperature (°C), Tmin = minimum temperature (°C), RHmax = maximum relative humidity (%), RHmin = minimum relative humidity (%), vw = wind speed (m/s), and SSH = sunshine hours.

Statistical analysis

The statistical analysis involved computation of mean, median, standard deviation (σ), variance (σ2), mean bias error (MBE), mean absolute error (MAE), root mean square error (RMSE), and Willmott index of agreement (d). MAE, RMSE, coefficient of determination (r2), σ, and d values were used in testing the performance of developed ETo models.

Mean bias error (MBE)

$$\mathrm{MBE }=\frac{1}{n}{\sum }_{i=1}^{n}\left({P}_{i}-{O}_{i}\right)$$
(21)

Mean absolute error (MAE)

$$\mathrm{MAE }=\frac{1}{\mathrm{n}}{\sum }_{\mathrm{i}=1}^{\mathrm{n}}\left|{\mathrm{P}}_{\mathrm{i}}-{\mathrm{O}}_{\mathrm{i}}\right|$$
(22)

Root mean square error (RMSE)

$$\mathrm{RMSE }=\sqrt{\frac{1}{\mathrm{n}}{\sum }_{\mathrm{i}=1}^{\mathrm{n}}{({\mathrm{P}}_{\mathrm{i}}-{\mathrm{O}}_{\mathrm{i}})}^{2}}$$
(23)

Standard deviation (SD)

$$\mathrm{SD}=\sqrt{{\mathrm{RMSE}}^{2}-{\mathrm{MBE}}^{2}}$$
(24)

Index of agreement (d)

$$\mathrm{d }=1-\left(\frac{\sum_{\mathrm{i}=1}^{\mathrm{n}}{\left({\mathrm{P}}_{\mathrm{i}}-{\mathrm{O}}_{\mathrm{i}}\right)}^{2}}{\sum_{\mathrm{i}=1}^{\mathrm{n}}{\left(\left|{\mathrm{P}}_{\mathrm{i}}-\overline{\mathrm{O} }\right|+\left|{\mathrm{O}}_{\mathrm{i}}-\overline{\mathrm{O} }\right|\right)}^{2}}\right), \left[0\le \mathrm{d}\le 1\right]$$
(25)

where n = number of data points, Pi = predicted or estimated data, and Oi = observed or standard data.

Results and discussion

Mann–Kendall’s trend analysis

The long-term minimum temperature (Tmin) was recorded to be in the range of 15.0–19.8 °C, 23.3–27.5 °C, 14.1–18.8 °C, and 4.5–8.5 °C for spring, summer, autumn, and winter seasons, respectively, whereas on annual basis, it was recorded as 14.8–18.5 °C. For Tmin, the Kendall’s tau (\(\tau\)) value was recorded to be positive for all the four seasons, as well as on annual basis and varied from 0.468 (winter) to 0.531 (summer), being 0.631 on annual basis (Table 1). There existed a significant trend (increasing) in long-term Tmin data during all the four seasons (spring, summer, autumn, and winter), as well as on annual basis (p < 0.05 (α) in each case) for 5% level of significance. Earlier, Grover and Upadhaya (2014) have reported a significant increase (1.4–2.1 °C) in Tmin during kharif season in the present study region. Kaur et al. (2016) have also reported an increasing trend in Tmin from year 1970 to 1990. Further, Kingra (2018) has confirmed the increasing trend in long-term Tmin in the same region for a period from 1970 to 2014. However, this increasing trend in Tmin with time, particularly during the months of February and March, may significantly reduce the yield of wheat crop grown in the region as these two months correspond to grain filling in wheat crop (Kaur et al. 2012). The long-term maximum temperature (Tmax) was recorded to be in the range of 29.5–36.6 °C, 33.6–37.3 °C, 28.7–31.9 °C, and 18.2–22.0 °C during spring, summer, autumn, and winter seasons, respectively, with the annual Tmax as 28.2–30.7 °C, being lowest and highest during winter and summer seasons, respectively. For Tmax, the \(\tau\) value was recorded to be positive for spring and on annual basis, whereas negative for rest of the three seasons (summer, autumn, and winter). The \(\tau\) value was recorded to be 0.111, − 0.078, − 0.145, − 0.117, and 0.010 for spring, summer, autumn, winter, and annual basis, respectively. No definite trend was recorded in the long-term data of Tmax for all the four respective seasons, as well as on annual basis (Table 1). Similar observation related to trend in long-term Tmax has been reported by Kingra (2018). The average temperature (Tmin and Tmax) was recorded to be highest during summer followed by spring, autumn, and winter (least).

Table 1 Parameters of Mann–Kendall’s trend analysis test

The rainfall during spring, summer, autumn, and winter seasons was recorded to be in the range of 9.7–191.7 mm, 97.6–822.8 mm, 6.7–668.6 mm, and 2.0–202.5 mm, respectively, whereas on annual basis, it varied as 379.6–1334 mm with average value of 747.4 mm. The average seasonal rainfall during study period was recorded to be highest during summer (485.9 mm) followed by autumn (123.3 mm) and least during spring (63.7 mm). The \(\tau\) values for rainfall were recorded to be positive for all seasons, except during summer (negative). The \(\tau\) value was recorded to be 0.071, − 0.019, 0.138, 0.043, and 0.031 for spring, summer, autumn, winter, and annual basis, respectively. No trend (insignificant) was recorded in the long-term rainfall data for all the four respective seasons, as well as on annual basis (Table 1). Similar observation related to rainfall has been made by Kashyap and Agarwal (2020). A significant trend (decreasing) was recorded in long-term ETo during all the four seasons (spring, summer, autumn, and winter), as well as on annual basis (p < 0.05 (α) in each case) for 5% level of significance. Similar observation related to ETo has been reported in Kashyap and Agarwal (2020). ETo was estimated to be in the range of 4.69–6.01 mm/day, 4.70–6.43 mm/day, 2.74–3.66 mm/day, and 1.49–2.27 mm/day during spring, summer, autumn, and winter seasons, respectively, whereas it varied in the range of 3.57–4.39 mm/day on annual basis, being lowest and highest during winter and spring seasons, respectively. Similar range of annual ETo (3.52–4.27 mm/day) has been reported by Kingra (2018) for the same region for a study period from 1970 to 2014. Thus, decreasing ETo, particularly in relation to increasing Tmin, confirms the presence of an evaporation paradox in the study area. The declining ETo may result in decreased crop water requirements. Kashyap and Agarwal (2020) have reported increasing trend in crop yields (rice and wheat) for the present study region with decrease in ETo. In case of ETo, the value of \(\tau\) was computed to be negative for all the four seasons as well as on annual basis. The \(\tau\) value varied from − 0.663 (for autumn) to − 0.313 (for spring), whereas it was computed to be − 0.609 on annual basis. The average ETo was recorded to be highest during spring (5.44 mm/day) followed by summer (5.44 mm/day), autumn (3.66 mm/day), and winter (1.79 mm/day). On annual basis, the average ETo was computed as 3.98 mm/day. The estimated ETo was obtained in the order as follows: ETo (spring) ≥ ETo (summer) > ETo (autumn) > ETo (winter). Irrespective of the higher temperature during summer as compared to spring, the ETo during summer was slightly lower as compared to spring.

Sen’s slope trend analysis

From the results of Sen’s slope test, an upward (increasing) trend was recorded in Tmin data during all the four respective seasons as well as on annual basis. Similar trend in Tmin has been reported by Kaur et al. (2012) and Grover and Upadhaya (2014) for the same region. The Sen’s slope varied from 0.042 to 0.060, having lowest and highest values during summer and spring seasons, respectively (Table 2). On annual basis, the Sen’s slope was recorded as 0.050. The increasing trend in Tmin in the present study region (from 1970 to 2006) on annual basis has also been reported in Kaur et al. (2006). Further, similar trend in Tmin has been reported in Kaur et al. (2016). In case of Tmax, an upward (increasing) trend was recorded during spring season (Sen’s slope = 0.017) as well as on annual basis (Sen’s slope = 0.001) as also reported in Kaur et al. (2016), whereas during summer, autumn, and winter seasons, a downward trend was recorded. Thus, the trend in Tmax was mainly downward or decreasing (from 1970 to 2006) as reported by Kaur et al. (2006), except during spring season and on annual basis. Similar observation has also been made by Kaur et al. (2012). The Sen’s slope varied from − 0.010 to 0.017 (Table 2), having lowest and highest values during winter and spring seasons, respectively. On annual basis, the Sen’s slope was recorded as 0.001. In case of rainfall, an upward (increasing) trend was recorded during spring, autumn, winter, and on annual basis, whereas a downward (decreasing) trend during summer season. Kaur et al. (2016) have also reported an increasing trend in rainfall in the region from year 1970 to 1990. Further, Krishan et al. (2015) have reported an increasing trend in annual rainfall in this region (from year 1901 to 2002). Similar trend in long-term rainfall of the present study region (1970 to 2006) has been reported by Kaur et al. (2006). The Sen’s slope varied from − 0.297 to 0.830 (Table 2), having lowest and highest values during summer and autumn seasons, respectively. On annual basis, the Sen’s slope was recorded as 0.663. The estimated ETo data indicated a downward (decreasing) trend during all the four respective seasons as well as on annual basis. The Sen’s slope varied from − 0.0139 to − 0.0084, having lowest and highest values during autumn and spring seasons, respectively (Table 2). On annual basis, the Sen’s slope was recorded as − 0.0104. The Sen’s slope test indicated a downward trend in ETo with increase in Tmin during all the four respective seasons as well as on annual basis. Overall, the Sen’s slope analysis indicated increasing (upward) and decreasing (downward) trend in long-term Tmin and ETo, respectively, with time. ETo may also decrease with decrease in Tmax (during summer, autumn, and winter) and rainfall (during summer season). Unlike Tmin and ETo, the trend in Tmax and rainfall were recorded to be either increasing or decreasing, indicating no definite trend throughout the year. Similarly, Kaur et al. (2012) have reported no definite trend in Tmax, unlike Tmin. The Sen’s slope test confirms the results of Mann–Kendall’s test for Tmin and ETo.

Table 2 Sen’s slope values during different seasons as well as on annual basis

Homogeneity test for change-point detection in Tmin, Tmax, ETo, and rainfall data

In standard normal homogeneity test (SNHT) and Pettitt’s test, using Monte Carlo simulations (10,000) was applied at 99% confidence interval on the p value (two-tailed test). As per both SNHT and Pettitt’s tests, change-points were detected in both Tmin and ETo data during all four seasons, as well as on annual basis. The p value was recorded to be lower than α value (0.05) indicating existence of a date at which there is a change in Tmin and ETo data (Table 3), both seasonally and annually. Jaiswal et al. (2015) and Ilori and Ajay (2020) have also reported change points in long-term Tmin and Tmean, respectively, indicating the increasing trend with time. The mean Tmin values before and after change-point during spring, summer, autumn, winter, and on annual basis were recorded as 16.6 °C and 18.3 °C, 25.0 °C and 26.3 °C, 15.6 °C and 17.3 °C, 5.8 °C and 7.2 °C, and 15.7 °C and 17.1 °C, respectively (Fig. 2a–e). Figure 2 demonstrates the presence of change-point and trend in Tmin during four respective seasons as well as on annual basis. In case of Tmax, a change-point was detected only during spring season (Fig. 3a), having the mean Tmax values before and after change-point as 32.9 °C and 34.1 °C, respectively (Fig. 3a). Whereas during summer, autumn, winter, and on annual basis, the mean Tmax value was recorded as 35.2, 30.6, 19.9, and 29.8 °C, respectively (Fig. 3b–e), indicating homogeneity (absence of change-point) in data series. The rainfall data was observed to be homogeneous. The rainfall was recorded as 63.7, 485.9, 123.3, 76.8, and 747.4 mm during spring, summer, autumn, winter, and on annual basis, respectively (Fig. 4a–e). Figure 4 demonstrates the absence of change-point and trend in rainfall during four respective seasons as well as on annual basis. The rainfall and Tmax were observed to be homogeneous (i.e., no change-point). The parameters of change-point detection in time-series data are presented in Table 3. The mean ETo values before and after change-point during spring, summer, autumn, winter, and on annual basis were recorded as 5.68 mm/day and 5.36 mm/day, 5.66 mm/day and 5.23 mm/day, 3.39 mm/day and 3.03 mm/day, 1.89 mm/day and 1.66 mm/day, and 4.12 mm/day and 3.84 mm/day, respectively (Fig. 5a–e), indicating decline in ETo after the change-points. Figure 5 demonstrates the presence of change-point and trend in ETo during four respective seasons as well as on annual basis.

Table 3 Parameters of homogeneity analysis
Fig. 2
figure 2

Change-point detection in Tmin during (a) spring, (b) summer, (c) autumn, (d) winter, and (e) on annual basis

Fig. 3
figure 3

Change-point detection in Tmax during (a) spring, (b) summer, (c) autumn, (d) winter, and (e) on annual basis

Fig. 4
figure 4

Change-point detection in rainfall during (a) spring, (b) summer, (c) autumn, (d) winter, and (e) on annual basis

Fig. 5
figure 5

Change-point detection in ETo during (a) spring, (b) summer, (c) autumn, (d) winter, and (e) on annual basis

The SNHT recorded 1997, 1983, 1984, 1985, and 1984 as change-point years in Tmin during spring, summer, autumn, winter, and on annual basis, respectively, whereas the Pettitt’s test recorded the change-points in years 1997, 1989, 1996, 1988, and 1997, during four respective seasons and on annual basis. For spring season, the change-point (year 1997) in Tmin was recorded to be same as per both tests. For Tmax, both tests (SNHT and Pettitt’s) recorded change-points in 1998 and 1997, respectively, for spring season only. Separately, in Tmin and Tmax, the change-points were recorded to be different by both tests, except in one season (spring) for Tmin. However, for ETo which is jointly affected by Tmin and Tmax, the change-points during all the four seasons as well as on annual basis were recorded to be same. The change-points recorded by both tests were 1981, 1993, 1996, 1996, and 1993, for spring, summer, autumn, winter, and on annual basis, respectively. ETo performed as a better representative of climate change in relation to temperature variation (Tmin and Tmax).

The seasonal lowest Tmin value was recorded to be in the range of 4.5–23.3 °C (being lowest and highest for winter and summer seasons, respectively), with an average value of 14.8 °C. Similarly, the seasonal highest Tmin value was recorded to be in the range of 8.5–27.5 °C (being lowest and highest for winter and summer seasons, respectively), with an average value of 18.5 °C (Fig. 6a–e). Figure 6 demonstrates the different statistical parameters estimated for all the seasons as well as on annual basis. The first quartile (Q1) value for seasonal Tmin was recorded to be in the range of 6.0–25.5 °C, with an average value of 16.1 °C. Similarly, the third quartile (Q3) for seasonal Tmin was recorded to be in the range of 7.3–26.5 °C, with an average value of 17.3 °C. The median value for seasonal Tmin was recorded to be in the range of 6.9–26.1 °C, with an average value of 16.8 °C. Similarly, the mean seasonal Tmin was computed in the range of 6.7–26.0 °C, with a mean value of 16.7 °C. The trend in Tmin, Tmax, Q1, Q3, median, and mean was similar (being lowest and highest for winter and spring seasons, respectively, in each case). However, the trend was slightly different for variance (σn-12) and standard deviation (σn-1) values. σn-12 value varied from 1.0 to 1.3 (lowest and highest values for winter and spring seasons, respectively), with an average value of 0.8 (Fig. 6a–e). Similarly, σn-1 value varied from 1.0 to 1.2 °C (lowest and highest values for winter and spring seasons, respectively), with an average value of 0.9 °C.

Fig. 6
figure 6

Depiction of parameters of statistical analysis for Tmin during (a) spring, (b) summer, (c) autumn, (d) winter, and (e) on annual basis

The seasonal lowest Tmax value was computed to be in the range of 18.2–33.6 °C (being lowest and highest values for winter and summer seasons, respectively), with an average value of 28.2 °C (Fig. 7a–e). Figure 7 demonstrates the different statistical parameters estimated for all the seasons as well as on annual basis. Similarly, the seasonal highest Tmax value was computed to be in the range of 22.0–37.3 °C (being lowest and highest values for winter and summer seasons, respectively), with an average value of 30.7 °C (Fig. 7a–e). The Q1 value was recorded to be in the range of 19.2–34.8 °C, with an average value of 29.4 °C. Similarly, Q3 for seasonal Tmax was recorded to be in the range of 20.5–35.6 °C, with an average value of 30.2 °C on annual basis. The median value for seasonal Tmax was recorded to be in the range of 19.8–35.1 °C, with an average value of 29.8 °C. Similarly, the mean seasonal Tmax was computed in the range of 19.9–35.2 °C, with a mean value of 29.8 °C. As reported above, the trend in Tmin, Tmax, Q1, Q3, median and mean was similar (being lowest and highest for winter and spring seasons, respectively, in each case). However, the trend was slightly different for σn-12 and σn-1 values. σn-12 value varied from 0.7 to 1.9 (lowest and highest values for winter and spring seasons, respectively), with an average value of 0.3 (Fig. 7a–e). Similarly, σn-1 value varied from 0.8 to 1.4 °C (lowest and highest values for winter and spring seasons, respectively), with an average value of 0.5 °C annual basis.

Fig. 7
figure 7

Depiction of parameters of statistical analysis for Tmax during (a) spring, (b) summer, (c) autumn, (d) winter, and (e) on annual basis

The seasonal lowest rainfall was recorded to be in the range of 2.0–97.6 mm (being lowest and highest values for winter and summer seasons, respectively), with a total of 379.6 mm. Similarly, the seasonal highest rainfall was recorded to be in the range of 191.7–822.8 mm, with a total of 1334.0 mm (Fig. 8a–e), being minimum and maximum during spring and summer seasons, respectively. Figure 8 demonstrates the different statistical parameters estimated for all the seasons as well as on annual basis. The Q1 value for seasonal rainfall was recorded to be in the range of 33.9–358.3 mm (having lowest and highest values for spring and summer seasons, respectively), with a total of 591.6 mm. Similarly, Q3 was computed to be in the range of 87.2–600.6 mm (having lowest and highest values for spring and summer seasons, respectively), with a total of 909.2 mm. The median value for seasonal rainfall was recorded to be in the range of 48.4–483.1 mm (having lowest and highest values for spring and summer seasons, respectively), having a total of 727.0 mm. Similarly, the mean rainfall was recorded in the range of 63.7–485.9 mm (having lowest and highest values for spring and summer seasons, respectively), having a total of 747.4 mm. σn2 varied from 1891.6 to 25,815.2 (lowest and highest values for spring and summer seasons, respectively), having a total of 48,383.6 (Fig. 8a–e). Similarly, σn and σn-1 values varied from 43.5 to 160.7 (lowest and highest values for spring and summer seasons, respectively), having a total of 220.0.

Fig. 8
figure 8

Depiction of parameters of statistical analysis for rainfall during (a) spring, (b) summer, (c) autumn, (d) winter, and (e) on annual basis

The seasonal lowest ETo was computed to be in the range of 1.49–4.70 mm/day (being lowest and highest values for winter and summer seasons, respectively), with an average value of 5.44 mm/day. On annual basis, ETo was computed as 3.57 mm/day. Similarly, the seasonal highest ETo value was computed to be in the range of 2.27–6.43 mm/day (being lowest and highest values for winter and summer seasons, respectively), with an average value of 5.44 mm/day. The annual ETo was computed as 4.39 mm/day (Fig. 9a–e). Figure 9 demonstrates the different statistical parameters estimated for all the seasons as well as on annual basis. The Q1 value for seasonal ETo was recorded to be in the range of 1.66–5.26 mm/day (having lowest and highest values for winter and spring seasons, respectively), with an average value of 3.84 mm/day. Similarly, Q3 for seasonal ETo was recorded to be in the range of 1.89–5.67 mm/day (having lowest and highest values for winter and summer seasons, respectively), with an average value of 4.08 mm/day. The median value for seasonal ETo was recorded to be in the range of 1.79–5.45 mm/day (having lowest and highest values for winter and spring seasons, respectively), with an average value of 3.98 mm/day. Similarly, the mean value for seasonal ETo was computed in the range of 1.79–5.44 mm/day (having lowest and highest values for winter and summer seasons, respectively), with an average value of 3.97 mm/day. σn2 values varied from 0.03 to 0.16 (lowest and highest values for winter and summer seasons, respectively), with an average value of 0.04 (Fig. 9a–e). Similarly, σn values varied from 0.17 to 0.40 (lowest and highest values for winter and summer seasons, respectively), with an average value of 0.19.

Fig. 9
figure 9

Depiction of parameters of statistical analysis for ETo during (a) spring, (b) summer, (c) sutumn, (d) winter, and (e) on annual basis

Inter-correlation test among estimated ETo and recorded micro-meteorological parameters

For obtaining the inter-correlation between ETo, Tmax, Tmin, RHmax, RHmin, vw, SSH, and rainfall, a correlation matrices were obtained for all the four seasons as well as on annual basis using XLSTAT Software (Tables 4, 5, 6, 7 and 8). The absolute correlation coefficient values of > 0.9, > 0.75 (> 0.75 and ≤ 0.90), and > 0.6 (> 0.6 and ≤ 0.75) were used as standards for indicating strong, good, and moderate correlation, respectively, as suggested in Meshram and Sharma (2015). However, the correlation coefficient value ≤ 0.6 was used as a standard to indicate a poor correlation.

Table 4 Correlation matrix (Pearson) for spring season
Table 5 Correlation matrix (Pearson) for summer season
Table 6 Correlation matrix (Pearson) for autumn season
Table 7 Correlation matrix (Pearson) for winter season
Table 8 Correlation matrix (Pearson) on annual basis

During spring season, ETo formed moderately good correlations with RHmax (r =  − 0.66) and RHmin (r =  − 0.69), whereas poor correlations with Tmax (r =  + 0.59), vw (r =  + 0.51), and rainfall (r =  − 0.52). Similar correlations of ETo with Tmin, RHmin, and Tmax have been reported by Kingra (2018). Tmax formed moderately good correlations with Tmin (r = 0.63) and RHmax (r =  − 0.62), whereas poor correlations with RHmin (r =  − 0.56) and rainfall (r =  − 0.56). Tmin was poorly correlated to vw (r =  − 0.49). RHmax formed moderately good correlations with RHmin (r =  + 0.70) and rainfall (r =  + 0.63). RHmin also formed a moderately good correlation with rainfall (r =  + 0.63). The analysis confirmed that ETo decreases with increase in RHmax, RHmin, and rainfall, whereas increases with increase in Tmax and vw. During summer season, ETo formed good correlations with RHmin (r =  − 0.78) and SSH (r =  + 0.82), whereas a moderately good correlation with Tmax (r =  + 0.73). ETo also formed poor correlations with RHmax (r =  − 0.58), vw (r =  + 0.41), and rainfall (r =  − 0.48). Tmax formed good and moderately good correlation with RHmin (r =  − 0.77) and RHmax (r =  − 0.68), respectively. Tmax was poorly correlated with SSH (r =  + 0.41) and rainfall (r =  − 0.57). Tmin formed a moderately good correlation with vw (r =  − 0.63) and was poorly correlated to RHmin (r =  + 0.30). RHmax formed a moderately good correlation with RHmin (r =  + 0.74), whereas poor correlations with vw (r =  − 0.34) and rainfall (r =  + 0.38). RHmin was poorly correlated with vw (r =  − 0.30), SSH (r =  − 0.48), and rainfall (r =  + 0.56). SSH was also poorly correlated to rainfall (r =  − 0.29). It revealed that ETo decreases with increase in RHmin, RHmax, and rainfall, whereas increases with increase in SSH and vw.

During autumn, ETo formed good correlations with vw (r =  + 0.79) and SSH (r =  + 0.75), whereas moderately good correlations with Tmin (r =  − 0.62) and RHmin (r =  − 0.73). ETo formed a negative correlation with Tmin, indicating decrease in ETo with increase in Tmin, which confirmed the results of Mann–Kendall’s test, Sen’s slope test, and homogeneity test. Similar observation has been made by Kingra (2018). Further, Kashyap and Agarwal (2020) have reported decreased ETo with increase in Tmin. ETo also formed a poor correlation with RHmax (r =  − 0.58). Tmax was poorly correlated with RHmin (r =  − 47) and RHmax (r =  − 0.43). Tmin formed a moderately good correlation with RHmin (r =  + 0.64), whereas poor correlations with RHmax (r =  + 0.45), vw (r =  − 0.54), and SSH (r =  − 0.35). RHmax formed a moderately good correlation with RHmin (r =  + 0.70) and poor correlations with vw (r =  − 0.40) and SSH (r =  − 0.31). RHmin was also poorly correlated with vw (r =  − 0.44) and SSH (r =  − 0.49). vw was also poorly correlated to SSH (r =  + 0.55). The analysis confirmed that ETo decreases with increase in Tmin, RHmin, and RHmax, whereas increases with increase in vw and SSH. During winter, ETo formed strong and good correlations with Tmin (r =  + 1.0) and RHmin (r =  − 0.80), respectively. ETo also formed moderately good correlations with Tmax (r =  + 0.68), vw (r =  + 0.67), and SSH (r =  + 0.71), whereas poor correlations with RHmax (r =  − 0.49) and rainfall (r =  − 0.30). Tmax formed a moderately good correlation with Tmin (r =  + 0.68), whereas poor correlations with RHmin (r =  − 0.53), SSH (r =  + 0.41), and rainfall (r =  − 0.35). Tmin formed a good correlation with RHmin (r =  − 0.80), whereas moderately good correlations with vw (r =  + 0.67) and SSH (r = 0.71). Tmin also formed poor correlation with RHmax (r =  − 0.49) and rainfall (r =  − 0.30). RHmax formed moderately good and poor correlations with RHmin (r =  + 0.62) and vw (r =  − 0.41), respectively. RHmin was poorly correlated with vw (r =  − 0.32), SSH (r =  − 0.53), and rainfall (= + 0.36). vw was also poorly correlated to SSH (r =  + 0.54). It revealed that ETo significantly decreases with increase in RHmin, RHmax, and rainfall, whereas increases with increase in Tmin, Tmax, vw, and SSH.

On annual basis, ETo formed good correlation with vw (r =  + 0.76), whereas moderately good correlations with Tmin (r =  − 0.64), RHmin (r =  − 0.75), and SSH (r =  + 0.63). ETo was negatively correlated to Tmin, indicating decreased ETo with increased Tmin, as reported in Kingra (2018). ETo also formed poor correlations with Tmax (r =  + 0.31), RHmax (r =  − 0.53), and rainfall (r =  − 0.30). Tmax was poorly correlated with RHmax (r =  − 0.38), RHmin (r =  − 0.31), and rainfall (r =  − 0.36). Tmin formed a good correlation with vw (r =  − 0.79), whereas a moderately good correlation with RHmin (r =  + 0.65). Tmin also formed poor correlations with RHmax (r =  + 0.42) and SSH (r =  − 0.31). RHmax formed moderately good and poor correlations with RHmin (r =  + 0.64) and vw (r =  − 0.41), respectively. RHmin was poorly correlated with vw (r =  − 0.51) and SSH (r =  − 0.33) and rainfall (= + 0.33). vw was also poorly correlated to SSH (r =  + 0.50). The analysis confirmed that ETo significantly decreases with increase in Tmin, RHmin, RHmax, and rainfall, whereas increases with increase in vw, Tmax, and SSH. ETo formed a positive correlation with Tmax for spring, summer, and winter seasons, indicating increase in ETo with increase in Tmax, as also reported in Kingra (2018). Similarly, ETo was negatively correlated to rainfall during spring, summer, winter, and on annual basis, indicating declining ETo with increasing rainfall.

Model validation

The model coefficients for Tmax, Tmin, RHmax, RHmin, vw, and SSH were standardized for all the seasons as well as on annual basis as shown in Fig. 10a–e. A relationship was also developed between computed and predicted ETo for all the respective seasons as well as on annual basis as shown in Fig. 11. At the time of model development, the coefficient of determination (r2) value varied in the range of 0.90–0.98, being lowest and highest during autumn and spring seasons, respectively, with a value of 0.91 on annual basis. The RMSE value varied in the range of 0.05–0.11, being lowest and highest during winter and summer seasons, respectively, with a value of 0.07 on annual basis.

Fig. 10
figure 10

Standardized coefficients of ETo modeling during (a) spring, (b) summer, (c) autumn, (d) winter, and (e) on annual basis

Fig. 11
figure 11

Relationship between ETo and predicted ETo during (a) spring, (b) summer, (c) autumn, (d) winter, and (e) on annual basis

During validation period (2000–2019), the mean bias error varied in the range of − 0.08 to 0.04, being lowest and highest during autumn and winter, respectively with a value of − 0.06 mm/day on annual basis. The mean absolute error was recorded to be in the range of 0.00–0.08 (Table 9), being lowest and highest during spring and autumn seasons, respectively, with a value of 0.06 on annual basis, whereas RMSE varied in the range of 0.05–0.11 (Table 9), being lowest and highest during spring and autumn seasons, respectively, having a value of 0.07 on annual basis. Similarly, σ value varied in the range of 0.05–0.07 (Table 9), being lowest and highest during spring/winter and summer/autumn seasons, respectively, having a value of 0.04 on annual basis. The d value varied in the range of 0.99–1.00 (Table 9), being lowest and highest values during autumn/winter and spring/summer seasons, respectively, having a value of 0.99 on annual basis. The statistical comparison indicated a fairly good agreement between the computed and predicted ETo values (Fig. 12). Thus, the developed models would be useful in simplified estimation of ETo on both seasonal and annual basis for the present study region.

Table 9 Statistical parameters of model validation
Fig. 12
figure 12

Comparison between predicted and observed ETo data during model development and validation

Conclusions

All the tests (Mann–Kendall’s test, Sen’s slope test, and homogeneity tests) confirmed the existence of increasing (upward) and decreasing (downward) trends in Tmin and ETo, respectively, during all the four seasons (spring, summer, autumn, and winter) as well as on annual basis. The decreasing trend in ETo is mainly due to the temporal increase in Tmin and homogeneity in Tmax, leading to decreasing temperature differences (i.e., Tmax-Tmin). The homogeneity tests indicated change point occurrence in Tmin (increasing trend) and ETo (decreasing trend) during all the four seasons as well on annual basis, whereas the Tmax (except during spring) and rainfall data was observed to be homogeneous. The correlation test indicated a significant decrease in ETo with increase in RHmin, RHmax, rainfall (except during autumn), and Tmin (except during spring, summer, and winter), whereas increase with increase in vw, SSH (except during spring season), and Tmax (except during summer and autumn). The statistical comparison indicated a fairly good agreement between the computed and predicted ETo values. The developed models would be useful in simplified estimation of ETo on seasonal and annual basis. Such studies may be useful for predicting the location-specific futuristic climate scenarios in relation to long-term historical climatic data and therefore in mitigating the climate change impacts on agricultural production. Moreover, the modeling of ETo would be useful to predict the crop water requirements or irrigation amounts, which in turn can help in planning crops and scheduling irrigation.