The Penman–Monteith equation (FAO-56) is accepted as the standard model for estimating reference evapotranspiration (ETo). However, the major obstacle to using FAO-56 widely is that it requires numerous climatic data. The Hargreaves–Samani (HS) method is frequently used for the calculation of ETo since it is based on measurements of daily minimum and maximum air temperature alone. Those are commonly recorded at many meteorological stations throughout the world. It is the objective of this paper to evaluate the quality of HS and calibrate the coefficients of this method for different climates as represented by the Köppen classification. Estimated values are compared with Penman–Monteith ETo values in terms of the coefficient of efficiency Ceff as well as the root mean square error, the mean absolute error and the Bayes information criterion. The Penman–Monteith equation for ETo (FAO-56) is based on physics and known to provide best estimates of ETo. The results of our work show that the correlation between long-term monthly means of HS and FAO-56 can be improved significantly by introducing climate-class specific coefficients.

Evapotranspiration (ET) from the Earth's surface is the driver of the global atmospheric water cycle. Accurate irrigation water requirement estimations are crucial for efficient management and planning of water resources and therefore the estimation of reference evapotranspiration (ETo) is important for irrigation management. The knowledge of monthly ET is of great importance in the study and management of present and future water resources and for solving many theoretical problems in the field of hydrology, climatology and geographical ecology. As an agroclimatic index, long-term monthly means of ETo have been widely used to assess the effect of water in agronomy, irrigation planning as well as climate change impact.

Many estimation methods based on meteorological variables have been developed. Numerous formulations, classified as radiation based, temperature based, pan-evaporation based, mass-transfer based as well as combinations of those have been developed (Jensen et al. 1990).

The FAO-56 Penman–Monteith (hereafter FAO-56) equation is recommended as the standard model for estimating ETo (Allen et al. 1998) in all climates. Many researchers have confirmed that FAO-56 is superior to other estimation methods (Hargreaves & Allen 2003; Berengena & Gavilán 2005; Sentelhas et al. 2010; Tabari & Talaee 2011; Rahimikhoob et al. 2012; Maestre-Valero et al. 2013; Tabari et al. 2013; Valiantzas 2013). Due to the absence of experimental records, data-driven models are often calibrated to calculate FAO-56 ETo targets. This procedure is also adopted for calibrating more conventional empirical approaches (Marti et al. 2015).

FAO-56 is of the best quality since it models evaporation based on physics. This is possible only if daily minimum and maximum temperature, humidity, wind speed and sunshine duration are known. However, observations of these variables are often not available. This is the major obstacle to using FAO-56 widely.

Among many other methods, the Hargreaves–Samani (HS) equation, which employs only maximum and minimum temperature data, can be used to approximate ETo. This empirical model is one of the most commonly used. It is recommended by Allen et al. (1998) and again by Allen (2006) as the best approximation to FAO-56. As an empirical method, HS involves empirical coefficients. While HS can be applied with some standard values of these coefficients, several authors (Allen et al. 1998) recommended calibrating HS with respect to FAO-56 at locations with comparable climate.

Samani (2000) found that factors other than solar radiation, wind speed and humidity can influence local observations of the difference in maximum and minimum temperature and thus the results of HS. These factors include latitude, elevation, topography, storm pattern, advection and proximity to large water bodies. At low latitudes, for example, the diurnal temperature range can become very small and, consequently, HS can significantly underestimate both solar radiation and ET.

Several attempts to improve the accuracy of HS have been made, mainly by using wind speed, elevation, precipitation, distance to coastline, air humidity or solar radiation data (Shahidian et al. 2013). However, it is not desirable to use these climatic variables directly in the HS equation because this would take away the ease of implementation and simplicity of the model.

HS modifications in the literature include modifying the original calibration coefficients by a linear regression with or without a constant term. Some authors include more variables that could be fit to observations or FAO-56 (Allen et al. 1998; Droogers & Allen 2002; Trajkovic 2007; Tabari & Talaee 2011; Razzaghi & Sepaskhah 2012; Mohawesh & Talozi 2012; Ngongondo et al. 2013; Raziei & Pereira 2013; Heydari & Heydari 2014). According to Alexandris et al. (2006), HS is often unable to capture the effect of some important climatic variables. Some authors have found overestimations of ET by HS under humid environments and underestimation under windy conditions, compared to the Penman–Monteith equation (Allen et al. 1998; Droogers & Allen 2002). Hargreaves & Allen (2003) have shown that the HS ET estimation differences are caused primarily by impacts of local humidity on the computed vapor pressure deficit.

HS performed better in semi-arid and arid regions (López-Urrea et al. 2006), while it performed poorly in humid climates (Yoder et al. 2005; Wang et al. 2014). In this regard, the performance of the HS model and its calibration have been widely assessed in different climatic zones. The study was carried out using a monthly timescale and FAO-56 benchmarks.

The main objective of the present study is the evaluation of the HS global performance for all climate zones and the fit of a calibrated Hargreaves equation (HSc) for different climate conditions. The goal is to provide optimized versions of the Hargreaves formulation for each individual Köppen class as an alternative to FAO-56 when only maximum and minimum daily temperatures are available.

Global climate data set

The models are applied using the climate database from the Agromet Group of United Nations Food and Agriculture Organization (FAO). The data set of long-term monthly means can be downloaded together with the interpolation tool New_LocClim from http://www.fao.org/nr/climpag/. Monthly mean values are available for 4,368 stations worldwide. Table 1 shows how the stations are distributed among the continents.

Table 1

Number of stations per continent within the FAO Agromet database

ContinentNo. of stations
Africa 1,042 
America 1,026 
Asia 1,254 
Europe 764 
Oceania 282 
ContinentNo. of stations
Africa 1,042 
America 1,026 
Asia 1,254 
Europe 764 
Oceania 282 

This data set is considered to be an excellent source of information to compare different ET estimates for different climate zones.

Köppen climate classification

Climate classifications are introduced to organize large amounts of climatic information and provide a concise description. A widely accepted system of climate classification is summarized by Köppen (1936). Recently updated world maps are available (Kottek et al. 2006; Peel et al. 2007). Although introduced in the nineteenth century, the Köppen classification was published in substantially its present form in 1918. It is still the most widely used since it reflects natural vegetation as an expression of climate. This climate–vegetation association provides a relation between a multivariate description of climate and an easily visualized landscape.

The Köppen classification identifies five main groups of climates: tropical climates (A), dry climates (B), temperate climates (C), boreal climates (D) and polar climates (E). All these main groups are further divided by Köppen in order to better classify sub-climates. In this paper we use the Köppen classes as provided in Table 2.

Table 2

Köppen classes used in this paper

ClassDefinition
Af Equatorial full humid rainforest 
As Equatorial savannah with dry summer 
Aw Equatorial savannah with dry winter 
BS Steppe climate 
BW Desert climate 
Cs Warm temperate climate with dry summer 
Cw Warm temperate climate with dry winter 
Cf Warm temperate fully humid climate 
Ds Snow climate with dry summer 
Dw Snow climate with dry winter 
Df Snow climate 
Polar climate 
ClassDefinition
Af Equatorial full humid rainforest 
As Equatorial savannah with dry summer 
Aw Equatorial savannah with dry winter 
BS Steppe climate 
BW Desert climate 
Cs Warm temperate climate with dry summer 
Cw Warm temperate climate with dry winter 
Cf Warm temperate fully humid climate 
Ds Snow climate with dry summer 
Dw Snow climate with dry winter 
Df Snow climate 
Polar climate 

The Köppen system of climate classification was found to be particularly suitable for disaggregating the correlations between FAO-56 and HS because it is a system with global applicability and is still the most widely used since it only depends on temperature and precipitation (De Pauw 2008). Figure 1 shows the number of stations of the FAO climate database for each of the sub-climate types considered. Data are available for 12 calendar months per station. Hence the analysis is based on 52,416 data pairs.
Figure 1

Number of stations in the FAO Agromet database per Köppen climate class.

Figure 1

Number of stations in the FAO Agromet database per Köppen climate class.

Close modal

FAO-56 Penman–Monteith ETo

ETo is defined in Allen et al. (1998) as the rate of ET from a hypothetical grass reference with an assumed crop height of 0.12 m, a fixed surface resistance of 70 s m−1 and an albedo of 0.23. The reference surface closely resembles an extensive surface of green, well-watered grass of uniform height, actively growing and completely shading the ground. The fixed surface resistance of 70 s m−1 implies a moderately dry soil surface resulting from about a weekly irrigation frequency. Standardized parameterizations of the FAO-56 formulation are described for calculating ET for grass and alfalfa references. The ETo, despite some shortcomings, can be a consistent and reproducible index for a weather-based potential ET. ETo computed using a short crop reference is abbreviated as ETo (Allen 2006). The variables used in the computation of ETo are net radiation, wind speed, air humidity and temperature. As the ETo computation is always made for the same reference surface, the crop type, stage of development and soil moisture do not change and cannot affect the ETo formulation. FAO-56 ETo is computed as (Allen et al. 1998; Allen 2006):
1
with the ETo (mm day−1), the slope of the saturation vapor pressure Δ (kPa °C−1), the net radiation Rn (MJ m−2 day−1), the soil heat flux density G, for monthly periods it is not 0 and was computed from surface temperature of previous and next month (MJ m−2 day1), the mean daily air temperature T at 2 m height in (°C), the short grass reference coefficients Cn = 900 and Cd = 0.34, the wind speed at 2 m height u2 (m s−1), the saturation vapor pressure es (kPa), the actual vapor pressure ea (kPa) and the psychrometric constant γ (kPa °C−1). The net radiation is the sum of the net short-wave radiation and the net long-wave radiation.

HS method

The empirical HS method (Hargreaves & Samani 1982, 1985) is given as:
2
where ETHS is the evapotranspiration estimated by the HS method (mm day−1), Ra is extraterrestrial radiation (MJ m−2 day−1), kRS is an empirical coefficient, Tm is the mean air temperature (°C), Tx is the daily maximum air temperature (°C) and Tn is the daily minimum air temperature (°C). The setoff of 17.8 °C sets ETHS = 0 for Tm = − 17.8 °C which corresponds to 0 Fahrenheit. For Tm < −17.8 °C ETHS is kept at 0. The factor 0.408 converts MJ m−2 day−1 into mm day−1. 0.0135 is the original empirical coefficient proposed by Hargreaves & Samani (1985).
The empirical coefficient kRS, was initially fixed at 0.17 for arid and semi-arid regions. Hargreaves (1994) recommended using 0.16 for inland areas and 0.19 for coastal regions. With Ra in mm day−1 and kRS = 0.17 this leads to:
3
The equation is based on the assumption that the difference between daily maximum and minimum temperatures provides a general indication of cloudiness. HS modifications in the literature include modifying the original empirical coefficients.

Modified HS equations

For the purpose of this work, HS is re-written in the general form:
4
where k1, k2 and k3 are calibration coefficients, with original, un-calibrated values of k1 = 0.0023, k2 = 0.5 and k3 = 0. For an optimization all three coefficients can be fit. Alternatively, one or two of them can be fixed at their given value while the other coefficients can be optimized.
In this study we compare the five different versions:
5
6
7
8
9

Statistical analysis

In order to quantify the performance of the different versions we use four measures. Those are the root mean square error (RMSE), the mean absolute error (MAE), the coefficient of efficiency (Ceff) and the Bayes information criterion (BIC). They are given as:
10
11
12
13
where ETm is the ETo estimate from FAO-56, ETc is the reference evapotranspiration ETHSc estimate from the respectively corrected HS equation, ETav is the mean of the FAO-56 ET for the respective climate class, n is the number of data pairs used and k is the number of free coefficients of the model.

Legates & McCabe (1999) suggested using the coefficient of efficiency for evaluating the goodness of fit. Ceff ranges from minus infinity to 1.0 with larger values indicating better agreement. The coefficient of efficiency is recommended by several authors to evaluate the performance of a model. Moriasi et al. (2007) classified model performance as very good if Ceff >0.75, good if 0.65 < Ceff ≤0.75, satisfactory if 0.50 < Ceff ≤0.65 and poor if Ceff ≤0.50.

In this work the coefficient of efficiency is used in conjunction with the RMSE and MAE. The RMSE is one of the commonly used error indices. Willmott & Matsuura (2005) indicate that MAE is the most natural measure of average error magnitude.

While RMSE, MAE and Ceff provide information on the quality of ETHSc, BIC (Schwarz 1978; Beal 2007) is especially useful for model selection since it penalizes models with a higher degree of freedom, i.e., more free coefficients. Usually models with the lowest BIC are preferred, according to the parsimony principle.

Köppen climate class, ETo by FAO-56, HS and the five versions of ETHSc are calculated for the 4,368 stations of the FAO Agromet global climate database. All stations are grouped by the 12 Köppen climate classes considered. The five calibrated ETHSc equations are optimized with respect to FAO-56 for each Köppen climate class separately.

The results of the best fit of the different ETHSc versions are provided in Table 3. It shows the RMSE, the MAE, the coefficient of efficiency (Ceff) and the BIC value and the best estimates of k1, k2, k3 for different Köppen climate zones and each ETHSc.

Table 3

Performance measures (RMSE, mm day−1, MAE, mm day−1, Ceff and BIC) of ETHSc as compared to FAO-56 ET as well as the respective coefficients k1, k2, k3 of the different corrections

ClassModelRMSEMAECeffBICk1k2k3
Af HS1 0.575 0.451 −2,768 0.002 0.5  
Af HS2 0.537 0.419 0.129 −3,113 0.0023 0.43222  
Af HS3 0.425 0.335 0.453 −4,273 0.0051 0.07193  
Af HS4 0.491 0.391 0.271 −3,551 0.0010 0.5 1.8778 
Af HS5 0.425 0.335 0.454 −4,268 0.0049 0.07415 0.1289 
Af HS 0.804 0.663 −0.955 −1,093 0.0023 0.5  
As HS1 0.709 0.523 0.104 −1,106 0.00204 0.5  
As HS2 0.679 0.496 0.179 −1,247 0.0023 0.44523  
As HS3 0.595 0.446 0.369 −1,666 0.00458 0.15343  
As HS4 0.649 0.487 0.25 −1,386 0.00116 0.5 1.7492 
As HS5 0.594 0.444 0.371 −1,665 0.00511 0.14317 − 0.3678 
As HS 0.872 0.728 −0.355 −443 0.0023 0.5  
Aw HS1 0.74 0.551 0.393 −5,120 0.00208 0.5  
Aw HS2 0.726 0.537 0.416 −5,444 0.0023 0.45534  
Aw HS3 0.706 0.523 0.448 −5,914 0.00321 0.31546  
Aw HS4 0.719 0.54 0.426 −5,584 0.00163 0.5 0.9053 
Aw HS5 0.704 0.523 0.451 −5,954 0.00283 0.33314 0.3466 
Aw HS 0.859 0.702 0.181 −2,578 0.0023 0.5  
BS HS1 0.893 0.664 0.764 −2,693 0.00231 0.5  
BS HS2 0.893 0.663 0.764 −2,690 0.0023 0.49988  
BS HS3 0.883 0.657 0.769 −2,946 0.00296 0.40288  
BS HS4 0.886 0.657 0.768 −2,876 0.00217 0.5 0.2921 
BS HS5 0.881 0.654 0.77 −2,997 0.00272 0.42152 0.1783 
BS HS 0.893 0.663 0.764 −2,700 0.0023 0.5  
BW HS1 1.22 0.92 0.749 2,312 0.00262 0.5  
BW HS2 1.231 0.924 0.744 2,414 0.0023 0.54699  
BW HS3 1.211 0.919 0.753 2,235 0.00338 0.4038  
BW HS4 1.22 0.92 0.749 2,318 0.00259 0.5 0.0719 
BW HS5 1.211 0.918 0.753 2,237 0.00354 0.39352 − 0.1157 
BW HS 1.394 0.993 0.672 3,842 0.0023 0.5   
Cf HS1 0.539 0.403 0.853 −12,499 0.00212 0.5   
Cf HS2 0.531 0.396 0.858 −12,805 0.0023 0.46412   
Cf HS3 0.516 0.384 0.866 −13,386 0.00323 0.32259   
Cf HS4 0.517 0.387 0.865 −13,358 0.00192 0.5 0.3199 
Cf HS5 0.505 0.377 0.871 −13,813 0.00277 0.35817 0.2345 
Cf HS 0.594 0.45 0.822 −10,543 0.0023 0.5  
Cs HS1 0.557 0.423 0.863 −1,974 0.00214 0.5  
Cs HS2 0.545 0.412 0.868 −2,049 0.0023 0.46837   
Cs HS3 0.497 0.376 0.89 −2,350 0.00413 0.23782   
Cs HS4 0.543 0.42 0.869 −2,051 0.00198 0.5 0.2663 
Cs HS5 0.497 0.375 0.89 −2,343 0.00419 0.2342 − 0.0208 
Cs HS 0.608 0.471 0.836 −1,683 0.0023 0.5   
Cw HS1 0.645 0.476 0.709 −3,740 0.00210 0.5   
Cw HS2 0.645 0.476 0.709 −3,736 0.0023 0.46359  
Cw HS3 0.645 0.475 0.71 −3,734 0.00218 0.48548  
Cw HS4 0.64 0.471 0.714 −3,801 0.00195 0.5 0.2863 
Cw HS5 0.64 0.471 0.714 −3,794 0.00191 0.50728 0.2939 
Cw HS 0.737 0.598 0.62 −2,604 0.0023 0.5  
Df HS1 0.474 0.33 0.903 −6,287 0.00203 0.5  
Df HS2 0.475 0.33 0.902 −6,256 0.0023 0.45044  
Df HS3 0.473 0.331 0.903 −6,292 0.00174 0.56201  
Df HS4 0.467 0.322 0.906 −6,407 0.00195 0.5 0.1309 
Df HS5 0.463 0.323 0.907 −6,468 0.00130 0.65944 0.1695 
Df HS 0.559 0.39 0.865 −4,907 0.0023 0.5  
Ds HS1 0.331 0.224 0.963 −393 0.00210 0.5  
Ds HS2 0.33 0.222 0.963 −394 0.0023 0.46617  
Ds HS3 0.329 0.221 0.963 −389 0.00240 0.44976   
Ds HS4 0.327 0.216 0.964 −392 0.00205 0.5 0.0854 
Ds HS5 0.327 0.216 0.964 −386 0.00211 0.48956 0.08 
Ds HS 0.419 0.275 0.941 −313 0.0023 0.5   
Dw HS1 0.534 0.409 0.873 −1,362 0.00199 0.5   
Dw HS2 0.527 0.405 0.876 −1,391 0.0023 0.44041   
Dw HS3 0.518 0.403 0.881 −1,424 0.00358 0.26577   
Dw HS4 0.48 0.345 0.898 −1,589 0.00171 0.5 0.4566 
Dw HS5 0.464 0.335 0.904 −1,654 0.00317 0.25526 0.4441 
Dw HS 0.667 0.478 0.802 −884 0.0023 0.5   
HS1 0.44 0.346 0.843 −762 0.00228 0.5   
HS2 0.44 0.346 0.843 −763 0.0023 0.49626   
HS3 0.438 0.346 0.844 −760 0.00256 0.45471   
HS4 0.38 0.292 0.883 −894 0.00188 0.5 0.4621 
HS5 0.378 0.29 0.884 −892 0.00146 0.59181 0.5134 
HS 0.44 0.347 0.843 −768 0.0023 0.5   
All HS1 0.846 0.599 0.785 −1,7548 0.00223 0.5   
All HS2 0.845 0.599 0.785 −1,7588 0.0023 0.48657   
All HS3 0.845 0.599 0.785 −1,7583 0.00234 0.47934   
All HS4 0.844 0.595 0.786 −1,7743 0.00216 0.5 0.1272 
All HS5 0.844 0.595 0.786 −1,7734 0.00219 0.49465 0.1214 
All HS 0.855 0.625 0.78 −16,366 0.0023 0.5  
ClassModelRMSEMAECeffBICk1k2k3
Af HS1 0.575 0.451 −2,768 0.002 0.5  
Af HS2 0.537 0.419 0.129 −3,113 0.0023 0.43222  
Af HS3 0.425 0.335 0.453 −4,273 0.0051 0.07193  
Af HS4 0.491 0.391 0.271 −3,551 0.0010 0.5 1.8778 
Af HS5 0.425 0.335 0.454 −4,268 0.0049 0.07415 0.1289 
Af HS 0.804 0.663 −0.955 −1,093 0.0023 0.5  
As HS1 0.709 0.523 0.104 −1,106 0.00204 0.5  
As HS2 0.679 0.496 0.179 −1,247 0.0023 0.44523  
As HS3 0.595 0.446 0.369 −1,666 0.00458 0.15343  
As HS4 0.649 0.487 0.25 −1,386 0.00116 0.5 1.7492 
As HS5 0.594 0.444 0.371 −1,665 0.00511 0.14317 − 0.3678 
As HS 0.872 0.728 −0.355 −443 0.0023 0.5  
Aw HS1 0.74 0.551 0.393 −5,120 0.00208 0.5  
Aw HS2 0.726 0.537 0.416 −5,444 0.0023 0.45534  
Aw HS3 0.706 0.523 0.448 −5,914 0.00321 0.31546  
Aw HS4 0.719 0.54 0.426 −5,584 0.00163 0.5 0.9053 
Aw HS5 0.704 0.523 0.451 −5,954 0.00283 0.33314 0.3466 
Aw HS 0.859 0.702 0.181 −2,578 0.0023 0.5  
BS HS1 0.893 0.664 0.764 −2,693 0.00231 0.5  
BS HS2 0.893 0.663 0.764 −2,690 0.0023 0.49988  
BS HS3 0.883 0.657 0.769 −2,946 0.00296 0.40288  
BS HS4 0.886 0.657 0.768 −2,876 0.00217 0.5 0.2921 
BS HS5 0.881 0.654 0.77 −2,997 0.00272 0.42152 0.1783 
BS HS 0.893 0.663 0.764 −2,700 0.0023 0.5  
BW HS1 1.22 0.92 0.749 2,312 0.00262 0.5  
BW HS2 1.231 0.924 0.744 2,414 0.0023 0.54699  
BW HS3 1.211 0.919 0.753 2,235 0.00338 0.4038  
BW HS4 1.22 0.92 0.749 2,318 0.00259 0.5 0.0719 
BW HS5 1.211 0.918 0.753 2,237 0.00354 0.39352 − 0.1157 
BW HS 1.394 0.993 0.672 3,842 0.0023 0.5   
Cf HS1 0.539 0.403 0.853 −12,499 0.00212 0.5   
Cf HS2 0.531 0.396 0.858 −12,805 0.0023 0.46412   
Cf HS3 0.516 0.384 0.866 −13,386 0.00323 0.32259   
Cf HS4 0.517 0.387 0.865 −13,358 0.00192 0.5 0.3199 
Cf HS5 0.505 0.377 0.871 −13,813 0.00277 0.35817 0.2345 
Cf HS 0.594 0.45 0.822 −10,543 0.0023 0.5  
Cs HS1 0.557 0.423 0.863 −1,974 0.00214 0.5  
Cs HS2 0.545 0.412 0.868 −2,049 0.0023 0.46837   
Cs HS3 0.497 0.376 0.89 −2,350 0.00413 0.23782   
Cs HS4 0.543 0.42 0.869 −2,051 0.00198 0.5 0.2663 
Cs HS5 0.497 0.375 0.89 −2,343 0.00419 0.2342 − 0.0208 
Cs HS 0.608 0.471 0.836 −1,683 0.0023 0.5   
Cw HS1 0.645 0.476 0.709 −3,740 0.00210 0.5   
Cw HS2 0.645 0.476 0.709 −3,736 0.0023 0.46359  
Cw HS3 0.645 0.475 0.71 −3,734 0.00218 0.48548  
Cw HS4 0.64 0.471 0.714 −3,801 0.00195 0.5 0.2863 
Cw HS5 0.64 0.471 0.714 −3,794 0.00191 0.50728 0.2939 
Cw HS 0.737 0.598 0.62 −2,604 0.0023 0.5  
Df HS1 0.474 0.33 0.903 −6,287 0.00203 0.5  
Df HS2 0.475 0.33 0.902 −6,256 0.0023 0.45044  
Df HS3 0.473 0.331 0.903 −6,292 0.00174 0.56201  
Df HS4 0.467 0.322 0.906 −6,407 0.00195 0.5 0.1309 
Df HS5 0.463 0.323 0.907 −6,468 0.00130 0.65944 0.1695 
Df HS 0.559 0.39 0.865 −4,907 0.0023 0.5  
Ds HS1 0.331 0.224 0.963 −393 0.00210 0.5  
Ds HS2 0.33 0.222 0.963 −394 0.0023 0.46617  
Ds HS3 0.329 0.221 0.963 −389 0.00240 0.44976   
Ds HS4 0.327 0.216 0.964 −392 0.00205 0.5 0.0854 
Ds HS5 0.327 0.216 0.964 −386 0.00211 0.48956 0.08 
Ds HS 0.419 0.275 0.941 −313 0.0023 0.5   
Dw HS1 0.534 0.409 0.873 −1,362 0.00199 0.5   
Dw HS2 0.527 0.405 0.876 −1,391 0.0023 0.44041   
Dw HS3 0.518 0.403 0.881 −1,424 0.00358 0.26577   
Dw HS4 0.48 0.345 0.898 −1,589 0.00171 0.5 0.4566 
Dw HS5 0.464 0.335 0.904 −1,654 0.00317 0.25526 0.4441 
Dw HS 0.667 0.478 0.802 −884 0.0023 0.5   
HS1 0.44 0.346 0.843 −762 0.00228 0.5   
HS2 0.44 0.346 0.843 −763 0.0023 0.49626   
HS3 0.438 0.346 0.844 −760 0.00256 0.45471   
HS4 0.38 0.292 0.883 −894 0.00188 0.5 0.4621 
HS5 0.378 0.29 0.884 −892 0.00146 0.59181 0.5134 
HS 0.44 0.347 0.843 −768 0.0023 0.5   
All HS1 0.846 0.599 0.785 −1,7548 0.00223 0.5   
All HS2 0.845 0.599 0.785 −1,7588 0.0023 0.48657   
All HS3 0.845 0.599 0.785 −1,7583 0.00234 0.47934   
All HS4 0.844 0.595 0.786 −1,7743 0.00216 0.5 0.1272 
All HS5 0.844 0.595 0.786 −1,7734 0.00219 0.49465 0.1214 
All HS 0.855 0.625 0.78 −16,366 0.0023 0.5  

Best fit coefficients are in bold font while default values are in italics.

Both MAE and RMSE are lowest for ETHS5 (sometimes together with ETHS3 or ETHS4). Improvements compared to the original HS method in MAE and RMSE are in the order of 20 to 50% for all three Köppen A classes. For other climate classes improvements are in the order of 10 to 40%.

In the ETHS5 model, the highest errors are observed in the dry B classes with RMSE (ETHS5) = 1.211 mm day−1 for climate class BW (desert) followed by the class BS with RMSE (ETHS5) = 0.881 mm day−1. The lowest errors are observed in the class Ds with RMSE (ETHS5) = 0.327 mm day−1 followed by the E climates with RMSE (ETHS5) = 0.378 mm day−1.

Mean ETo per climate class ranges from 1.91 mm day−1 in polar climates to 5.13 mm day−1 in deserts. Given this wide range of more than factor 2.5 in mean ETo it is reasonable to look at a relative MAE, defined as MAE over ETav per climate class. Figure 2 shows these relative values of MAE. For ETHS5 highest relative MAE occurs in Df climates with 18.7% of the mean ETo followed by BW with 17.9%. The lowest MAE with respect to mean ETo occurs in climate class Af with 9%, followed by Ds with 10.1% and As with 11%. These ratios are considerably higher for the original HS method. Since HS was originally calibrated for semi-arid climates no substantial improvements are achieved for the BS climate class.
Figure 2

Relative MAE (MAE over mean ETo per climate class) of HS and various calibrations of HS. Values of mean ETo per climate class in mm day−1 are provided as well.

Figure 2

Relative MAE (MAE over mean ETo per climate class) of HS and various calibrations of HS. Values of mean ETo per climate class in mm day−1 are provided as well.

Close modal
The results of statistical indices obtained are similar to the ranges obtained by Gavilán et al. (2006), Tabari & Talaee (2011) and Shahidian et al. (2013). For all climate classes, Ceff values of ETHS5 are highest, indicating that this calibrated version performs best. For A climates Ceff is below 0.5 for all versions, i.e., all versions perform poorly. This indicates that the proxy (TxTn)k2 is not optimal for the estimation of ETo in tropical climates. Ceff is 0.714 for ETHS5 and climate class Cw meaning that HS5 performs well for this climate. For all other climate classes ETHS5 performs very well with Ceff values larger than 0.75 (Figure 3).
Figure 3

Coefficient of efficiency (Ceff) of HS and various calibrations of HS.

Figure 3

Coefficient of efficiency (Ceff) of HS and various calibrations of HS.

Close modal
Since ETHS5 fits three free coefficients and therefore has more degrees of freedom than all other ETHSc versions, it is also important to look at BIC. BIC values depend on the number of data pairs used. This number is very different for each climate class (Figure 1). For better visualization we therefore standardize all BIC values within each climate class. The resulting values are depicted in Figure 4. In 5 out of 12 climate classes BIC is lowest for ETHS5 indicating that the full freedom of three coefficients is not needed in all climate classes. For the climate classes Af, As, BW and Cs the additive constant k3 leads to no significant improvement. In Cw and E climates the variation of k2 is less important than the additive constant k3 while for climate class Ds the major improvement is due to k2. In these cases, RMSE and MAE of ETHS5 are not significantly lower than for ones of the other calibrations with less freedom. Including the free coefficient k3 as an additive constant, however, leads to an unbiased estimate. This is a major advantage of ETHS5.
Figure 4

Standardized values of BIC for HS and various calibrations of HS.

Figure 4

Standardized values of BIC for HS and various calibrations of HS.

Close modal

Table 3 also presents the coefficients of the calibrated Hargreaves method by Köppen class. It can be seen that the regression coefficients vary widely by Köppen class indicating the importance of optimized coefficients.

The best estimate of the exponent k2 depends strongly on the climate class. Its original value in the Hargreaves approach is 0.5. If all data are used the best fit is k2 = 0.495 confirming that 0.5 is a good choice in general. However, for A climates much lower best-fit values are obtained, ranging from 0.074 for Af over 0.143 for As to 0.333 for Aw climates. This reflects the relatively weak dependence of ET on the daily temperature range (Tx – Tn) in tropical climates. The good performance of ETHS3 in these cases indicates that the inappropriately high value of k2 = 0.5 in the original Hargreaves method is the major source of the relatively large errors for A climates. For E and Df climates best estimates of k2 reach 0.592 and 0.659, respectively, and are therefore considerably higher than the original value of 0.5.

Although BIC values do not indicate that ETHS5 is superior to simpler models in each climate class, we suggest this model for all climate classes with the best-fit coefficient values obtained from our analysis. Aside from providing the lowest estimation error (RMSE and MAE) and the best Ceff, this allows for one generalized formulation for all climate classes.

Adjusted Hargreaves coefficients are usually very site specific. According to Table 3, part of these fluctuations can be attributed to the local climate expressed as Köppen climate class. The separation by climate class is meaningful since it reduces error measures like MAE and RMSE without increasing BIC. Estimates of optimal values for the coefficients k1, k2 and k3 per climate class are provided in Table 3 as well. But are these values significantly different for different climate classes? In order to investigate this question we calculated the 90% confidence interval (5 to 95% range) for each of the coefficients and each climate class. Together with the best estimates they are depicted in Figure 5 and confirm that the separation by climate class is meaningful with respect to the long-term monthly averages used. We therefore recommend using the new HS coefficient values for agroclimatological studies.
Figure 5

Best estimates and 90% confidence intervals (5% and 95%) for the coefficients k1 (upper panel), k2 (middle panel) and k3 (lower panel) by climate class.

Figure 5

Best estimates and 90% confidence intervals (5% and 95%) for the coefficients k1 (upper panel), k2 (middle panel) and k3 (lower panel) by climate class.

Close modal

It should be taken into account, however, that this study is based on the analysis of long-term monthly means. It is important to point out that the results encountered and conclusions drawn might only be valid for planning in general, whereas they might be unsuitable for monitoring applications.

The results show that HS deviates significantly from FAO-56 even for climatic values and that these deviations are climate-class specific. For some purposes that require long-term ET estimates the differences between models may not be significant to justify the extra effort. In tropical climates the differences between modified models are higher and the daily temperature range is not an efficient indicator of ETo in terms of Ceff. In these regions further research should be undertaken for evaluating the validity of other simple methods as suggested by De Pauw (2008).

Long-term monthly means of ET for 4,368 stations worldwide are estimated by the Penman–Monteith model (FAO-56) and several variations of the HS method. The comparison of the results by climate class showed that simple modifications of the HS model with climate-class specific coefficient values lead to significant improvements compared with the un-calibrated HS method. The addition of a constant term yields an unbiased estimator. Calibrating all the coefficients in HS and introducing a new constant term transforms HS into a highly efficient equation for estimating FAO-56 when only temperature data are available. This allows for a wide range of applications.

Considering the problems associated with the availability of meteorological data in the world, the HS temperature-based model is recommended as the most simple and practical method for estimating FAO-56 in the literature. Results obtained from the comparisons of ET estimates by the HS equation and its modifications against FAO-56 throughout different Köppen climate classes showed high variability even for long-term monthly means. For all but tropical climates the results indicate that monthly ET values estimated by the HS method are a suitable approximation of FAO-56 for agro-climatological studies.

In A climates the reduction of estimation errors due to calibration of the HS method is largest. This is most pronounced in the Af climate where MAE is reduced from its original value of 0.663 to 0.335 mm day−1 for ETHS5. However, the low values of Ceff indicate the need for the search of other simple methods for the estimation of ET in tropical climates.

This study strongly supports the use of the calibrated Hargreaves equation ETHS5 at different climatic conditions in the case when only maximum and minimum temperature data are available.

Alexandris
S.
Kerkides
P.
Liakatas
A.
2006
Daily reference evapotranspiration estimates by the ‘Copais’ approach
.
Agric. Water Manage.
82
,
371
386
.
Allen
R. G.
2006
Evaporation modeling: potential
. In:
Encyclopedia of Hydrological Sciences
(
Anderson
M. G.
McDonnell
J. M.
, eds).
Wiley-Blackwell, Chichester
.
Allen
R. G.
Pereira
L. S.
Raes
D.
Smith
M.
1998
Crop evapotranspiration – Guidelines for computing crop water requirements, FAO Irrigation and drainage paper 56. FAO, Rome, Italy, 300
.
Beal
D. J.
2007
Information criteria methods in SAS for multiple linear regression models
.
15th Annual SouthEast SAS Users Group (SESUG) Proceedings
,
4–6 November
,
Hilton Head, South Carolina, USA
,
Paper SA05
.
De Pauw
E.
2008
Climatic and soil datasets for the ICARDA wheat genetic resource collections of the Eurasia region: Explanatory notes. Technical Note, GIS Unit, ICARDA, Syria
.
Gavilán
P.
Lorite
I.
Tornero
S.
Berengena
J.
2006
Regional calibration of Hargreaves equation for estimating reference ET in a semiarid environment
.
Agric. Water Manage.
81
,
257
281
.
Hargreaves
G.
1994
Simplified coefficients for estimating monthly solar radiation in North America and Europe. Department paper, Department of Biological and Irrigation Engineering, Utah State University, Logan, UT, USA
.
Hargreaves
G. H.
Allen
R. G.
2003
History and evaluation of Hargreaves evapotranspiration equation
.
J. Irrig. Drain. Eng.
129
,
53
63
.
Hargreaves
G. H.
Samani
Z. A.
1982
Estimating potential evapotranspiration
.
J. Irrig. Drain. Div.
108
,
225
230
.
Hargreaves
G. H.
Samani
Z. A.
1985
Reference crop evapotranspiration from ambient air temperature
.
Appl. Engin. Agri.
1
(
2
),
96
99
.
Jensen
M. E.
Burman
R. D.
Allen
R. G.
1990
Evapotranspiration and Irrigation Water Requirements
.
ASCE
,
New York
,
USA
.
Köppen
W.
1936
Das geographisca System der Klimate
. In:
Handbuch der Klimatologie (Handbuch der Klimatologie, vol.1: C.)
(
Köppen
W.
Geiger
G.
, eds).
Gebruder Borntraeger
,
Berlin
,
Germany
, p.
44
.
Kottek
M.
Grieser
J.
Beck
C.
Rudolf
B.
Rubel
F.
2006
World map of the Koppen-Geiger climate classification updated
.
Meteorol. Zeitschrift
15
,
259
263
.
López-Urrea
R.
Martín de Santa Olalla
F.
Fabeiro
C.
Moratalla
A.
2006
Testing evapotranspiration equations using lysimeter observations in a semiarid climate
.
Agric. Water Manage.
85
,
15
26
.
Maestre-Valero
J.
Martínez-Alvarez
V.
González-Real
M.
2013
Regionalization of the Hargreaves coefficient to estimate long-term reference evapotranspiration series in SE Spain
.
Span. J. Agric. Res.
11
,
1137
1152
.
Marti
P.
González-Altozano
P.
López-Urrea
R.
Mancha
L.
Shiri
J.
2015
Modeling reference evapotranspiration with calculated targets. Assessment and implications
.
Agric. Water Manage.
149
(
2
),
81
90
.
Moriasi
D.
Arnold
J.
Van Liew
M.
Bingner
R.
Harmel
R.
Veith
T.
2007
Model evaluation guidelines for systematic quantification of accuracy in watershed simulations
.
Trans. ASABE
50
,
885
900
.
Peel
M. C.
Finlayson
B. L.
McMahon
T. A.
2007
Updated world map of the Köppen-Geiger climate classification
.
Hydrol. Earth Syst. Sci. Dis.
4
,
439
473
.
Rahimikhoob
A.
Behbahani
M. R.
Fakheri
J.
2012
An evaluation of four reference evapotranspiration models in a subtropical climate
.
Water Resour. Manage.
26
,
2867
2881
.
Schwarz
G.
1978
Estimating the dimension of a model
.
Ann. Stat.
6
,
461
464
.
Shahidian
S.
Serralheiro
R.
Serrano
J.
Teixeira
J.
2013
Parametric calibration of the Hargreaves–Samani equation for use at new locations
.
Hydrol. Process.
27
,
605
616
.