SciELO - Scientific Electronic Library Online

 
vol.16 número31Propuesta de plan de mejora para el incremento en el nivel de servicio proporcionado en la Administradora de Fondos para el Retiro PENSIONISSSTEDiseño de una Red de Conocimiento para los docentes del IEMS índice de autoresíndice de materiabúsqueda de artículos
Home Pagelista alfabética de revistas  

Servicios Personalizados

Revista

Articulo

Indicadores

Links relacionados

  • No hay artículos similaresSimilares en SciELO

Compartir


RIDE. Revista Iberoamericana para la Investigación y el Desarrollo Educativo

versión On-line ISSN 2007-7467

RIDE. Rev. Iberoam. Investig. Desarro. Educ vol.16 no.31 Guadalajara jul./dic. 2025  Epub 17-Sep-2025

https://doi.org/10.23913/ride.v16i31.2532 

Scientific articles

Performance and prediction of reference evapotranspiration using seven alternative methods, in the state of Sinaloa, Mexico

Desempeño y predicción de la evapotranspiración de referencia utilizando siete métodos alternativos, en el estado de Sinaloa, México

Desempenho e previsão da evapotranspiração de referência usando sete métodos alternativos no estado de Sinaloa, México

Omar Llanes Cárdenas1  , Conceptualización, Validación, Recursos, Escritura - Preparación del borrador original, Escritura - Revisión y edición, Administración de Proyectos, Adquisición de fondos
http://orcid.org/0000-0001-8362-7607

Mariano Norzagaray Campos2  , Metodología, Investigación, Recursos, Administración de Proyectos, Adquisición de fondos
http://orcid.org/0000-0002-6911-7392

Ernestina Pérez González3  , Análisis Formal, Investigación, Visualización
http://orcid.org/0000-0002-2768-9245

Jeován A. Ávila Díaz4  , Metodología, Supervisión
http://orcid.org/0000-0002-7692-4547

Marco A. Arciniega Galaviz5  , Software, Curación de datos, Visualización
http://orcid.org/0000-0001-8532-7130

1Instituto Politécnico Nacional, Centro Interdisciplinario de Investigación para el Desarrollo Integral Regional, Mexico ollanesc@ipn.mx

2Instituto Politécnico Nacional, Centro Interdisciplinario de Investigación para el Desarrollo Integral Regional, Mexico mnorzagarayc@ipn.mx

3Instituto Politécnico Nacional, Centro Interdisciplinario de Investigación para el Desarrollo Integral Regional, Mexico eperezg@ipn.mx

4Universidad Autónoma de Occidente, Unidad Los Mochis, Mexico jeovan.avila@uadeo.mx

5Universidad Autónoma de Occidente, Unidad Los Mochis, Mexico marco.arciniega@uadeo.mx


Abstract

This study aimed to evaluate the daily performance of seven alternative ETo methods ( EToaltiValidation; the letter i refers to alternative methods) and to predict annual accumulated ETo with the standard method of Penman-Monteith with limited data (EToPMP), in the state of Sinaloa, Mexico. Daily data from 11 weather stations in Sinaloa were obtained for the period 1969-2018 from the National Water Comission and the National Meteorological Service (CONAGUA-SMN), including maximum temperature, minimum temperature, and evaporation (Eva). Additionally, from the San Juan CONAGUA-SMN weather station, the following were obtained: wind speed, mean temperature, incident solar radiation, atmospheric pressure, and relative humidity. The seven alternative ETo methods (EToalti) calculated included: Romanenko (EToRo), Priestley-Taylor (EToPT), McGuinness and Bordne (EToMB), Hargreaves (EToH75), pan evaporation (EToTE), Hargreaves (EToH85), and Oudin (EToOu). The Daily mean ETo using the limited data Penman-Monteith method (EToPM) was also calculated. The mean absolute error (MAE) and the root mean square error (RMSE) between EToPM and the seven EToalti were calculated. Multiple linear and nonlinear regression models were used to predict EToPMP (dependent variable) from the seven EToalti methods (independent variables). In general, the EToalti with the best performance were EToTE (MAE from 0.360 mm day-1 to 2.294 mm day-1 and RMSE from 0.594 mm day−1 to 3.094 mm day-1). EToPT was the only EToalti that contributed to the explanation of all models of EToPMP. The models developed in this study can contribute to improving agricultural irrigation efficiency in Sinaloa, a state considered “the breadbasket of Mexico.”

Keywords: Penman-Monteith reference evapotranspiration; alternative methods; predicting ETo with limited data

Resumen

Este estudio tuvo como objetivo evaluar el desempeño diario de siete métodos alternativos de ETo (EToalti; la letra i se refiere a métodos alternativos) y predecir la ETo acumulada anual con el método estándar de Penman-Monteith con datos limitados (EToPMP), en el estado de Sinaloa, México. Se obtuvieron datos diarios de 11 estaciones meteorológicas en Sinaloa para el período 1969-2018 de la Comisión Nacional del Agua y el Servicio Meteorológico Nacional (CONAGUA-SMN), incluyendo temperatura máxima, temperatura mínima y evaporación (Eva). Además, de la estación meteorológica San Juan de CONAGUA-SMN, se obtuvieron los siguientes datos: velocidad del viento, temperatura media, radiación solar incidente, presión atmosférica y humedad relativa. Los siete métodos alternativos de ETo (EToalti) calculados incluyeron: Romanenko (EToRo), Priestley-Taylor (EToPT), McGuinness y Bordne (EToMB), Hargreaves (EToH75), evaporación en tanque (EToTE), Hargreaves (EToH85) y Oudin (EToOu). También se calculó la ETo media diaria utilizando el método de Penman-Monteith (EToPM), con datos limitados. Se calcularon el error absoluto medio (MAE) y el error cuadrático medio (RMSE) entre EToPM y los siete métodos de EToalti. Se utilizaron modelos de regresión lineal y no lineal multiples para predecir la EToPMP (variable dependiente) a partir de los siete métodos de EToalti (variables independientes). En general, los EToalti con mejor rendimiento fueron EToTE (MAE de 0.360 mm día⁻1 a 2.294 mm día⁻1 y RMSE de 0.594 mm día⁻1 a 3.094 mm día⁻1). La EToPT fue la única EToalti que contribuyó a la explicación de todos los modelos de EToPMP. Los modelos desarrollados en este estudio pueden contribuir a mejorar la eficiencia del riego agrícola en Sinaloa, estado considerado el granero de México.

Palabras clave: evapotranspiración de referencia de Penman-Monteith; métodos alternativos; predicción de ETo con datos limitados

Resumo

Este estudo teve como objetivo avaliar o desempenho diário de sete métodos alternativos de ETo (EToalt_i; a letra i refere-se a métodos alternativos) e prever a ETo cumulativa anual usando o método padrão de Penman-Monteith com dados limitados (EToPMP), no estado de Sinaloa, México. Dados diários foram obtidos de 11 estações meteorológicas em Sinaloa para o período de 1969 a 2018 da Comissão Nacional de Águas e do Serviço Meteorológico Nacional (CONAGUA-SMN), incluindo temperatura máxima, temperatura mínima e evaporação (Eva). Além disso, os seguintes dados foram obtidos da estação meteorológica de San Juan da CONAGUA-SMN: velocidade do vento, temperatura média, radiação solar incidente, pressão atmosférica e umidade relativa. Os sete métodos alternativos de ETo (EToalt_i) calculados incluíram: Romanenko (EToRo), Priestley-Taylor (EToPT), McGuinness e Bordne (EToMB), Hargreaves (EToH75), evaporação em tanque (EToTE), Hargreaves (EToH85) e Oudin (EToOu). A ETo média diária também foi calculada usando o método de Penman-Monteith (EToPM), com dados limitados. O erro absoluto médio (MAE) e a raiz do erro quadrático médio (RMSE) entre EToPM e os sete métodos EToalt_i foram calculados. Modelos de regressão linear múltipla e não linear foram usados para prever EToPMP (variável dependente) a partir dos sete métodos EToalt_i (variáveis independentes). No geral, os EToalt_i com melhor desempenho foram os EToTE (MAE de 0,360 mm dia⁻1 a 2,294 mm dia⁻1 e RMSE de 0,594 mm dia⁻1 a 3,094 mm dia⁻1). O EToPT foi o único EToalt_i que contribuiu para a explicação de todos os modelos EToPMP. Os modelos desenvolvidos neste estudo podem contribuir para a melhoria da eficiência da irrigação agrícola em Sinaloa, um estado considerado o celeiro do México.

Palavras-chave: Evapotranspiração de referência de Penman-Monteith; métodos alternativos; predição de ETo com dados limitados

Introduction

Reference evapotranspiration (ETo) is an essential variable for hydrological modeling and design of agricultural irrigation (Matsui & Osawa, 2023; Kim et al., 2024), especially under conditions of limited data availability and prevailing drought (Elbeltagi et al., 2022; Fang et al., 2024; Matimolane et al., 2024; Sutanto et al., 2024). ETo “is the evapotranspiration rate of a hypothetical reference crop 12 cm tall and growing under optimal water conditions” (Kim et al., 2024; Skhiri et al., 2024). At the global level and when all observed variables are available, the standard method for estimating ETo is Penman-Monteith FAO-56 (EToPMO; Raja et al., 2024). However, due to the large number of variables required for its calculation, ETo is usually estimated using alternative methods (EToalti; Song et al., 2018).

One of the EToalti (the letter i refers to alternative methods) that is recommended in the growth stage of agricultural crops (Celestin et al., 2020; Uzunlar & Dis, 2024) is Romanenko (EToRo; Romanenko, 1961), cited by Vásquez et al. (2011). On the other hand, many authors, e.g., Gao et al. (2017), Celestin et al. (2020), Raja et al. (2024) and Uzunlar & Dis (2024), recommend the use of the Priestley-Taylor method (EToPT; Priestley & Taylor, 1972) due to its high sensitivity and consistency under semi-arid climate conditions. Also, because they only use the variables of mean air temperature (Tmean) and extraterrestrial solar radiation (Ra), the McGuinness and Bordne (EToMB; McGuinness & Bordne, 1972) and Oudin (EToOu; Oudin et al., 2005) methods can be a good alternative for measuring ETo. The above is particularly reliable when a good performance is desired (Vásquez et al., 2011; Yang et al., 2021; Li et al., 2024) highlighting the practical necessity of simplified methods. According to Matimolane et al. (2024), Raja et al. (2024) and Uzunlar et al. (2024), the Hargreaves method (Hargreaves, 1975; Hargreaves & Samani, 1985; Hargreaves et al., 2003) is a widely used EToalti (EToH75 and EToH85) worldwide, because it is an excellent alternative when the only variables available are Tmean, maximum temperature (Tmax), and minimum temperature (Tmin). However, when only evaporation (Eva) data are available, Usta (2024) recommends the pan-evaporation method (EToTE), which offers acceptable accuracy, low cost, and operational simplicity. The seven EToalti listed above are widely used in under constraints typical of developing countries, such as Mexico, mainly because weather stations usually present three limitations: a) small number of measured variables, b) high percentage of missing data and c) nonhomogeneity of the climate series. These three limitations are not foreign to Sinaloa, which is an eminently agricultural state and has a mostly semi-arid climate (Llanes et al., 2022), so strategies must be developed to calculate EToPMO using the limited data available (EToPM).

In this study, through the National Water Commission and the National Meteorological Service (CONAGUA-SMN, 2024a), daily data on Tmax, Tmin and Eva were obtained for 11 weather stations in Sinaloa (period 1969-2018). Once the series of series of Tmax, Tmin, and Eva were homogenized, Tmean was computed. Next, ETo was calculated by means of each of the seven EToalti described in the second paragraph of this introduction. Based on the equations proposed by Allen et al. (1998), EToPM was also calculated. Using the mean absolute error (MAE) and the root mean square error (RMSE), the average daily performance of the seven EToalti was calculated. For the MAE and RMSE, the variables were EToPM vs EToalti (i=1,…,7). After calculating the annual cumulated value of EToPM at the 11 weather stations, the predicted annual cumulated value of EToPM [EToPMP (dependent variable)] was modeled using multiple linear and nonlinear regressions, where the seven EToalti acted as independent variables. The 11 models of EToPMP were validated using the three tests recommended by Llanes et al. (2022): a) normality of residuals, b) linearity and fit, and c) homogeneity of residuals. Due to the small number of weather stations, EToPM was validated at only one weather station. This validation consisted of finding a significant Pearson and Spearman correlations in the daily data (Out of sample data) for the year 2008 between EToPM (Mocorito station) and EToPMO (San Juan station).

The goal of the study was to evaluate the performance of seven EToalti and predict EToPMP in the state of Sinaloa, Mexico.

The 11 EToPMP models developed in this study offer a reliable tool for quantifying crop water requirements in Sinaloa (Sutanto et al., 2024). This represents a valuable contribution to sustainable agricultural water management in semi-arid regions (Llanes et al., 2022; Satpathi et al., 2024).

Materials and methods

Study area

This study was carried out in the state of Sinaloa, located in northwestern Mexico (Figure 1). Although the state covers only 2.9% of the area of Mexico, it is considered the largest producer of vegetables and grains (CODESIN, 2023), hence, it is commonly referred to as “the breadbasket of Mexico” (Galindo & Alegría, 2018). According to Flores et al. (2012), the climate conditions of Sinaloa range from dry and semi-dry in the coastal plain to temperate and semi-warm-subhumid in the mountain range. Tmean (semi-sum of Tmax and Tmin) ranges mostly from 14.0°C to 26.0°C. The study uses data from 11 weather stations: Culiacán, El Playón, Guatenipa, Ixpalino, La Cruz, Mocorito, Sanalona II, Rosario, Santa Cruz de Alaya, Siqueros and Surutato. An additional station, San Juan was used for validation of the results of Mocorito station (Figure 1).

Source: Authors, following database https://smn.conagua.gob.mx/es/climatologia/informacion-climatologica/informacion-estadistica-climatologica and https://smn.conagua.gob.mx/tools/GUI/sivea_v3/sivea.php).

Figure 1 Geographic location of the 11 principal weather stations and 1 weather station for validation, in the state of Sinaloa, Mexico. 

Data

Daily data on Tmax, Tmin and Eva were obtained from the 11 weather stations for the period 1969-2018. Provided by (CONAGUA-SMN, 2024a): https://smn.conagua.gob.mx/es/climatologia/informacion-climatologica/informacion-estadistica-climatologica. CONAGUA-SMN (2024b) also provided data for the year 2008 from San Juan station (located approximately 7.7 km from the Mocorito station): https://smn.conagua.gob.mx/tools/GUI/sivea_v3/sivea.php. The sub-hourly series (every 10 minutes) of data provided for San Juan station were wind speed at a height of 10 m (Uz), observed mean temperature (TmeanO), observed incident solar radiation (SRR), observed atmospheric pressure (PatmO), and observed relative humidity (RHO).

Data quality control

The following quality controls were applied to the daily series of Tmax, Tmin and Eva:

  1. To improve the statistical confidence of the results, weather stations containing at least 50 years of available data were chosen.

  2. The missing days were filled in (it was verified that all series recorded 18,262 days); that is, 38 normal years and 12 leap years. The percentages of missing data for the 11 weather stations ranged from Tmax = 0.51% (Culiacán) to Tmax = 32.81% (Surutato); from Tmin = 0.57% (Culiacán) to Tmin = 32.82% (Surutato) and from Eva = 1.27% (Sanalona II) to Eva = 100% (Mocorito).

  3. It was verified that Tmax > Tmin and that Eva ≥ 0.

  4. Missing daily data were imputed using the method of interpolation of standardized neighboring series (Kennedy et al., 2023).

  5. The daily climate series were homogenized using the standard normal homogenization test (SNHT) (Alexandersson, 1986; Perčec et al., 2023).

Items d and e were done with the climatol package, version 4.1.0 (https://cran.r-project.org/web/packages/climatol/climatol.pdf), developed by Guijarro (2024). After quality control, Tmean was calculated from Tmax and Tmin.

The sub-hourly series from the San Juan station were subjected to three quality controls:

  1. The missing days were filled in. Since 2008 is a leap year, it was verified that each series contained 52,704 data points, that is, 366 days. The percentages of missing data from the San Juan station were: Uz = 41.47%, TmeanO = 41.49%, SRR = 65.88%, PatmO = 41.48% and RHO = 41.49%.

  2. Using the multiple imputation technique (Rubin, 2004; Remiro et al., 2024), missing data were imputed.

  3. The daily average of each series was then calculated.

Reference evapotranspiration methods (ETo)

In table 1 are mentioned seven alternative methods and the standard method. These eight methods are widely used in scientific literature due to their simplicity and effectiveness.

Table 1 Reference evapotranspiration methods (ETo) (translation). Source: Authors. 

Formulation Method Citations
EToRo=4.51+Tmean2521-eaes
,
Romanenko Romanenko (1961); Vásquez et al. (2011); Li et al. (2024) (1)
EToPT=1.26+γ Rn-Gλ
,
Priestley-Taylor Penman (1948); Priestley-Taylor (1972); Sentelhas et al. (2010) (2)
EToMB=RaTmean+568
,
McGuinness Bordne McGuinness Bordne (1972); Vásquez et al. (2011) (3)
EToH75=0.0135(Tmean+17.78)SR
,
Hargreaves 1975 Hargreaves (1975); Hargreaves et al. (2003) (4)
EToTE=Eva kp
,
Pan-evaporation Doorembos & Pruitt (1977); Chávez et al. (2013) (5)
EToH85=0.0023RaTmean+17.78Tmax-Tmin0.5,
Hargreaves 1985 Hargreaves & Samani (1985); Hargreaves et al. (2003) (6)
EToOu=RaTmean+5100
,
Oudin Oudin et al. (2005) (7)
EToPM=0.408Rn-G+γ900Tmean+273U2(es-ea)+γ(1+0.34U2)
,
Penman-Monteith (standard method) Allen et al. (1998); Sentelhas et al. (2010) (8)

Tmean = mean temperature (°C), ea = actual vapor pressure (kPa), es = saturation vapor pressure (kPa), ∆ = slope of the saturated vapor pressure curve (kPa °C-1), γ = psychrometric constant (kPa °C-1), Rn = net radiation (MJ m-2 day-1), G = soil heat flux density (MJ m-2 day-1, null when working at the daily scale), λ = latent heat of vaporization (2.45 MJ kg-1), SR = calculated incident solar radiation (MJ m-2 day-1), Ra = extraterrestrial solar radiation (MJ m-2 day-1), Tmax = maximum temperature (°C), Eva = evaporation of water from the pan (placed in a dry fallow area; mm day-1), kp = tabulated adjustment coefficient and U2 = daily wind speed at a height of 2 m (m s-1).

In this study U2 = 2 m s-1 was applied because it is a value recommended by Allen et al. (1998), when observed data are not available. In addition, the same value of U2 was also obtained for 2000 weather stations around the world (Allen et al., 1998; cited by Córdova et al., 2015). Finally, many authors; for example, Lin et al. (2022), Varga et al. (2022) and Yonaba et al. (2023), point out that U2 has a marginal impact on the value of EToPM compared to Tmean and SR.

Performance metrics between the seven alternative methods (EToalti) and the Penman-Monteith method with limited data (EToPM)

Mean absolute error (MAE) and root mean square error (RMSE)

Using two performance metrics, mean absolute error (MAE; Equation 9) and root mean square error (RMSE; Equation 10), the performance of the seven EToalti was evaluated using two metrics: MAE and RMSE.

MAE=1n i=1n EToalti-EToPMi (9)

RMSE=1n i=1n EToalti-EToPMi2 (10)

As: MAE = mean absolute error (mm day-1), RMSE = root mean square error (mm day−1), EToalti = reference evapotranspiration for alternative method i (mm day-1), and EToPMi = Penman-Monteith reference evapotranspiration with limited data (mm day-1).

Predictive models of Penman-Monteith annual cumulative reference evapotranspiration with limited data (EToPMP)

First, the annual cumulative value of EToPM was calculated. Multiple linear and non-linear regressions were applied to all series of EToPM. The annual cumulative EToPM values were modeled as EToPMP (dependent variable) and the seven EToalti were the independent variables.

Validation

Predictive models of Penman-Monteith annual cumulative reference evapotranspiration with limited data (EToPMP)

The following validations were applied to the residuals of all multiple regressions (linear and non-linear):

  1. Normality: the Shapiro-Wilk test was applied to the residuals of the linear regressions.

  2. If the residuals of the linear regressions were normal, the model was considered validated, otherwise, a non-linear regression (square polynomial) was applied.

  3. Homogeneity: the nullity of the averages of the residuals of all regressions (linear and non-linear) was verified.

  4. Linearity and fit: a correlation hypothesis test was applied based on Equations 11 and 12 to assess goodness of fit. All linear regressions showed linearity: Pearson correlation (Pr) (Pearson critical correlation (|Pcr|) [(|Pcr| = 0.279; n = 50)]. All non-linear regressions showed good fit: Spearman correlation (Sr) ( Spearman critical correlation ((Scr() [(|Scr| = 0.280; n = 50)]. In all models, Pr and Sr were obtained using √R2.

H0:PrPcrand SrScrPr, Sr0 (11)

H1:Pr>Pcrand Sr<ScrPr, Sr=0 (12)

Penman-Monteith daily reference evapotranspiration with limited data (EToPM)

At San Juan station, using Equation 13, the average daily wind speed was determined at a height of 2 m.

U2=Uz4.87ln67.8z-5.42, 13

where: Uz = average daily wind speed measured at a height of 10 m (m s-1) and z = measurement height of Uz (m).

Because San Juan station also presented PatmO and RHO data, the observed saturation vapor pressure (ess) was calculated with Equation 14, respectively:

ess=ea(100)RHO, (14)

As: ess = observed saturation vapor pressure (kPa) and RHO = observed relative humidity (%).

Finally, for the San Juan station data, a dispersion analysis was applied between EToPM vs EToPMO (Equation 15). After a normality analysis, it was found that Pr ( (Pcr( (|Pcr| = 0.103; n = 366 for the year 2008).

EToPMO=0.408Rn-G+γO900TmeanO+273U2(ess-ea)+γO(1+0.34U2), (15)

As: EToPMO = Penman-Monteith observed reference evapotranspiration (mm day-1) and TmeanO = observed mean temperature (°C).

Software used and significance of statistical analysis

The following software packages were used to perform statistical analyses and visualization: Office 365, XLstat version 2024, RStudio version 2023.12.1 build 402, Past 4.02 and CorelDRAW version 2019.

All statistical analyses were performed with a statistical significance of α = 0.05.

Results

Variation of maximum (Tmax), minimum (Tmin) and mean (Tmean) temperatures, and evaporation (Eva)

According to the data (table 2), the average daily maximum temperature (Tmax) ranged from 24.995 °C in Surutato to 34.633 °C in Guatenipa. The absolute maximum reached 47.000 °C (Guatenipa), while the lowest recorded maximum was 37.500 °C (Surutato). Regarding minimum temperatures (Tmin), the average values varied from 7.257 °C (Surutato) to 19.545 °C (Culiacán), with extremes ranging from -6.000 °C (Surutato and El Playón) to 2.000 °C (Culiacán). The mean temperature (Tmean) averaged between 16.126 °C (Surutato) and 26.230 °C (Culiacán). For evaporation (Eva), the average values ranged from 3.976 mm (Surutato) to 6.648 mm (El Playón), with monthly extremes between 0.000 mm and 17.900 mm.

Table 2 Maximum, minimum, and average daily values for Tmax, Tmin, Tmean (°C) and Eva (mm), for the period 1969-2018.  

Weather station Statistical inference Tmax (°C) Tmin (°C) Tmean (°C) Eva (mm)
Culiacán Average 32.921 19.545 26.230 5.769
maximum 46.000 30.000 36.700 17.900
Minimum 15.500 2.000 11.000 0.000
El Playón Average 31.361 16.863 24.112 6.648
maximum 45.500 37.000 38.000 17.800
Minimum 13.000 -6.000 8.750 0.100
Guatenipa Average 34.633 17.789 26.211 4.890
maximum 47.000 30.000 36.500 14.700
Minimum 15.000 0.500 11.500 0.000
Ixpalino Average 34.229 17.318 25.774 4.878
maximum 46.000 28.500 34.250 17.400
Minimum 18.000 -1.200 11.400 0.100
La Cruz Average 30.299 17.447 23.872 4.409
maximum 42.000 33.000 34.500 18.000
Minimum 12.000 0.000 9.100 0.000
Mocorito Average 32.971 17.318 25.144 No value
maximum 45.000 32.000 37.500 No value
Minimum 9.000 0.000 6.250 No value
Sanalona II Average 33.872 15.847 24.860 5.464
maximum 44.000 28.500 35.000 17.800
Minimum 17.000 -5.000 8.250 0.000
Rosario Average 32.659 18.735 25.697 4.810
maximum 41.000 31.000 35.000 16.600
Minimum 17.000 1.400 12.750 0.000
Santa Cruz de Alaya Average 32.476 17.763 25.118 5.543
maximum 43.000 34.000 37.000 15.400
Minimum 13.400 1.000 11.800 0.000
Siqueros Average 33.907 17.958 25.932 4.746
maximum 43.000 28.500 34.500 14.600
Minimum 17.000 -0.500 11.000 0.000
Surutato Average 24.995 7.257 16.126 3.976
maximum 37.500 20.500 27.500 12.500
Minimum 9.000 -6.000 2.300 0.000

Source: Authors, following database (https://smn.conagua.gob.mx/es/climatologia/informacion-climatologica/informacion-estadistica-climatologica).

Average daily reference evapotranspiration (ETo) estimated using seven alternative methods (EToalti) and the Penman-Monteith method with limited data (EToPM)

The values of ETo (table 3) estimated by the seven alternative methods (EToalti) exhibited seasonal variation. For example, EToH85 ranged from 2.987 mm day-1 (December in La Cruz) to 7.798 mm day-1 (May in Guatenipa), while EToH75 varied between 2.806 and 6.877 mm day-1 in the same periods. The Priestley-Taylor method (EToPT) presented values from 1.920 mm day-1 to 6.767 mm day-1. EToTE values ranged from 1.521 to 6.554 mm day-1. McGuinness and Bordne (EToMB) reached a maximum of 8.710 mm day-1 (June in Guatenipa), and Romanenko (EToRo) recorded the highest values overall, with up to 10.972 mm day-1. The standard Penman-Monteith method with limited data (EToPM) ranged from 2.071 to 4.321 mm day-1.

Table 3 Average daily reference evapotranspiration (ETo) estimated using seven alternative methods (EToalti) and the Penman-Monteith method with limited data (EToPM), for the period 1969-2018 (mm day-1).  

Weather station Average reference evapotranspiration (mm day-1) 1969-2018 (mm day-1)
Month EToPM EToH85 EToH75 EToPT EToTE EToMB EToRo EToOu
Culiacán Jan 2.196 3.245 3.047 2.317 2.190 3.668 6.363 2.494
Feb 2.467 4.040 3.794 3.180 2.895 4.491 6.792 3.054
Mar 2.854 5.064 4.756 4.246 3.990 5.545 7.484 3.771
Apr 3.219 6.031 5.664 5.264 4.935 6.719 8.088 4.569
May 3.413 6.564 6.164 5.889 5.647 7.781 8.317 5.291
Jun 3.078 6.108 5.736 5.717 5.835 8.501 7.085 5.781
Jul 2.923 5.885 5.527 5.553 4.775 8.497 6.642 5.778
Aug 2.724 5.483 5.149 5.156 4.224 8.063 6.298 5.483
Sep 2.488 4.843 4.548 4.482 3.751 7.248 6.038 4.928
Oct 2.601 4.497 4.223 3.843 3.529 5.975 7.097 4.063
Nov 2.397 3.682 3.458 2.776 2.680 4.429 7.066 3.011
Dec 2.112 3.047 2.861 2.109 1.996 3.537 6.283 2.405
El Playón Jan 2.298 3.199 3.004 2.094 2.614 3.197 6.428 2.174
Feb 2.553 3.981 3.739 2.957 3.304 3.946 6.819 2.683
Mar 2.866 4.939 4.638 4.007 4.413 4.931 7.341 3.353
Apr 3.070 5.747 5.397 4.961 5.425 6.088 7.593 4.140
May 3.273 6.326 5.941 5.606 6.211 7.074 7.932 4.810
Jun 2.847 5.813 5.460 5.429 6.554 8.021 6.564 5.454
Jul 2.722 5.625 5.283 5.346 5.527 8.304 6.125 5.647
Aug 2.621 5.349 5.023 5.060 4.979 7.943 6.027 5.402
Sep 2.470 4.819 4.526 4.464 4.411 7.110 6.020 4.835
Oct 2.585 4.440 4.170 3.736 4.142 5.664 7.075 3.851
Nov 2.524 3.692 3.467 2.612 3.192 4.032 7.320 2.742
Dec 2.263 3.053 2.867 1.920 2.483 3.131 6.523 2.129
Guatenipa Jan 2.596 3.578 3.360 2.331 1.785 3.618 7.677 2.460
Feb 2.999 4.589 4.309 3.379 2.476 4.584 8.479 3.117
Mar 3.544 5.877 5.520 4.682 3.498 5.819 9.570 3.957
Apr 4.040 7.102 6.670 5.971 4.530 7.200 10.506 4.896
May 4.321 7.798 7.323 6.767 5.260 8.275 10.972 5.627
Jun 3.906 7.299 6.855 6.604 4.891 8.710 9.640 5.923
Jul 3.141 6.304 5.921 5.861 3.516 8.149 7.611 5.541
Aug 2.898 5.834 5.479 5.417 3.050 7.680 7.144 5.223
Sep 2.724 5.222 4.904 4.733 2.715 6.897 7.065 4.690
Oct 2.955 4.898 4.600 3.986 2.527 5.661 8.442 3.850
Nov 2.815 4.032 3.786 2.801 2.055 4.244 8.482 2.886
Dec 2.462 3.316 3.115 2.096 1.599 3.451 7.460 2.346
Ixpalino Jan 2.906 3.859 3.624 2.449 1.862 3.721 8.171 2.530
Feb 3.257 4.787 4.495 3.418 2.445 4.526 8.739 3.077
Mar 3.676 5.894 5.535 4.569 3.271 5.513 9.430 3.749
Apr 3.993 6.876 6.458 5.653 4.062 6.629 9.966 4.508
May 4.058 7.323 6.877 6.274 4.801 7.623 10.032 5.184
Jun 3.479 6.648 6.243 6.047 4.715 8.354 8.329 5.681
Jul 3.109 6.157 5.782 5.716 3.657 8.284 7.291 5.633
Aug 2.855 5.690 5.344 5.289 3.160 7.862 6.775 5.346
Sep 2.616 5.049 4.742 4.627 2.884 7.105 6.475 4.831
Oct 2.842 4.794 4.502 4.013 2.767 5.938 7.803 4.038
Nov 2.933 4.191 3.936 2.958 2.221 4.469 8.546 3.039
Dec 2.755 3.609 3.389 2.252 1.715 3.631 8.015 2.469
La Cruz Jan 2.143 3.162 2.969 2.206 1.625 3.382 5.990 2.300
Feb 2.365 3.878 3.642 3.003 2.114 4.062 6.305 2.762
Mar 2.624 4.732 4.444 3.956 2.93 4.987 6.715 3.391
Apr 2.862 5.516 5.181 4.837 3.658 6.015 7.073 4.090
May 2.909 5.863 5.506 5.318 4.264 7.001 7.019 4.761
Jun 2.504 5.312 4.988 5.054 4.583 7.833 5.669 5.327
Jul 2.415 5.154 4.840 4.951 3.884 7.996 5.358 5.437
Aug 2.368 4.991 4.688 4.763 3.393 7.667 5.386 5.213
Sep 2.221 4.50 4.226 4.224 3.036 6.949 5.307 4.726
Oct 2.276 4.135 3.883 3.615 2.734 5.727 6.062 3.894
Nov 2.252 3.539 3.324 2.695 2.089 4.258 6.490 2.895
Dec 2.071 2.987 2.806 2.041 1.521 3.339 5.959 2.271

Source: Authors.

For the remaining stations, similar seasonal variations were observed (table 4). EToH85 ranged from 2.533 to 7.494 mm day-1, and EToH75 from 2.379 to 7.038 mm day-1, both in Surutato and Sanalona II, respectively. EToPT values reached up to 6.338 mm day-1, while EToTE remained below 5.396 mm day-1. EToRo and EToMB continued to show the highest estimates, reaching up to 10.390 and 8.553 mm day-1, respectively. Notably, the Mocorito station lacked Eva data for the entire study period (1969-2018), limiting the use of EToTE at that site.

Table 4 Average daily reference evapotranspiration (ETo) estimated using seven alternative methods (EToalti) and the Penman-Monteith method with limited data (EToPM) for the period 1969-2018 (mm day-1; continuation).  

Weather station Average reference evapotranspiration (mm day-1) 1969-2018 (mm day-1)
Month EToPM EToH85 EToH75 EToPT EToTE EToMB EToRo EToOu
Mocorito Jan 2.350 3.263 3.064 2.135 No value value 3.319 6.675 2.257
Feb 2.694 4.142 3.890 3.050 No value 4.137 7.285 2.813
Mar 3.228 5.366 5.039 4.261 No value 5.261 8.366 3.577
Apr 3.698 6.525 6.128 5.450 No value 6.509 9.258 4.426
May 3.969 7.223 6.783 6.238 No value 7.69 9.756 5.229
Jun 3.594 6.806 6.391 6.190 No value 8.553 8.551 5.816
Jul 3.107 6.160 5.785 5.747 No value 8.422 7.213 5.727
Aug 2.832 5.642 5.299 5.256 No value 7.888 6.673 5.364
Sep 2.687 5.098 4.788 4.640 No value 7.066 6.705 4.805
Oct 2.700 4.554 4.277 3.796 No value 5.685 7.440 3.866
Nov 2.532 3.703 3.477 2.639 No value 4.123 7.407 2.804
Dec 2.242 3.039 2.854 1.932 No value 3.214 6.537 2.186
Sanalona II Jan 2.925 3.728 3.501 2.246 1.928 3.417 7.996 2.323
Feb 3.273 4.665 4.381 3.233 2.598 4.219 8.590 2.869
Mar 3.706 5.816 5.462 4.433 3.570 5.251 9.354 3.571
Apr 4.103 6.934 6.512 5.622 4.542 6.455 10.136 4.389
May 4.221 7.494 7.038 6.338 5.396 7.530 10.390 5.120
Jun 3.64 6.872 6.453 6.185 5.339 8.329 8.786 5.663
Jul 3.187 6.279 5.897 5.794 4.027 8.234 7.534 5.599
Aug 2.925 5.790 5.437 5.345 3.629 7.790 7.011 5.297
Sep 2.711 5.156 4.842 4.667 3.233 6.998 6.810 4.759
Oct 2.967 4.863 4.567 3.942 2.945 5.686 8.210 3.866
Nov 3.022 4.136 3.884 2.755 2.298 4.144 8.654 2.818
Dec 2.796 3.49 3.277 2.034 1.767 3.312 7.892 2.252
Rosario Jan 2.442 3.601 3.382 2.546 1.924 3.904 7.030 2.655
Feb 2.796 4.468 4.196 3.421 2.439 4.669 7.635 3.175
Mar 3.181 5.467 5.134 4.451 3.328 5.577 8.267 3.793
Apr 3.465 6.320 5.935 5.391 4.058 6.602 8.687 4.490
May 3.469 6.617 6.214 5.867 4.685 7.534 8.516 5.123
Jun 2.987 5.978 5.614 5.566 4.676 8.137 6.973 5.533
Jul 2.695 5.575 5.236 5.276 3.864 8.075 6.159 5.491
Aug 2.497 5.200 4.884 4.927 3.525 7.703 5.755 5.238
Sep 2.235 4.559 4.282 4.287 3.199 7.000 5.322 4.760
Oct 2.339 4.273 4.013 3.776 2.870 5.991 6.189 4.074
Nov 2.412 3.812 3.580 2.968 2.308 4.659 6.998 3.168
Dec 2.300 3.362 3.157 2.372 1.816 3.847 6.809 2.616
Santa Cruz de Alaya Jan 2.374 3.403 3.196 2.329 2.394 3.645 6.847 2.479
Feb 2.638 4.205 3.949 3.201 3.031 4.433 7.239 3.014
Mar 3.034 5.246 4.926 4.285 3.932 5.452 7.932 3.707
Apr 3.425 6.253 5.872 5.335 4.789 6.551 8.615 4.455
May 3.600 6.787 6.374 5.963 5.366 7.492 8.869 5.095
Jun 3.242 6.35 5.963 5.819 5.185 8.146 7.714 5.539
Jul 2.886 5.861 5.504 5.472 4.073 8.021 6.733 5.454
Aug 2.619 5.367 5.040 5.024 3.634 7.587 6.170 5.159
Sep 2.413 4.762 4.472 4.384 3.296 6.843 5.944 4.653
Oct 2.660 4.555 4.278 3.825 3.205 5.732 7.295 3.898
Nov 2.603 3.859 3.624 2.806 2.801 4.339 7.629 2.950
Dec 2.324 3.229 3.032 2.144 2.259 3.537 6.874 2.405
Siqueros Jan 2.752 3.828 3.595 2.557 2.056 3.870 7.867 2.632
Feb 3.081 4.703 4.417 3.470 2.513 4.637 8.365 3.153
Mar 3.463 5.728 5.380 4.541 3.232 5.557 8.950 3.779
Apr 3.795 6.672 6.265 5.557 3.887 6.597 9.490 4.486
May 3.829 7.048 6.619 6.108 4.450 7.531 9.462 5.121
Jun 3.307 6.424 6.033 5.891 4.353 8.263 7.876 5.619
Jul 3.044 6.066 5.697 5.649 3.500 8.243 7.124 5.605
Aug 2.863 5.707 5.359 5.305 3.093 7.868 6.794 5.351
Sep 2.631 5.087 4.777 4.664 2.883 7.131 6.504 4.849
Oct 2.750 4.739 4.451 4.040 2.749 6.042 7.496 4.109
Nov 2.788 4.143 3.890 3.053 2.313 4.632 8.163 3.150
Dec 2.601 3.579 3.362 2.373 1.953 3.795 7.681 2.581
Surutato Jan 1.941 2.651 2.490 1.750 1.356 2.086 5.081 1.418
Feb 2.177 3.376 3.171 2.614 1.883 2.669 5.529 1.815
Mar 2.472 4.303 4.041 3.688 2.613 3.462 6.137 2.354
Apr 2.85 5.372 5.045 4.828 3.342 4.485 7.018 3.050
May 3.035 6.066 5.697 5.565 3.982 5.471 7.620 3.721
Jun 2.640 5.753 5.403 5.471 3.866 6.345 6.803 4.315
Jul 2.137 5.022 4.716 4.972 2.802 6.227 5.403 4.234
Aug 2.103 4.83 4.536 4.716 2.569 5.938 5.455 4.038
Sep 2.050 4.392 4.125 4.113 2.269 5.246 5.587 3.567
Oct 2.168 3.899 3.661 3.238 2.107 3.982 6.162 2.708
Nov 2.149 3.131 2.940 2.151 1.610 2.722 5.992 1.851
Dec 1.929 2.533 2.379 1.553 1.217 2.049 5.179 1.393

Source: Authors

Performance metrics comparing the seven alternative methods (EToalti) with the Penman-Monteith method with limited data (EToPM)

During summer (June-August), the EToTE method showed the best performance, with MAE ranging from 0.399 to 2.294 mm day-1 and RMSE from 0.636 to 3.094 mm day-1. In contrast, for winter (December-February), the best-performing method was EToOu, with MAE values between 0.244 and 0.386 mm day-1 and RMSE between 0.395 and 0.561 mm day-1. The least accurate method during summer was EToMB, with MAE and RMSE values exceeding 3.4 and 4.4 mm day-1, respectively. In winter, EToRo yielded the poorest results (Figure 2).

Source: Authors

Figure 2 Mean absolute error (MAE) and root mean square error (RMSE) of the average daily reference evapotranspiration between seven alternative methods (EToalti) and the Penman-Monteith method with limited data (EToPM) (mm day-1).  

In Figure 3, the EToalti that performed best for summer was EToTE, because MAE ranged from 0.360 mm day-1 (August in Siqueros; Figure 3i) to 1.238 mm day-1 (June in Santa Cruz de Alaya; Figure 3g) and RMSE ranged from 0.594 mm day-1 (August in Siqueros; Figure 3j) to 1.745 mm day-1 (June in Santa Cruz de Alaya; Figure 3h). For winter, the EToalti with the best performance was EToOu, since MAE ranged from 1.023 mm day-1 (June in Surutato; Figure 3k) to 1.752 mm day-1 (July in Rosario; Figure 3e) and RMSE ranged from 1.386 mm day-1 (June in Surutato; Figure 3l) to 2.110 mm day-1 (July in Mocorito; Figure 3b). The minimum performance in summer was recorded for EToMB, since MAE ranged from 2.254 mm day-1 (June in Surutato; Figure 3k) to 3.356 mm day-1 (July in Rosario; Figure 3e) and RMSE ranged from 2.948 mm day-1 (June in Surutato; Figure 3l) to 4.271 mm day-1 (July in Rosario; Figure 3f). The minimum performance in the winter season was for EToRo, since MAE ranged from 1.894 mm day-1 (February in Surutato; Figure 3k) to 3.691 mm day-1 (December in Santa Cruz de Alaya; Figure 3g) and RMSE ranged from 2.530 mm day-1 (January in Surutato; Figure 3l) to 4.086 mm day-1 (December in Sanalona II; Figure 3d).

Source: Authors

Figure 3 Mean absolute error (MAE) and root mean square error (RMSE) of the average daily reference evapotranspiration between seven alternative methods (EToalti) and the Penman-Monteith method with limited data (EToPM) (mm day-1; continuation).  

Predictive models of Penman-Monteith annual cumulative reference evapotranspiration with limited data (EToPMP)

Eleven predictive models (Equations 16-26; table 5) were developed to estimate annual EToPMP, five of which were linear and six nonlinear. The linear models were fitted to stations such as Culiacán and El Playón, while nonlinear models were applied to sites like Ixpalino and Surutato. EToPT was the only independent variable present in all equations, indicating its strong predictive power. Nonlinear models showed better fit in all cases, incorporating squared terms for enhanced accuracy.

Table 5 EToPMP predictive equations (dimensionless) 

EToPMP(Culiacán)=-264.700+1.020EToH85-0.701EToPT+0.128EToMB+0.089(EToRo)
(16)
EToPMP(El Playón)=-147.094+1.385EToH85-0.979EToPT-0.016EToTE+0.128(EToOu)
(17)
EToPMP(Guatenipa)=-58.576+0.833EToH75-0.469EToPT+0.036EToTE+0.127(EToRo)
(18)
EToPMP(Ixpalino)=1126.860-3952.740EToH85+4207.710EToH75+2.300EToPT+0.106EToTE-4920.820EToMB+0.278EToRo+7233.980EToOu-1.927EToH852+2.186EToH752-0.001EToPT2-0.001EToTE2+1.615EToMB2-0.001EToRo2-3.491(EToOu)2
(19)
EToPMPLa Cruz=-15.250-3.301EToH85+6.082EToH75-2.035EToPT+0.028EToTE+157.502EToMB-0.170EToRo-231.630EToOu-4.054EToH852+4.600EToH752+0.001EToPT2-0.001EToTE2+0.681EToMB2+0.001EToRo2-1.472(EToOu)2
(20)
EToPMPMocorito=-328.877+1.473EToH75-0.948EToPT+0.204(EToOu)
(21)
EToPMPSanalona II=-1313.880-5.543EToH85+6.461EToH75+0.647EToPT+0.021EToTE+0.451EToMB+0.093EToRo+0.122EToOu+1.235EToH852-1.4000EToH752-0.001EToPT2-0.001EToTE2-5.116EToMB2-0.001EToRo2+11.064(EToOu)2
(22)
EToPMPRosario=535.329-13.260EToH85+16.187EToH75-2.197EToPT+0.176EToTE-0.358EToMB+0.053EToRo-0.002(EToOu)-3.721EToH852+4.219EToH752+0.001EToPT2-0.001EToTE2-2.508EToMB2-0.001EToRo2+5.425(EToOu)2
(23)
EToPMPSanta Cruz de Alaya=-395.051-0.497EToH85-0.040EToH75+0.360EToPT-0.153EToTE-13.693EToMB+0.332EToRo+21.063EToOu+2.723EToH852-3.087EToH752-0.001EToPT2+0.001EToTE2+2.374EToMB2-0.001EToRo2-5.135(EToOu)2
(24)
EToPMPSiqueros=-283.497+1.477EToH75-0.908EToPT+0.121(EToOu)
(25)
EToPMPSurutato=940.336+18.042EToH85-10.433EToH75-8.341EToPT+0.047EToTE-0.433EToMB-1.303EToRo+1.001EToOu-5.318EToH852+6.028EToH752+0.003EToPT2-0.001EToTE2+3.661EToMB2+0.001EToRo2-7.917(EToOu)2
(26)

Source: Authors

Validation

Predictive models of Penman-Monteith annual cumulative reference evapotranspiration with limited data (EToPMP)

Normality of residuals

Normality of residuals was assessed using the Shapiro-Wilk test (table 6). The W values ranged from 0.891 (Ixpalino) to 0.983 (Mocorito). Residuals were non-normal (p < 0.05) in six of the eleven stations. Despite this, all models demonstrated high correlation coefficients. For linear regressions, Pearson’s r ranged from 0.997 to 0.999. Nonlinear models showed a perfect Spearman correlation (r = 0.999), confirming strong model fit. Residual means were close to zero in all cases, confirming homogeneity.

Table 6 Normality of residuals (dimensionless) 

Weather station Shapiro-Wilk (W) P(normal)
Culiacán 0.969 0.207
EL Playón 0.976 0.411
Guatenipa 0.975 0.371
Ixpalino 0.891 0.001
La Cruz 0.905 0.001
Mocorito 0.983 0.662
Sanalona II 0.903 0.001
Rosario 0.940 0.013
Santa Cruz de Alaya 0.940 0.013
Siqueros 0.981 0.593
Surutato 0.952 0.042

Source: Authors

Linearity and fit

All linear regressions showed linearity ((Pr(> 0.279) and all non-linear regressions showed good fit ((Sr( > 0.280). Specifically, the linear regressions yielded correlations from Pr = 0.997 in El Playón (Figure 4b) and Guatenipa (Figure 4c) to Pr = 0.999 in Culiacán (Figure 4a), Mocorito (Figure 4f) and Siqueros (Figure 4j). All non-linear regressions recorded a value of Sr = 0.999 [Ixpalino (Figure 4d), La Cruz (Figure 4e), Sanalona II (Figure 4g), Rosario (Figure 4h), Santa Cruz de Alaya (Figure 4i) and Surutato (Figure 4k)].

Source: Authors.

Figure 4 Multiple linear and nonlinear regressions between Penman-Monteith annual cumulated reference evapotranspiration with limited data (EToPM) and with models (EToPMP) (mm year-1).  

Homogeneity of residuals

Nearly all residual averages (linear and non-linear regressions) were null (Figure 5). Specifically, residual averages ranged from -0.003 mm year-1 (Rosario; Figure 5h) to 0.001 mm year-1 (La Cruz and Surutato; Figures 5e and 5k, respectively). The completely homogeneous residuals (0.000 mm year-1) were recorded in Culiacán, El Playón, Guatenipa, Ixpalino, Mocorito, Sanalona II, Santa Cruz de Alaya and Siqueros (Figures 5a-5d, 5f, 5g, 5i and 5j; respectively).

Source: Authors

Figure 5 Temporal variation of residuals generated between Penman-Monteith annual cumulated reference evapotranspiration with limited data (EToPM) and with models (EToPMP) (mm year-1).  

Spearman correlation (Sr) between daily Penman-Monteith reference evapotranspiration and limited data in Mocorito (EToPM), and observed data in San Juan (EToPMO)

A Spearman correlation analysis was performed between daily EToPM from Mocorito and observed EToPMO data from San Juan (Figure 6). After verifying that only EToPM data were normally distributed (W = 0.996; p = 0.436), a significant correlation was found (Sr = 0.265), exceeding the critical threshold (|Scr| = 0.103; n = 366).

Source: Authors.

Figure 6 Dispersion of daily Penman-Monteith reference evapotranspiration, with limited data in Mocorito (EToPM) and with observed data in San Juan (EToPMO) (mm day-1).  

Discussion

The results in Table 2 are similar to those reported by Flores et al. (2012), as these authors indicate that Tmean in Sinaloa ranges mostly from 24°C to 26°C, where areas with higher elevation, such as Surutato (1460 masl), record ranges from 14°C to 20°C.

The variation in Eva observed in this study (Table 2) is consistent with the results reported by Velasco & Pimentel (2010), furthermore these authors indicate that the average monthly Eva values for Sinaloa ranged from 98.720 mm month-1 in December (3.185 mm day-1) to 267.830 mm month-1 in May (8.640 mm day−1). In addition, Galindo et al. (1991) and Velasco & Pimentel (2010) also agree that the highest magnitudes of Eva in Sinaloa occur in the spring (March-May)-summer agricultural cycle.

EToTE estimates obtained in this study (Tables 3 and 4) are consistent with the results reported by Velasco & Pimentel (2010), moreover these authors indicate that the average monthly magnitudes of EToTE in Sinaloa ranged from 89.840 mm month-1 in December (2.898 mm day-1) to 222.300 mm month-1 in May (7.171 mm day-1).

The variation in EToPM (Tables 3 and 4) was also consistent with that reported by López et al. (2024), in agreement with these authors, EToPM in Culiacán for the year 2020 ranged from 1.600 mm day-1 in February to 10.300 mm day-1 in September. In addition to the above, the highest magnitudes of EToalti and EToPM (Tables 3 and 4) are consistent with Llanes (2023), who states that the highest percentages of accumulated annual EToH85, for the period 1969-2018 and for the stations Culiacán (60.16%), El Varejonal (60.780%), Ixpalino (59.650%), La Concha (59.250%), Rosario (59.500%), Sanalona II (60.280%), and Santa Cruz de Alaya (59.820%) occur in the spring-summer agricultural cycle.

In general, EToTE showed better performance for summer than EToPT (Figures 2 and 3). Considering the comparative limitations between the climate conditions between Mexico and India, Raja et al. (2024) did not analyze EToTE, these authors point out that EToPT records better performance than EToH85, furthermore they state that in a region of India the RMSE ranged from 0.770 mm day-1 (EToH85) to 3.120 mm day-1 (EToPT). This difference may be explained by the greater stability of radiation-based models under the specific climatic conditions of Sinaloa (González et al., 2008; Valdes et al., 2013). On the other hand, Ndule & Ranjan (2021) calculated the performances for three EToalti (EToPT, EToH85 and EToRo) for Manitoba, Canada, finding the following performances, respectively: MAE = 0.362 mm day-1 and RMSE = 0.516 mm day−1, MAE = 0.514 mm day-1 and RMSE = 0.651 mm day-1, and MAE = 0.534 mm day-1 and RMSE = 0.701 mm day-1. These findings are in agreement with Ndule & Ranjan (2021), since in winter, EToRo recorded the lowest performances and EToPT recorded higher performance than EToH85 (Figures 2 and 3). Another investigation that is consistent with the findings of this study is that of Santiago et al. (2012), because these authors point out that in the state of Mexico, the average annual RMSE for the period 2003-2008 ranged from 0.442 mm day-1 (EToPT for 2008) to 0.873 mm day-1 (EToH85 in 2007). Vásquez et al. (2011) also agree on two aspects: EToOu is the model with the best performance (MAE = 1.100 mm day-1 and RMSE = 1.440 mm day-1).

Azua et al. (2020) note that when generating predictions of EToPMP, specification errors should always be minimized by validating the models (Llanes et al., 2022). Residuals were evaluated for normality and linearity. Non-normal residuals were analyzed using non-linear regression methods (Morantes et al., 2019; Llanes et al., 2024). In all models where the residuals did not present normality (Table 5; Equations 19, 20, 22-24 and 26), Model fit was confirmed when Sr exceeded the critical Spearman correlation value (|Scr|) (Figures 4d, 4e, 4g-4i and 4k; Llanes et al., 2022). The 11 models proposed in this study recorded homogeneity in the residuals (Figure 5; Carrasquilla et al., 2016; Llanes et al., 2024; O.C.R., 2024).

These validations support the reliability for the use of the predictive models of EToPMP, particularly when complete climate series are not available (Sentelhas et al., 2010; Fang et al., 2024; CONAGUA-SMN, 2024a), which supports their applicability in regions with incomplete climatological records (López et al., 2024).

Conclusions

Despite Sinaloa being an eminently agricultural state, in many cases complete climate series are not available, which makes the use of EToalti and the modeling of EToPMP an effective alternative for estimating ETo under incomplete data conditions. In general, EToTE is the best performing EToalti for summer and autumn (September-November), and EToOu is the best performing EToalti for winter. As a result, and due to poorer fit in summer, the use of EToMB and EToRo is not recommended for data from Sinaloa weather stations. This study developed 11 predictive models of EToPMP, where seven EToalti serve as explanatory variables. EToPT was the only method that contributed to all predictive models. The use of EToPMP can help minimize errors of overestimation and underestimation of crop water needs, which in turn can ensure the hydro-agricultural needs of Sinaloa and Mexico. This is particularly relevant under anomalously dry conditions, when irrigation scheduling is often inadequate, affecting both the availability and efficiency of water use in crops. Therefore, the application of the proposed EToPMP models represents a valuable tool for improving irrigation practices and water management in regions with incomplete climatic records.

Future lines of research

Future research should consider site-specific measurement of solar radiation (SR) at each weather station, as this variable may enhance the evaluation and differentiation of model performance.

Given that EToPT was applied across all 11 weather stations, it is advisable to conduct individual calibrations for this method, aiming to enable it to approximate the Penman-Monteith standard more accurately.

Although this study applied the most widely used alternative ETo methods, exploring additional methods could further improve the models’ predictive performance. Moreover, future studies are encouraged to incorporate machine learning techniques-such as multivariate adaptive regression splines, gradient boosting, classification and regression trees, and random forests-to potentially enhance the models' explanatory power (R²).

Finally, establishing an agricultural research station in the study region is recommended, allowing direct observation of all input variables of the Penman-Monteith equation, which would enable comprehensive comparisons between observed EToPM and its predictive alternatives.

Acknowledgments

The authors acknowledge the financial support provided by the Research and Postgraduate Secretariat of the National Polytechnic Institute (SIP-IPN) through the research project SIP20240953.

References

Alexandersson, H. (1986). A homogeneity test applied to precipitation data. J. Climatol., (6), 661−675. https://doi.org/10.1002/joc.3370060607. [ Links ]

Allen, R.G., Pereira, L.S., Raes, D. and Smith, M. (1998). Crop evapotranspiration: guidelines for computing crop water requirements., No. 56, Ed. FAO. Rome, 327 p. https://www.fao.org/4/x0490e/x0490e00.htm. [ Links ]

Azua, B.M., Arteaga, R.R., Vázquez, P.M.A. and Quevedo, N.A. (2020). Calibración y evaluación de modelos matemáticos para calcular evapotranspiración de referencia en invernaderos. Rev. Mex. Cienc. Agríc., (11), 125-137. https://www.scielo.org.mx/pdf/remexca/v11n1/2007-0934-remexca-11-01-125.pdf. [ Links ]

Carrasquilla, B.A., Chacón, R.A., Núñez, M.K., Gómez, E.O., Valverde, J. and Guerrero, B.M. (2016). Regresión Lineal Simple y Múltiple: Aplicación en la Predicción de Variables Naturales Relacionadas con el Crecimiento Microalgal. Tecnología en Marcha. Encuentro de Investigación y Extensión, (5), 33-45. https://www.scielo.sa.cr/scielo.php?pid=S0379-39822016000900033&script=sci_abstract&tlng=es. [ Links ]

Celestin, S., Qi, F., Li, R., Yu, T. and Cheng, W. (2020). Evaluation of 32 Simple Equations against the Penman-Monteith Method to Estimate the Reference Evapotranspiration in the Hexi Corridor, Northwest China. Water, (12), 2772. https://doi.org/10.3390/w12102772. [ Links ]

Chávez, R.E., González, C.G., González, B.J.L., Dzul, L.E., Sánchez, C.I., López, S.A. and Chávez, S.J.A. (2013). Uso de estaciones climatológicas automáticas y modelos matemáticos para determinar la evapotranspiración. Tecnol. Cienc. Agua, (4), 115-126. https://www.revistatyca.org.mx/index.php/tyca/article/view/381. [ Links ]

Comisión Nacional del Agua-Servicio Meteorológico Nacional (CONAGUA-SMN) (2024a). Base de datos meteorológicos de México. Available online: https://smn.conagua.gob.mx/es/climatologia/informacion-climatologica/informacion-estadistica-climatologica (accessed on 16 July 2024). [ Links ]

Comisión Nacional del Agua-Servicio Meteorológico Nacional (CONAGUA-SMN) (2024b). Base de datos meteorológicos de México. Available online: https://smn.conagua.gob.mx/tools/GUI/sivea_v3/sivea.php (accessed on 22 August 2024). [ Links ]

Consejo para el Desarrollo Económico de Sinaloa (CODESIN) (2023). Sinaloa en números: agricultura en Sinaloa al 2022, 10. https://sinaloaennumeros.codesin.mx/wp-content/uploads/2023/06/Reporte-24-del-2023-de-Agricultura-en-sinaloa-2022.pdf. [ Links ]

Córdova, M., Carrillo, R.G., Crespo, P., Wilcox, B. and Célleri R. (2015). Evaluation of the Penman-Monteith (FAO 56 PM) Method for Calculating Reference Evapotranspiration Using Limited Data. Mt. Res. Dev., (35), 230-239. https://doi.org/10.1659/MRD-JOURNAL-D-14-0024.1. [ Links ]

Doorenbos, J. and Pruitt, W. (1977). Guidelines for predicting crop water requirements. Rome: FAO. https://www.fao.org/4/f2430e/f2430e.pdf. [ Links ]

Elbeltagi, A., Nagy, A., Mohammed, S., Pande, C.B., Kumar, M., Bhat, S.A., Zsembeli, J., Huzsvai, L., Tamás, J., Kovács, E., Harsányi, E. and Juhász, C. (2022). Combination of Limited Meteorological Data for Predicting Reference Crop Evapotranspiration Using Artificial Neural Network Method. Agronomy, (12), 516. https://doi.org/10.3390/agronomy12020516. [ Links ]

Fang, S.L., Lin, Y.S., Chang, S.C., Chang, Y.L., Ysai, B.Y. and Kuo, B.J. (2024). Using Artificial Intelligence Algorithms to Estimate and Short-Term Forecast the Daily Reference Evapotranspiration with Limited Meteorological Variables. Agriculture, (14), 510. https://doi.org/10.3390/agriculture14040510. [ Links ]

Flores, C.L.M., Arzola, G.J.F., Ramírez, S.M. and Osorio, P.A. (2012). Global climate change impacts in the Sinaloa state, Mexico. Cuad. Geogr., (21), 115-129. http://www.scielo.org.co/scielo.php?script=sci_arttext&pid=S0121-215X2012000100009. [ Links ]

Galindo, I., Castro, S. and Valdes, M. (1991). Satellite derived solar irradiance over Mexico. Atmósfera, (4), 189-201. http://www.ejournal.unam.mx/atm/Vol04-3/ATM04306.pdf. [ Links ]

Galindo, R.J.G. and Alegría, H. (2018). Toxic effects of exposure to pesticides in farm workers in Navolato, Sinaloa (Mexico). Rev. Int. Contam. Ambient., (34), 505-516. https://doi.org/10.20937/rica.2018.34.03.12. [ Links ]

Gao, F., Feng, G., Ouyang, Y., Wang, H., Fisher, D., Adeli, A. and Jenkins, J. (2017). Evaluation of Reference Evapotranspiration Methods in Arid, Semiarid, and Humid Regions. J. Am. Water Resour. Assoc., (53), 791-808. https://www.srs.fs.usda.gov/pubs/ja/2017/ja_2017_ouyang_008.pdf. [ Links ]

González, C.J.M., Cervantes, O.R., Ojeda, B.W. and López, C.I. (2008). Predicción de la evapotranspiración de referencia mediante redes neuronales artificiales. Ing. Hidraul. Mex., (13), 127-138. http://repositorio.imta.mx/handle/20.500.12013/852. [ Links ]

Guijarro, J.A. (2024). Package ‘climatol’ version 4.1.0: climate tools (series homogenization and derived products). Repository CRAN, 41 p. https://cran.r-project.org/web/packages/climatol/climatol.pdf. [ Links ]

Hargreaves, G.H. (1975). Moisture availability and crop production. Trans. ASAE, (18), 980-984. https://elibrary.asabe.org/abstract.asp?aid=36722&t=2&redir=&redirType=. [ Links ]

Hargreaves, G.H. and Samani, Z.A. (1985). Reference crop evapotranspiration from ambient air temperature. Am. Soc. Agric. Eng., (1), 96-99. https://www.researchgate.net/publication/247373660_Reference_Crop_Evapotranspiration_From_Temperature. [ Links ]

Hargreaves, G.H., ASCE, F. and Allen, R.G. (2003). History and evaluation of Hargreaves evapotranspiration equation. J. Irrig. Drain Eng., (129), 53-63. https://uon.sdsu.edu/onlinehargreaves.pdf. [ Links ]

Kennedy, S.R., Chen, C.D., Guijarro, J.A. and Chen, Y. (2023). Quantifying the evolving role of intense precipitation runoff when calculating soil moisture trends in east Texas. Meteorol. Atmos. Phys., (135), 8. https://doi.org/10.1007/s00703-022-00947-w. [ Links ]

Kim, C.G., Lee, J., Lee, J.E. and Chung, I.M. (2024). Calibration and Evaluation of Alternative Methods for Reliable Estimation of Reference Evapotranspiration in South Korea. Water, (16), 2471. https://doi.org/10.3390/w16172471. [ Links ]

Li, Z., Li, Y., Yu, X., Jia, G., Chen, P., Zheng, P., Wang, Y. and Ding, B. (2024). Applicability and improvement of different potential evapotranspiration models in different climate zones of China. Ecol. Process., (13), 20. https://doi.org/10.1186/s13717-024-00488-7. [ Links ]

Lin, N.J., Feng, H.Y., Sheng, Y.S.L. and Wen, T.J. (2022). Comparative assessment of reference crop evapotranspiration models and its sensitivity to meteorological variables in Peninsular Malaysia. Stoch. Environ. Res. Risk Assess., (36), 3557-3575. https://doi.org/10.1007/s00477-022-02209-y. [ Links ]

Llanes, C.O. (2023). Predictive association between meteorological drought and climate indices in the state of Sinaloa, northwestern Mexico. Arab. J. Geosci., (16), 79. https://doi.org/10.1007/s12517-022-11146-7. [ Links ]

Llanes, C.O., Estrella, G.R.D., Parra, G.R.E., Gutiérrez, R.O.G., Ávila, D.J.A. and Troyo, D.E. (2024). Modeling Yield of Irrigated and Rainfed Bean in Central and Southern Sinaloa State, Mexico, Based on Essential Climate Variables. Atmosphere, (15), 573. https://doi.org/10.3390/atmos15050573. [ Links ]

Llanes, C.O., Norzagaray, C.M., Gaxiola, A., Pérez, G.E., Montiel, M.J. and Troyo, D.E. (2022). Sensitivity of Four Indices of Meteorological Drought for Rainfed Maize Yield Prediction in the State of Sinaloa, Mexico. Agriculture, (12), 525. https://doi.org/10.3390/agriculture12040525. [ Links ]

López, A.J.E., López, I.H.J., Tirado, R.M.A., Estrada, A.M.D. and Martínez, G.J.A. (2024). Requerimiento hídrico, coeficiente de cultivo y productividad de pasto híbrido Convert 330 (Brachiaria sp) en un clima semiárido cálido de México. Terra Latinoam., (42), 1-15. https://doi.org/10.28940/terra.v42i0.1797. [ Links ]

Matimolane, S., Strydom, S., Mathivha, F.I. and Chikoore, H. (2024). Evaluating the spatiotemporal patterns of drought characteristics in a semi‐arid region of Limpopo Province, South Africa. Environ. Monit. Assess., (196), 1062. https://doi.org/10.1007/s10661-024-13217-6. [ Links ]

Matsui, H. and Osawa, K. (2023). Alternative net longwave radiation equation for the FAO Penman-Monteith evapotranspiration equation and the Penman evaporation equation. Theor. Appl. Climatol., (153), 1355-1360. https://doi.org/10.1007/s00704-023-04524-y. [ Links ]

McGuinness, J.L. and Bordne, E.F. (1972). A comparison of lysimeter-derived potential evapotranspiration with computed values. TB1452. U. S. Department of Agricultural. Tech. Bull., (1452). 71. https://www.google.es/url?sa=t&source=web&rct=j&opi=89978449&url=https://ageconsearch.umn.edu/record/171893/files/tb1452.pdf&ved=2ahUKEwik7NXD-cyJAxUSJ0QIHeztMeQQFnoECBAQAQ&usg=AOvVaw2Fqxo_hE0RQt6TL4JM5yfJ. [ Links ]

Morantes, Q.G.R., Rincón, P.G. and Pérez, S.N.A. (2019). Modelo de Regresión Lineal Múltiple Para Estimar Concentración de PM1. Rev. Int. Contam. Ambie., (35), 179-194. https://www.scielo.org.mx/scielo.php?pid=S0188-49992019000100179&script=sci_abstract. [ Links ]

Ndule, E. and Ranjan, S.R. (2021). Performance of the FAO Penman-Monteith equation under limiting conditions and fourteen reference evapotranspiration models in southern Manitoba. Theor. Appl. Climatol. (143), 1285-1298. https://doi.org/10.1007/s00704-020-03505-9. [ Links ]

Oudin, L., Hervieu, F., Michel, C., Perrin, C., Andréassian, V., Anctil, F. and Loumagne, C. (2005). Which potential evapotranspiration input for a lumped rainfall-runoff model? Part 2-Towards a simple and efficient potential evapotranspiration model for rainfall-runoff modeling. J. Hydrol., (303), 290-306. https://doi.org/10.1016/j.jhydrol.2004.08.026. [ Links ]

Oxford Cambridge and RSA (OCR) (2024). Formulae and Statistical Tables (ST1). 1-8: Database of Critical Values. https://www.ocr.org.uk/Images/174103-unit-h869-02-statistical-problem-solving-statistical-tables-st1-.pdf. (accessed on 20 June 2024). [ Links ]

Penman, H. L. (1948). Natural evaporation from open water, bare soil and grass. Proc. R. Soc., (193), 120-145. https://royalsocietypublishing.org/doi/epdf/10.1098/rspa.1948.0037. [ Links ]

Perčec, T.M., Pasarić, Z. and Guijarro, J.A. (2023). Croatian high‑resolution monthly gridded dataset of homogenized surface air temperature. Theor. Appl. Climatol., (15), 227-251. https://doi.org/10.1007/s00704-022-04241-y. [ Links ]

Priestley, C.H.B. and Taylor, R.J. (1972). On the assessment of surface heat-flux and evaporation using large-scale parameters. MWR, (100), 81-92. https://journals.ametsoc.org/view/journals/mwre/100/2/1520-0493_1972_100_0081_otaosh_2_3_co_2.xml. [ Links ]

Raja, P., Sona, F., Surendran, U., Srinivas, C.V., Kannan, K., Madhu, M., Mahesh, P., Annepu, S.K., Ahmed, M., Chandrasekar, K., Suguna, A.R., Kumar, V. and Jagadesh, M. (2024). Performance evaluation of different empirical models for reference evapotranspiration estimation over Udhagamandalm, The Nilgiris, India. Sci. Rep., (14), 12429. https://doi.org/10.1038/s41598-024-60952-4. [ Links ]

Remiro, A.A., Heath, A. and Baio, G. (2024). Model-based standardization using multiple imputation. BMC Med. Res. Methodol., (24), 32. https://doi.org/10.1186/s12874-024-02157-x. [ Links ]

Romanenko, V.A. (1961). Computation of the autumn soil moisture using a universal relationship for a large area, Proc. Ukrainian Hydrometeorological Research Institute. Kiev. No. 3. [ Links ]

Rubin, D.B. (2004). Multiple Imputation for Nonresponse in Surveys. 81. New York: Wiley. https://www.wiley.com/en-us/Multiple+Imputation+for+Nonresponse+in+Surveys-p-9780471655749. [ Links ]

Santiago, R.S., Arteaga, R.R., Sangerman, J.D.M., Cervantes, O.R. and Navarro, B.A. (2012). Reference evapotranspiration estimated by Penman-Monteith-Fao, Priestley-Taylor, Hargreaves and ANN. Rev. Mex. Cienc. Agríc., (3), 1535-1549. https://www.scielo.org.mx/scielo.php?script=sci_arttext&pid=S2007-09342012000800005. [ Links ]

Satpathi, A., Danodia, A., Abed, S.A., Nain, A.S., Al-Ansari, N., Ranjan, R., Vishwakarma, D.K., Gacem, A., Mansour, L. and Yadav, K.K. (2024). Estimation of the crop evapotranspiration for Udham Singh Nagar district using modified Priestley‑Taylor model and Landsat imagery. Sci. Rep., (14), 21463. https://doi.org/10.1038/s41598-024-72299-x. [ Links ]

Sentelhas, P.C., Gillespie, T.J. and Santos, E.A. (2010). Evaluation of FAO Penman-Monteith and alternative methods for estimating reference evapotranspiration with missing data in Southern Ontario, Canada. Agric. Water Manag., (97), 635-644. https://doi.org/10.1016/j.agwat.2009.12.001. [ Links ]

Skhiri, A., Ferhi, A., Bousselmi, A., Khlifi, S. and Mattar, M.A. (2024). Artificial Neural Network for Forecasting Reference Evapotranspiration in Semi-Arid Bioclimatic Regions. Water, (16), 602. https://doi.org/10.3390/w16040602. [ Links ]

Song, X., Lu, F., Xiao, W., Zhu, K., Zhou, Y. and Xie, Z. (2018). Performance of 12 reference evapotranspiration estimation methods compared with the Penman-Monteith method and the potential influences in northeast China. Meteorol. Appl., (26), 83-96. https://doi.org/10.1002/met.1739. [ Links ]

Sutanto, S.J., Zarzoza, M.S.B., Supit, I. and Wang, M. (2024). Compound and cascading droughts and heatwaves decrease maize yields by nearly half in Sinaloa, Mexico. npj Nat. Hazards, (1), 26. https://doi.org/10.1038/s44304-024-00026-7. [ Links ]

Usta, S. (2024). Estimation of reference evapotranspiration using some class-A pan evaporimeter pan coefficient estimation models in Mediterranean-Southeastern Anatolian transitional zone conditions of Turkey. PeerJ, (12), e17685. http://doi.org/10.7717/peerj.17685. [ Links ]

Uzunlar, A., and Dis, M.O. (2024). Novel Approaches for the Empirical Assessment of Evapotranspiration over the Mediterranean Region. Water, (16), 507. https://doi.org/10.3390/w16030507. [ Links ]

Valdes, B.M., Riveros, R.D., Arancibia, B.C.A. and Bonifaz, R. (2013). The solar resource assessment in Mexico: state of the art. Energy Proc., (57), 1299-1308. https://doi.org/10.1016/j.egypro.2014.10.120. [ Links ]

Varga, H.Z., Szalka, É. and Szakál, T. (2022). Determination of Reference Evapotranspiration Using Penman-Monteith Method in Case of Missing Wind Speed Data under Subhumid Climatic Condition in Hungary. Atmos. Clim. Sci., (12), 235-245. https://www.scirp.org/journal/paperinformation?paperid=115214. [ Links ]

Vásquez, M.R., Ventura, R.E.J. and Acosta, G.J.A. (2011). Habilidad de estimación de los métodos de evapotransporación para una zona semiárida del centro de México. Rev. Mexicana cienc. agric., (2), 399-415. https://www.scielo.org.mx/scielo.php?script=sci_arttext&pid=S2007-09342011000300008. [ Links ]

Velasco, I. and Pimentel, E. (2010). Zonificación agroclimática de Papadakis aplicada al estado de Sinaloa, México. Inv. Geog., (73), 86-102. https://www.scielo.org.mx/scielo.php?script=sci_arttext&pid=S0188-46112010000300007. [ Links ]

Yang, Y., Chen, R., Han, C. and Liu, Z. (2021). Evaluation of 18 models for calculating potential evapotranspiration in different climatic zones of China. Agric. Water Manag., (244), 106545. https://doi.org/10.1016/j.agwat.2020.106545. [ Links ]

Yonaba, R., Tazen, F., Cissé, M., Adjadi, M.L., Belemtougri, A., Alligouamé, O.V., Koïta, M., Niang, D., Karambiri, H. and Yacouba, H. (2023). Trends, sensitivity and estimation of daily reference evapotranspiration ETo using limited climate data: regional focus on Burkina Faso in the West African Sahel. Theor. Appl. Climatol., (153), 947-974. https://doi.org/10.1007/s00704-023-04507-z. [ Links ]

Rol de Contribución Autor (es)
Conceptualización Omar Llanes Cárdenas
Metodología Mariano Norzagaray Campos «principal»
Jeovám A. Ávila Díaz «que apoya»
Software Marco A. Arciniega Galaviz
Validación Omar Llanes Cárdenas
Análisis Formal Ernestina Pérez González
Investigación Mariano Norzagaray Campos «principal»
Ernestina Pérez González «que apoya»
Recursos Omar Llanes Cárdenas «principal»
Mariano Norzagaray Campos «que apoya»
Curación de datos Marco. A. Arciniega Galaviz
Escritura - Preparación del borrador original Omar Llanes Cárdenas
Escritura - Revisión y edición Omar Llanes Cárdenas
Visualización Ernestina Pérez González «principal»
Marco A. Arciniega Galaviz «que apoya»
Supervisión Jeován A. Ávila Díaz
Administración de Proyectos Omar Llanes Cárdenas «principal»
Mariano Norzagaray Campos «que apoya»
Adquisición de fondos Omar Llanes Cárdenas «principal»
Mariano Norzagaray Campos «que apoya»

Received: February 2025; Accepted: July 2025

Creative Commons License Este es un artículo publicado en acceso abierto bajo una licencia Creative Commons