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J. Appl. Environ. Biol. Sci., 3(6)31-41, 2013 © 2013, TextRoad Publication ISSN: 2090-4215 Journal of Applied Environmental and Biological Sciences www.textroad.com * Corresponding Author: Abolfazl Majnooni-Heris, Department of Water Engineering, Faculty of Agriculture, University of Tabriz, Tabriz, Iran. E-mail [email protected] Evaluate Several Potential Evapotranspiration Methods for Regional Use in Tabriz, Iran Ali Rashid Niaghi 1 , Abolfazl Majnooni-Heris *1 , Davoud Zare Haghi 2 and Ghorban Mahtabi 3 1 Department of Water Engineering, Faculty of Agriculture, University of Tabriz, Tabriz, Iran 2 Department of Soil Sciences, Faculty of Agriculture, University of Tabriz, Tabriz, Iran 3 Department of Water Engineering, Faculty of Agriculture, University of Zanjan, Zanjan, Iran ABSTRACT Accurate evapotranspiration estimates are needed to determine the crop water requirements for the purpose of irrigation scheduling. Numerous methods have been developed for evapotranspiration estimation out of which some techniques have been developed partly in response to availability of data. The Penman-Monteith equation standardized by the Food and Agriculture Organization (FAO56-PM) is accepted as a standard method to estimate ET o . Therefore, the other methods are evaluated by FAO56-PM method results. Nine methods in three groups, which are temperature based methods (Thornthwaite (TH), Hargreaves (HA) and Blaney-Criddle (BC)), solar based method (Priestley-Taylor (PT), Makkink (MA) , R s (Ir- R s ) and R n (Ir- R n ) based methods), and combined methods (Penman (PE) and Penman-FAO24 (PE24)), were used to evaluate with FAO56-PM method to choose the best method for using in research and projects. Performance analysis for the estimated values using climatic data for 7 years (Jan 2003 – Dec 2009) and validation of methods using 2 years climatic data (Jan 2010- Dec 2011) were made. The root mean square error (RMSE) was calculated on a monthly basis. The estimated values by the mentioned methods were all correlated with FAO56-PM having RMSE values were 67.89, 49.45, 36.22, 61.35, 63.98, 58.28, 58.26, 5.48, 23.19 mm/month, respectively. The difference among the nine ET o methods before calibration showed a wide range of variation across the research period about 712 mm/yr. As a result of using the calibrated constant values in the equations, all nine methods are able to estimate monthly values perfectly. The RMSE of methods after validation were 37.16, 21.50,16.67, 27.82, 17.50, 17.70, 32.15, 2.62, 3.70 mm/month, respectively. Investigation shows the closer slope to 1 and intercept to 0 for PE method. However, the worst amounts of slope, intercept, R 2 and RMSE before calibration were belong to MA, BC, IR-R n and TH, respectively. The best output after calibration was belong to the BC method without considering the combined methods, and the TH method had worst results. Although these revised methods increase the accuracy of estimates, FAO56-PM method is preferred if it is applicable due to the complexity of its input parameters. KEYWORDS: Reference evapotranspiration, temperature, radiation, FAO56-PM INTRODUCTION Potential evapotranspiration (ET P ) is a major input in soil water balance models. Although several variations of the definition exist, ET P can be generally defined as the amount of water that could evaporate and transpire from a vegetated landscape without restrictions other than the atmospheric demand (Thornthwaite 1948, Penman, 1948). Potential evapotranspiration is also used as an index to represent the available environmental energies and ecosystem productivity (Currie, 1991). Although the ET P concept has many uses, it has been regarded as a confusing term because the reference evaporation surface, usually the vegetation type, is defined uncertainly (Nokes 1995). Consequently, the ET P concept has been gradually replaced in the past decade by other more narrowly defined terms, such as reference crop evapotranspiration, or surface dependent evapotranspiration (Federer et al. 1996). Accurate evapotranspiration estimation is needed to determine the water requirement of crops for irrigation scheduling. Potential evapotranspiration can be measured directly by lysimeter, but generally, it is estimated by theoretical or empirical equations, or derived simply by multiplying the standard pan evaporation data by a pan coefficient (Grismer et al. 2002). However, field measurement of evapotranspiration is rarely available and actual crop evapotranspiration (ET c ) is usually calculated from estimated reference crop evapotranspiration (ET o ) using the crop factor method, which is calculated by multiplying the reference crop evapotranspiration (ET o ) by a crop coefficient (Kc). ET o is defined as the rate of evapotranspiration from the hypothetical crop with as assumed crop height (12 cm), an albedo of 0.23, and a fixed canopy resistance (70 Sm -1 ) which would closely resemble evapotrasnpiration from an extensive surface of the green grass cover of uniform height actively growing, completely shading the ground and not short of water (Allen et al., 1998). Inaccurate estimation of ETo, and as a result ETc, can lead to inefficient use of water, increase potential for surface and ground water pollution, and reduced for the grower. To overcome inaccurate ETo estimation, there are many methods have been developed, 31

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Page 1: Evaluate Several Potential Evapotranspiration Methods for

J. Appl. Environ. Biol. Sci., 3(6)31-41, 2013

© 2013, TextRoad Publication

ISSN: 2090-4215 Journal of Applied Environmental

and Biological Sciences www.textroad.com

*Corresponding Author: Abolfazl Majnooni-Heris, Department of Water Engineering, Faculty of Agriculture, University of Tabriz, Tabriz, Iran. E-mail [email protected]

Evaluate Several Potential Evapotranspiration Methods for Regional Use in Tabriz, Iran

Ali Rashid Niaghi1, Abolfazl Majnooni-Heris*1, Davoud Zare Haghi2 and Ghorban Mahtabi3

1Department of Water Engineering, Faculty of Agriculture, University of Tabriz, Tabriz, Iran

2Department of Soil Sciences, Faculty of Agriculture, University of Tabriz, Tabriz, Iran 3Department of Water Engineering, Faculty of Agriculture, University of Zanjan, Zanjan, Iran

ABSTRACT

Accurate evapotranspiration estimates are needed to determine the crop water requirements for the purpose of irrigation scheduling. Numerous methods have been developed for evapotranspiration estimation out of which some techniques have been developed partly in response to availability of data. The Penman-Monteith equation standardized by the Food and Agriculture Organization (FAO56-PM) is accepted as a standard method to estimate ETo. Therefore, the other methods are evaluated by FAO56-PM method results. Nine methods in three groups, which are temperature based methods (Thornthwaite (TH), Hargreaves (HA) and Blaney-Criddle (BC)), solar based method (Priestley-Taylor (PT), Makkink (MA) , Rs (Ir- Rs) and Rn (Ir- Rn) based methods), and combined methods (Penman (PE) and Penman-FAO24 (PE24)), were used to evaluate with FAO56-PM method to choose the best method for using in research and projects. Performance analysis for the estimated values using climatic data for 7 years (Jan 2003 – Dec 2009) and validation of methods using 2 years climatic data (Jan 2010- Dec 2011) were made. The root mean square error (RMSE) was calculated on a monthly basis. The estimated values by the mentioned methods were all correlated with FAO56-PM having RMSE values were 67.89, 49.45, 36.22, 61.35, 63.98, 58.28, 58.26, 5.48, 23.19 mm/month, respectively. The difference among the nine ETo methods before calibration showed a wide range of variation across the research period about 712 mm/yr. As a result of using the calibrated constant values in the equations, all nine methods are able to estimate monthly values perfectly. The RMSE of methods after validation were 37.16, 21.50,16.67, 27.82, 17.50, 17.70, 32.15, 2.62, 3.70 mm/month, respectively. Investigation shows the closer slope to 1 and intercept to 0 for PE method. However, the worst amounts of slope, intercept, R2 and RMSE before calibration were belong to MA, BC, IR-Rn and TH, respectively. The best output after calibration was belong to the BC method without considering the combined methods, and the TH method had worst results. Although these revised methods increase the accuracy of estimates, FAO56-PM method is preferred if it is applicable due to the complexity of its input parameters. KEYWORDS: Reference evapotranspiration, temperature, radiation, FAO56-PM

INTRODUCTION

Potential evapotranspiration (ETP) is a major input in soil water balance models. Although several variations of the definition exist, ETP can be generally defined as the amount of water that could evaporate and transpire from a vegetated landscape without restrictions other than the atmospheric demand (Thornthwaite 1948, Penman, 1948). Potential evapotranspiration is also used as an index to represent the available environmental energies and ecosystem productivity (Currie, 1991). Although the ETP concept has many uses, it has been regarded as a confusing term because the reference evaporation surface, usually the vegetation type, is defined uncertainly (Nokes 1995). Consequently, the ETP concept has been gradually replaced in the past decade by other more narrowly defined terms, such as reference crop evapotranspiration, or surface dependent evapotranspiration (Federer et al. 1996). Accurate evapotranspiration estimation is needed to determine the water requirement of crops for irrigation scheduling. Potential evapotranspiration can be measured directly by lysimeter, but generally, it is estimated by theoretical or empirical equations, or derived simply by multiplying the standard pan evaporation data by a pan coefficient (Grismer et al. 2002). However, field measurement of evapotranspiration is rarely available and actual crop evapotranspiration (ETc) is usually calculated from estimated reference crop evapotranspiration (ETo) using the crop factor method, which is calculated by multiplying the reference crop evapotranspiration (ETo) by a crop coefficient (Kc).

ETo is defined as the rate of evapotranspiration from the hypothetical crop with as assumed crop height (12 cm), an albedo of 0.23, and a fixed canopy resistance (70 Sm-1) which would closely resemble evapotrasnpiration from an extensive surface of the green grass cover of uniform height actively growing, completely shading the ground and not short of water (Allen et al., 1998). Inaccurate estimation of ETo, and as a result ETc, can lead to inefficient use of water, increase potential for surface and ground water pollution, and reduced for the grower. To overcome inaccurate ETo estimation, there are many methods have been developed,

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revised and recommended for various types of climatic conditions over the years. Some of these methods need many weather parameters as inputs while others need less. Numerous methods have been developed for evapotranspiration estimation out of which some techniques have been developed partly in response to availability of data. Factors such as data availability, the intended use, and the time scale required by the problem must be considered when choosing the evapotranspiration calculation techniques (Allen et al., 1998).

The FAO Penman-Monteith model, which had presented in FAO-56 paper (FAO56-PM), ranked as the best method for all climatic condition. Allen et al. (1998) also showed that ETo computed using the Penman-Monteith equation yielded estimates close to measured ETo values. Therefore, the FAO56-PM method was confirmed as the standard method for definition and computation of the ETo from grass reference surface. Several other works have confirmed the validity of the Penman-Monteith equation (Howell et al. 1997, Itenfisu 2003 and Alkaeed et al. 2006).

In spite of the advantages of the more physically based Penman method, empirical ETo methods have remained in popular use because of simplicity and the smaller number of input parameters needed for computation. Therefore, these empirical methods should be evaluated to choose a method with good performance and relation with evapotranspiration values. The Hargreaves and Samani (1985) equation is one of the common useful equations among the empirical methods. The method is popular in cases where the availability of data is rare, as it requires only temperature measurement, with extraterrestrial radiation calculated as a function of latitude and day of the year. The Priestly- Taylor (1972), Makkink (1957) and Thornthwaite (1948) are the other empirical methods which have need mean daily temperature and the daytime length.

It is important to compare the performance of empirical methods to FAO56-PM model, therefore, the different methods were compared with FAO56-PM results to reach the best method with good performance which has require less input parameters and significant correlation with FAO56-PM results.

MATERIALS AND METHODS

Materials: This study was carried out at the Tabriz University Agriculture Faculty experimental field, which is named Karkaj, located in the north west of Iran (latitude, longitude and elevation of the station are 38⁰03' N, 46⁰37'E and 1567.3m above mean sea level, respectively). The meteorological data of 7 years at the Karkaj station covering the period of January 2003- December 2009 were analyzed for the purpose of evaluating and revising thenine ETo methods in comparison with the FAO56-PM method. Further, the climatic data covering the period of January 2010- December 2011 were used to validate the performance of revised methods. The climate in the experimental area is terrestrial, summers are mild and dry, and winters are cold and snowy (Majnooni-Heris et al., 2012). The average annual precipitation in study period is 364 mm with 34.5 mm falling during the growing season (July to October), and average temperature is 13.48⁰C. The highest average monthly temperature recorded was 41⁰C in August 2009, while the lowest value was -16.8⁰C in January 2008. The monthly average of the main weather variables for the period of study (Jan 2003-Dec 2009) are given in table 1.

Table (1) Average monthly weather variables for the study period (Jan 2003-Dec 2009)

The soil of the research area has a sandy-loam texture. Theaverage values of field capacity, permanent

wilting point and bulk density of soil in effective root depth are 0.28(m3m-3), 0.125 (m3m-3) and 1.58 g cm-3, respectively. The water holding capacity of the experimental site wasobserved as 140 mm in 0-90 cm profile.

Methods: Nine methods were selected to estimate ETo of the study area to evaluate their performanceby comparing them with the FAO56-PM output. These methods can be divided into three broad groups as three temperature based (Thornthwaite 1948, Blaney-Criddle 1950 and Hargreaves and Samani 1985), four radiation based (Makkink 1957, Priestley-Taylor 1972, and two Irmak et al. (2003) presented equations), and two combined equations (Penman 1948, Penman-FAO24).

FAO56-PM method: The FAO56-PM combined the fixed bulk surface resistance and vapour aerodynamic. It has a strong theoretical basis and can be expressed as below:

퐸푇 =. ∆( )

. ( )

∆ ( . ) (1) where the ETo is the reference evapotranspiration (mm day-1); ∆ is the slope vapour curve (kPa⁰C-1);푇 is the mean daily air temperature (⁰C); U2 is the wind speed at 2 m (m s-1); Rn is the net radiation flux density (MJ m-2

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d-1); G is the soil heat flux density (MJ m-2 d-1); VDP is vapour pressure deficit (kPa) in the atmosphere, and 훾 is the psychrometric constant (kPa⁰C-1).

Temperature based methods

Thornthwaite method (TH): The Thornthwaite method (Thornthwaite 1948) is based on an empirical relationship between ETo and mean air temperature changes. Therefore, this equation can be written as: 퐸푇 = 퐸푇 (2)

퐸푇 = 16( ) (3)

퐼 = ∑ ( ) . (4) where,퐸푇 is the gross evapotranspiration; N is the maximum number of sunny hours in function of the month latitude; 푑 is the number of days per month; 푇 is the mean temperature (⁰C); I is the monthly heat index, and 훼 = 0.49239 + 1792 × 10 퐼 − 771 × 10 퐼 + 675 × 10 퐼 (5)

Hargreaves Method (HA): Hargreaves and Samani (1982, 1985) proposed several improvements for the Hargreaves (1975) equation for estimating grass-related ETo. Because solar radiation data frequently are not available, Hargreaves and Samani (1982, 1985) recommended estimating RS from extraterrestrial radiation, RA, and the difference between mean monthly maximum and minimum temperatures, TD (°C), and Ta is daily mean air temperature (°C), The resulting form of the equation is: 퐸푇 = 0.0023.푅 .푇퐷 . (푇 + 17.8) (6)

The extraterrestrial radiation, RA, is expressed in equivalent evaporation units. For a given latitude and day RA is obtained from tables or may be calculated using a set of equations. The only variable for a given location and time period is air temperature. The Hargreaves method, therefore, has become a temperature based method.

Bleny-Criddle method (BC): This method is one of the simplest methods that were used to calculate ETo. It was widely used before the introduction of Penman-Montieth equation. This method only considers temperature changes at a particular region for measuring ETo. The Blaney-Criddle formula for estimating ETo is as follows: 퐸푇 = 푝(0.46푇 + 8.13) (7) where, 푝 is the mean daily percentage of annual daytime hours due to the latitude region; and 푇 is mean temperature(⁰C).

Solar and temperature based methods

Makkink method (MA): Makkink (1957) proposed a simple method for ETo estimation by using only temperature and radiation parameters as following equation 퐸푇 = 0.61 ∆

∆− 0.012 (8)

where,푅 is the solar radiation of the crop surface (MJ m-2 day-1); ∆ is the slope vapour curve (kPa⁰C-1), 훾 is the psychrometric constant (kPa⁰C-1), and 휆 is the latent heat of vapour(MJkg-1).

Priestley-Taylor (PT): The Priestley and Taylor (1972) were developed as a substitute to the Penman–Monteith equation to remove dependence on observations. Priestley-Taylor found that the actual evaporation is 1.26 times greater than the potential evaporation and hence they replaced the aerodynamic terms with a constant value of 1.26. Consequently, Priestley-Taylor method needs only long-wave radiation and temperature to estimate ETo. which is given below: 퐸푇 = 1.26 (푅 −퐺) (9) where Rn (MJ m-2 day-1) is net radiation, ∆ is the slope vapour curve (kPa⁰C-1), 휆 is the latent heat of vapour(MJkg-1), G is the soil heat flux density (MJ m-2 d-1),훾 is the psychrometric constant (kPa⁰C-1), and 푇 is mean temperature(⁰C).

Rs based method (Rs): (Irmak et al., 2003) 퐸푇 = −0.611 + 0.149푅 + 0.079푇 (10) where Rs (MJ m-2 day-1) is solar shortwave radiation, and 푇 is mean temperature(⁰C).

Rn based method (Rn): (Irmak et al., 2003) 퐸푇 = 0.489 + 0.289푅 + 0.023푇 (11) where Rn (MJ m-2 day-1) is net radiation, and 푇 is mean temperature(⁰C).

Combined methods

Penman(PE) and Penman-FAO24 (PE24): The FAO-24 Penman is a variation form of the Penman method (Doorenbos and Pruitt 1977). The Penman methods combine an energy balance with an expression that describes heat fluxes to derive a method to estimate vapour flux from a vegetated surface. Monteith (1965)

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introduced modifications to the original Penman equation by incorporating a stomatal resistance term resulting in the well-known Penamn-Monteith equation. For a number of years, the FAO-24 Penman method (eq. 12) was used as a standard equation for estimating ETo when all weather data (temperature, humidity, wind, and solar radiation) were available.

)eW)f(u)(e(1

λG)(RW

ρCET da

n

wr

(12)

where W is a temperature and the altitude of the area related weighting factor, f(u) is the wind related function( kg hPa-1m-2d-1); ea is the saturation vapour pressure at mean air temperature, hPa; ed is the mean actual vapour pressure of the air (hPa), and C is an adjustment factor to account for day and night weather conditions.

Statistical analysis Performance of models was evaluated by statistical cross-correlation (R2), and root mean square error

(RMSE). Also the slope and intercept of the nine mentioned methods withFAO56-PM method were calculated and they were comparedwith slope and intercept of 1:1 line (i. e. y=1x+0).

RESULTS AND DISCUSSION

Climate Data: The daily measured precipitation, temperature, relative humidity, actual sunshine hours (n) and estimated short wave (Rs) and net solar radiation (Rn) were shown in figure 1. The daily Rs and Rn values were estimated by the procedures which are presented in the FAO56-paper (Allen et al. 1998). These variables are important for the ETo calculation with FAO56-PM method. The relationship between short wave and net solar radiation indicate the same trend in all years wherein the total solar radiation is doubled of that in the net radiation. The same result has been reached by Alkaeed et al.(2006) for Itoshima Peninsula Area, Fukuoka, Japan Japan .

Figure (1) Input parameters used in ETo calculation with different methods; from left to right precipitation, temperature, solar radiation, relative humidity, net solar radiation, and actual sunshine hours, respectively.

The seven year-daily weather data were used to examine the performances of the commonly used ETo

estimation methods. Figure 2 shows the comparison of monthly ETo values trend which are estimated by the FAO56-PM, temperature based, and combined methods. Although the trends of the estimated ETo are in

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proximity among the applied methods, none of the methods except combined methods show the same results. Seasonal variations in the ETo estimation reflect the differences in the variables applied in each method.

For illustrative purposes, the estimated ETo from the above-mentioned nine methods are plotted against FAO56-PM values for the station Karkaj (Fig.2). The results of combined method are closer to the FAO56-PM outcome. However, the trends of temperature based models have a different result with each other. TH method gives a very small amount of accumulative evapotranspiration in the first months of the year. Lu et al. (2005) reported the same result for Thornthwaite method underestimation for southeastern United States. The HA method gives a closer result in comparison with the FAO56-PM method except for the hot season as the temperature and solar radiation are high; the value of ETo, therefore, increases by increasing the net radiation.

Martinez-Cob and Tejero-Juste (2004) indicated that the calibrated HA ETo method worked well for windy locations under the semiarid conditions in northeastern Spain. The computed values by BC method are similar to HA method and both of them have similar trends in various times. The MA method gives a smaller amount of ETo in comparison with the other solar based methods.

Although solar radiation hasan important effect on ETo values, figure 2 shows that solar based methods don't have an acceptable relation to the FAO56-PM method. The values which are estimated by these types of ETo methods are lower than FAO-PM and temperature based methods outputs. As the MA method, other solar based methods underestimate the value of evapotranspiration in different months of the year. Some of the temperature based methods have an accurate and acceptable output rather than solar based methods in the present study area. Bois et al. (2005) indicated that in semi-arid conditions, radiation based methods don't appear more relevant than temperature based methods. In spite of the temperature based method as TH has an acceptable result for Japan weather condition ( Alkaeed et al. 2006), it hasn't reasonable output for the semi-arid region as the study area. Tukimat et al. (2012) showed the wise versa results in comparison with current research result. They found that BC method had a higher error in comparison with other temperature and radiation based equations in northof Malaysia.

Comparison of the nine mentioned methods were all correlated with FAO56-PM having R2 values and fitted linear equations for all studied methods. This procedure had been used to analyze the monthly reference evapotranspiration values, which are computed by different methods, with FAO56-PM values. The cross-correlation (R2), slope, intercept and root mean square error (RMSE), which is used to rank the methods, between FAO56-PM outputs and the ETo computed using other methods are presented in Table 3.

For statistical analysis, it was assumed that the best methods were those that had the lowest RMSE. The estimated ETo values by the TH, HA, BC, PT, MA, IR-Rs, IR-Rn, PE and PE24 methods were evaluated with FAO56-PM having RMSE values 67.89, 49.45, 36.22, 61.35, 63.98, 58.28, 58.26, 5.48, 23.19 mm/month, respectively. Investigation shows the closer slope to 1 and intercept to 0 for PE method. However, the worst amounts of slope, intercept, R2 and RMSE were belong to MA, BC, IR-Rn and TH, respectively. Dauda and Baiyeri (2011) reported that the TH, PT and PE24 methods yielded the poor correlation with the FAO56-PM values. Nevertheles, they found that the HA and BC method values had the high coefficient of determination (R2) for their condition.

The previous discussion shows that temperature and solar based methods, as used in this study, may be reliable in the areas and over the periods for which they were developed, but large errors, i.e., higher values of intercepts and larger biases of regression slopes, can be expected when they are extrapolated to other climatic areas without recalibrating the constants involved in the formulae. Accordingly, modifications were made to the original equations used here to improve results.

Using the calibrated constant values in the equations, all nine methods are able to estimate monthly values perfectly, with a maximum RMSE of 27.94 (mm/month) in the case of the IR-Rn based method for station Karkaj. The calculated mean monthly evapotranspiration values are also improved significantly for all of the methods in the station (Figure 3). The estimated ETo values by modified TH, HA, BC, PT, MA, IR-Rs, IR-Rn, PE and PE24 methods were evaluated with FAO56-PM having RMSE values 13.58, 15.96, 15.98, 24.06, 21.72, 14.10, 27.94, 2.83, 3.93 mm/month, respectively. Although the amount of modified methods RMSE are improved and some of ranking position is changed, they don't give a confidential result. So, these results should be confirmed by validating with independent meteorological data.

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Figure (2) Comparison of FAO56-PM monthly ETo with different estimation methods

Table (3) Results of comparing the performance of the different methods output with the FAO56-PM in monthly scale.

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Figure (3) Modified methods are plotted against FAO56-PM values

Modified and unmodified trends of nine methods and FAO56-PM method were plotted to compare their

results before and after modification. According to the figure 4, the dash line on each graph shows the modified method and the line shows the unmodified result of each method. The modified methods have a similar amounts and trends with FAO56-PM method.

The annual ETo before and after modification values for each method are shown in Table 4. In the present calculations, the annual sum of ETo estimations based on the temperature as input variable showed the lowest average value among the tested methods having the values ranged from 914 mm yr-1– 1495 mm yr-1, while 1046 mm yr-1– 1199 mm yr-1 for solar based method, respectively. The annual amounts of ETo after modification become closer to the result of FAO56-PM output. The difference among the various ETo methods, which are used for comparison at this study, showed a wide range of variation across the research period about 712 mm/yr. The similar trend of variation was also presented in the previous studies by Amatya et al. (1995), Federer et al. (1996). Lu et al. (2005) reported the differences in six ETo methods across the southeastern United States approximately 500 mm/yr.

In the present study, annual amounts of ETo are more than the reported amounts by Tukimat et al. (2012) in Malaysia and Alkaeed et al. (2006) in Japan. The high evapotranspiration rate could be caused by some local climatic condition in our experimental site. In the semi-arid zone, the rate of evapotranspiration is high (Majnooni-Heris et al. 2011, 2008) and may be associated with advection phenomena in arid and semiarid regions such as Iran (Majnooni-Heris et al 2007).

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Figure (4) Comparison of unmodified and modified methods with each other

Table(4) Total annual estimated ETo given by the different methods covering the 7 years meteorological data

obtained from the Agriculture Faculty station, Tabriz, Iran

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Validation

Nine modified ETo methods were validated by using an independent meterological data. The slope,

intercept, R2 and RMSE are presented in table 5. The table statistical analysis is confirmed the performance of all modified methods to estimate the amount of ETo. According to the previous results on table 3, which shows the ranking of methods before modification, the ranking of methods after validation of modified equations are shown the same ranking for the worst and the best methods. As a result, the TH method has a lowest accuracy as it was depicted among the other methods, previously. Further, the results of validation confirmed that the combined methods have a high accuracy among the temperature and solar based methods. However, because of complexity of combined methods and more required parameters to calculate the amount of ETo, the best method with less number of inputs and high rate of accuracy is BC. The usage of methods are recommended as their ranking on table 5. Combined methods especially the FAO56-PM method are recommended to use for ETo calculation if there are enough meteorological data which combined methods required.

Table (5) Results of modified methods validation in comparison with FAO56-PM in monthly scale.

CONCLUSION

Evapotranspiration is a major controlling factor and large component of the hydrology cycle in arid and semi-arid regions; so, the ETo estimation methods should be used with caution for estimating actual water loss from natural systems. Climate change will affect the hydrological processes mainly through Evapotranspiration. Estimation of ETo is especially important in the context of climate change. The Performance of nine ETo methods were evaluated in this study, and were compared with FAO56-PM output data with aim to guide the researchers and water practitioners in selecting appropriate methods which have closet results for estimating and projecting ETo at Karkaj irrigation scheme in Tabriz, Iran. A methodology based on linear regression and root mean square error (RMSE) has been proposed for evaluating the methods, and the validation are drieved for ranking the methods accuracy. Investigation shows the closer slope to 1 and intercept to 0 for PE method. However, the worst amounts of slope, intercept, R2 and RMSE were belong to MA, BC, IR-Rn and TH models, respectively. The difference among the nine ETo methods before calibration showed a wide range of variation across the research period about 712 mm/yr. The annual sum of ETo estimations based on the temperature as input variable showed the lowest average value among the tested methods having the values ranged from 914 mm yr-1– 1495 mm yr-1, while 1046 mm yr-1– 1199 mm yr-1 for solar based method, respectively. The annual amounts of ETo after modification become closer to the result of FAO56-PM output. As a result of using the calibrated constant values in the equations, all nine methods are able to estimate monthly values perfectly, with a maximum RMSE of 37.15 (mm/month) in the case of the TH method for station Karkaj. The calculated mean monthly evapotranspiration values are also improved significantly for all of the methods in the station. However, the analysis has been performed for monthly estimates of potential evapotranspiration and the obtained results enabled the following conclusion. The combined methods presented excellent performance compared with a FAO56-PM method which is a combined method too. Because the combined methods need various kinds of data for estimation, the empirical methods which are based on temperature and solar radiation were compared to reach the model with good performance. Therefore, the BC method that is the temperature based method gives the best performance in comparison with other temperature based methods. Solar based methods didn't give a good performance like the temperature based methods, but solar radiation and net radiation based methods may be useful in the regions without a sufficient temperature data to estimate. We recommended the use of the FAO56-PM method as much as possible to calculate daily ETo if the local weather station record all the input variables which are necessary for the FAO56-PM model. It is important to compare several empirical methods to

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the FAO56-PM model with records from the closet reference weather station. In some cases, recalibration of empirical coefficients or adding coefficients which are coming from comparing the FAO56-PM model with empirical methods might be useful; nevertheless, the methods should be used to estimate evapotranspiration value as their rank previously.

Acknowledgement The first author thanks Professor V. Bralts of Purdue University for his kind assistance in review and useful comments.

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