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Article

Prediction of Crops Cycle with Seasonal Forecasts to Support Decision-Making

1
LEAF—Linking Landscape, Environment, Agriculture and Food Research Center, Associate Laboratory TERRA, Instituto Superior de Agronomia, Universidade de Lisboa, Tapada da Ajuda, 1349-017 Lisboa, Portugal
2
Luiz de Queiroz College of Agriculture, University of São Paulo, Piracicaba 13418-900, Brazil
3
CITAB—Centre for the Research and Technology of Agro-Environmental and Biological Sciences, Inov4Agro—Institute for Innovation, Capacity Building, and Sustainability of Agri-Food Production, University of Trás-os-Montes e Alto Douro, UTAD, 5000-801 Vila Real, Portugal
*
Author to whom correspondence should be addressed.
Agronomy 2025, 15(6), 1291; https://doi.org/10.3390/agronomy15061291
Submission received: 12 April 2025 / Revised: 20 May 2025 / Accepted: 20 May 2025 / Published: 24 May 2025
(This article belongs to the Section Farming Sustainability)

Abstract

:
Climate variability, intensified by climate change, poses significant challenges to agriculture, affecting crop development and productivity. Integrating seasonal weather forecasts (SWF) into crop growth modelling tools is therefore essential for improving agricultural decision-making. This study assessed the uncertainties of raw (non-bias-corrected) temperature forecasts from the European Centre for Medium-Range Weather Forecasts (ECMWF) SEAS5 seasonal (seven-month forecasts) to estimate the spring–summer maize, melon, sunflower, and tomato crops cycle from 2013 to 2022 in the Caia Irrigation Scheme, southern Portugal. AgERA5 reanalysis data, after simple bias correction using local weather station data, was used as a reference. The growing degree-day (GDD) approach was applied to estimate the crop cycle duration, which was then validated against ground truth and satellite data. The results show that SWF tend to underestimate maximum temperatures and overestimate minimum temperatures, with these biases partially offsetting to improve mean temperature accuracy. Forecast skill decreased non-linearly with lead time, especially after the second month; however, in some cases, longer lead times outperformed earlier ones. Temperature forecast biases affected GDD-based crop cycle estimates, resulting in a slight underestimation of all crop cycle durations by around a week. Nevertheless, the forecasts captured the overall increasing temperature trend, interannual variability, and anomaly signals, but with marginal added value over climatological data. This study highlights the potential of integrating ground truth and Earth observation data, together with reanalysis data and SWF, into GDD tools to support agricultural decision-making, aiming at enhancing yield and resources management.

1. Introduction

Climate variability represents a major source of uncertainty in agriculture and has been exacerbated by climate change. This impacts crop development and productivity [1,2,3,4,5]. The Mediterranean region, a climate change hotspot [6,7], is experiencing raising temperatures, shifting precipitation patterns, and an increase in extreme weather events, such as droughts and heatwaves (e.g., [8]). Such events can disrupt crop growth conditions and ultimately threaten agricultural production [9,10,11]. Climate variability further increases the complexity of agricultural production and the decision-making processes of farmers and other stakeholders. Uncertainty about future weather conditions hampers seasonal planning, increases risks, and frequently results in production and economic losses. It may also have negative environmental impacts [12,13,14]. Therefore, accessible and innovative tools are needed to support decision-making and to help cope with climate uncertainty [15]. This could be achieved through the use of early warning systems and the integration of climate forecasts into crop growth modelling tools and resource management strategies [16,17,18,19].
Crop growth and productivity are highly dependent on climatic conditions, particularly temperature [20,21,22,23]. Changes in the temperature regimes affect the crop development rates, ultimately impacting quantity and quality of yields [24,25]. Several authors have reported that, in the absence of major biotic and abiotic stresses, crop development rates are generally assumed to be linearly related to temperature. This relationship is used in the growing degree-days (GDD) approach [21,26,27]. The GDD approach accumulates heat units above a lower threshold temperature (base temperature) and considers an upper limit above which development stops. This provides a simplified yet effective way of estimating crop growth stages and crop cycle duration. Although more complex modelling approaches are widely used, particularly to simulate crop–climate interactions, e.g., AquaCrop crop growth model [28], they require extensive input data, calibration, and technical knowledge, making them less accessible for routine use by farmers, water managers or technicians [29]. In contrast, the GDD approach provides a practical and intuitive decision-support tool that enables timely adjustments in agricultural planning and management. Therefore, GDD-based estimates are particularly suitable for operational applications [30,31].
Seasonal forecasts (SWF) aim to provide insight into the expected weather conditions over the coming months, as well as any deviations from long-term averages. Despite the inherent unpredictability of the atmosphere, advances in modelling have improved the reliability of these forecasts, establishing them as valuable decision-making tools in agriculture [32,33,34]. Several studies have focused on using SWF to estimate the timing of specific phenological stages [35,36], as well as for predicting early season yields [18,37,38,39,40,41,42]. Furthermore, some studies have emphasised the added value of using SWF compared to historical climatological data in an agricultural context [43,44,45]. Although SWF have limitations, such as varying accuracy depending on region, season and variables of interest [35,46,47], recent studies show that integrating seasonal temperature forecasts with crop growth models can effectively support decision-making by providing early estimates of crop development and productivity [16,48,49]. However, their practical application in Mediterranean agriculture remains limited due to uncertainties in forecast accuracy and the complexity of their use [50,51].
Incorporating seasonal temperature forecasts into a GDD tool enables proactive adjustments to planting and harvesting. This helps farmers adapt to climate variability and mitigate the risks associated with unpredictable seasonal shifts (e.g., early frosts, heatwaves or droughts). It will also enable more efficient resources management, particularly water, and promote yield optimisation by ensuring that crops develop within specific time windows. This study aims to assess how accurately the raw (non-bias-corrected) seasonal temperature forecasts, provided by the European Centre for Medium-Range Weather Forecasts (ECMWF) SEAS5 predict the duration of spring–summer crop cycles in a water-scarce region of southern Portugal. The specific objectives of this work are: (1) to assess the accuracy and skill of the SWF in predicting maximum, minimum, and mean temperature; (2) to evaluate the influence of lead time on forecast performance; (3) to estimate the performance of crop cycle length estimation using the GDD approach driven by SWF. The novelty of the current study lies in the comprehensive assessment of the practical utility of seasonal forecasts for supporting agricultural decision-making, achieved by combining direct validation of temperature forecast skill and indirect validation of its accuracy in estimating crop growth cycles. This study is a step towards identifying the practical potential and constraints to the widespread adoption of such simplified tools.

2. Materials and Methods

This study analyses the quality, skill, and usability of SWF data produced by the ECMWF for predicting the duration of the growing cycle of various spring–summer crops. This assessment used the SWF temperature data ingested in the GDD approach. The procedure followed the flowchart in Figure 1 and included the collection and Quality Assurance and Quality Control (QAQC) assessment of the different sources of temperature, i.e., the observed weather data (2013–2022), the AgERA5 reanalysis data, and SWF data. Ground truth and remotely sensed crop cycle data from previous studies [52] developed in the targeted Caia Irrigation Scheme were used as a baseline for the GDD approach. The need for bias correction of the AgERA5 reanalysis data were assessed prior to its use. After appropriate bias correction, the AgERA5 data were used as “observations” in the direct validation of the SWF data. The indirect validation of the SWF was performed by analysing the estimated crop cycle lengths using the cumulative GDD approach (Figure 1).

2.1. Study Site Brief Characterisation

The current study was conducted at the Caia Irrigation Scheme (CIS) in Elvas, Alentejo region, southern Portugal (Figure 2). The CIS has been in operation since 1969 and is currently managed by the Caia Water Users Association (Caia WUA). It covers an area of approximately 7000 hectares and supplies water to over 800 farmers [52]. Water from the Caia Reservoir on the Caia River is distributed through an open channel system with upstream control, following a fixed rotation schedule that limits water allocation per hectare to each farmer. Irrigation is mainly drip irrigation (82%), followed by sprinkler irrigation (17%)—mainly center pivots—while surface irrigation accounts for approximately 2% of the total irrigated area.
According to the Caia WUA, cropping patterns in the CIS have changed in recent decades, shifting from annual crops to highly profitable permanent orchards, primarily of olive (Olea europaea L.) and nuts (almonds and walnuts). Currently, olive orchards are the main crop in the CIS [52,53]. However, annual crops such as maize, winter cereals, processing tomato, and various oilseed and vegetable crops remain an important part of CIS production. For the current study, the main irrigated crops were selected, i.e., maize (Zea mays L.), melon (Cucumis melo L.), sunflower (Helianthus annuus L.) and tomato (Solanum lycopersicum L.).
According to the FAO classification [54], the main soils in the CIS are Fluvissols (45%), Luvissols (30%), and Calcissols (19%). Overall, the soils in the CIS are well-suited for irrigated agriculture, with a variety of textures (loamy-sand, silty-clay, clay) and structure, adequate drainage capacity, and gentle slopes (<6%) [55].
The region has a typical temperate Mediterranean climate, characterised by hot and dry summers. According to the Köppen–Geiger classification [56], it is classified as a Csa. The long-term (2002–2021) average annual precipitation is approximately 505 mm, of which around 25% occurs between April and September. The mean temperature is around 16.7 °C. The average maximum temperature exceeds 30 °C during the summer months, while the average minimum temperature falls below 5 °C in the winter months (Figure 3). The Elvas region is considered a climate change hotspot, so preparedness and adaptation measures are essential [57,58].

2.2. Atmospheric Data

2.2.1. Ground Truth Data

The ground-based meteorological data were obtained from a weather station belonging to the operational network of automatic agrometeorological stations installed across the major irrigated areas of the Alentejo region. This network is managed by the Centro Operativo e de Tecnologia de Regadio (COTR). The station is located within a 5 × 5 m grass-covered area, and comprises a central data acquisition unit, and a set of sensors. Air temperature is measured using a Thies Clima thermohygrometer (model 1.1005.54.000), with a measurement range of −30 to 70 °C and a response time of 20 s. Sensor readings are taken every 10 s and compiled into hourly and daily reports. The data are stored in Data Taker 500 loggers and transmitted automatically between 01:00 and 02:00 each day. Daily validated data are made available to users through the COTR platform. Further information is provided by Oliveira et al. [59]. Daily maximum (Tmax, °C) and minimum (Tmin, °C) temperature weather data covering the period 2013–2022 was collected from the meteorological station of Caia, Elvas (38°53′27″ N, 07°08′23″ W, 208 m a.s.l) which is located close to the CIS and within a 10 km radius of the crop plots observed during 2017–2019.

2.2.2. Reanalysis

To address the issue of the point location weather dataset and, therefore, upscaling to the CIS, a reanalysis dataset was considered for this study. The AgERA5 (version 1.1) daily reanalysis dataset provided by the ECMWF and available in the Copernicus Climate Change Service Data Store was selected [60]. The AgERA5 dataset is based on the forcing of ECMWF ERA5 hourly data and has been developed for agricultural and agroecological studies (e.g., [61,62]). AgERA5 covers the period from 1979 to the present day, (one month prior to the date of access) on a global grid with a resolution of 0.1° and includes a large number of atmospheric and surface variables. In the current study, the six grid cells covering the CIS area were selected, and Tmax and Tmin data for the decade 2013–2022 were collected. To account for the differences in altitude between the weather station and the reanalysis grid points, a temperature correction was applied using a constant lapse rate, i.e., ratio of the variation in temperature and the variation in altitude, of 6.5 °C per km. This is a standard value for mid-latitude regions [63,64,65]. This adjustment improved the agreement between the reanalysis and the observed temperatures.

2.2.3. Seasonal Forecasts

The seasonal forecast data were provided by the European Centre for Medium-Range Weather Forecasts (ECMWF). This dataset is part of the Copernicus Climate Change Service (C3S) multi-system seasonal forecast service and is available from the Copernicus Climate Data Store (CDS) as “Seasonal forecast daily and sub-daily data on single levels”. It is produced by the ECMWF SEAS5 (v5.1) system [66]. The dataset consists of an ensemble of gridded data with global coverage and a horizontal resolution of 1°, with temporal coverage from 1981 to the present day (with a one-month lag). The dataset includes hindcasts (1981 to 2016) with 25 ensemble members and real-time forecasts (2017 to the present day) with 51 ensemble members, extending 7 months into the future [32]. Daily Tmax and Tmin forecasts, initialised on 1 April for mainland Portugal, were collected to cover the spring–summer season; thus, the crop cycle of all the selected crops (Table 1). The analysis below focuses on the period 2013 to 2022, using data from the grid cell closest to the CIS (39°00′00″ N, 07°00′00″ W, 294 m a.s.l.). The CIS is entirely contained within a single SEAS5 grid cell and the grid point closest to it was selected as representative of the region. As each SEAS5 grid point represents an average condition within its cell, the selected point is considered to adequately capture the average conditions within the study area.

2.3. Data Analysis

2.3.1. Quality Assurance and Quality Control (QAQC)

The integrity and quality of weather data, whether from weather stations or gridded datasets, must be assessed prior to use. Poor sensor calibration, malfunctions, or limited maintenance can affect weather station measurements for different variables [67,68]. Conversely, modelled data often exhibits some bias [63,69,70,71,72]. Therefore, analysing data consistency is mandatory, and data corrections should be applied if necessary to address these issues [73]. The temperature data collected for this study underwent a QAQC process, during which missing, duplicate, and suspicious records were identified and corrected as necessary. The range and seasonal pattern of temperature values were examined to ensure that no records showed maximum temperatures lower than minimum temperatures. The Tmax and Tmin values were then used to calculate the daily mean temperature (Tmean) for the three datasets.

2.3.2. Reanalysis Data Bias Correction and Validation

A set of goodness of fit indicators was used to compare TOBS and TREAN in order to assess the need for bias correction, including the following: (i) the regression coefficient (b0) of a forced to the origin (FTO) linear regression; (ii) the coefficient of determination (R2) of an ordinary least squares (OLS) linear regression; (iii) the root mean square error (RMSE); (iv) the normalised root mean square error (NRMSE, %), calculated as the ratio of the RMSE to the mean of the observed values ( O ¯ ), providing a dimensionless measure of the relative error of the model; and (v) the Nash and Sutcliff [74] model efficiency (EF). A similar approach has been used in previous studies [63,71,75,76,77].
The use of these metrics highlighted the need for bias correction in the reanalysis data. A simplified approach was adopted for both Tmax and Tmin by adding a constant c(month) to the uncorrected TREAN unc as follows:
c m o n t h i = T R E A N   u n c ( m o n t h i ) ¯ T O B S ( m o n t h i ) ¯
Due to the small temperature differences within the study area, the correction factor for each variable was calculated using the reanalysis grid point closest to the Caia weather station (38°53′60″ N, 07°05′60″ W, 226 m a.s.l.) and then applied to all reanalysis grid points within the CIS.

2.3.3. Seasonal Forecasts Direct Validation Approach

The first assessment of SWF performance was based on a direct comparison between temperature data from the reanalysis dataset and SWF datasets for the same period (2013–2022). Temperature values were assessed at two levels, monthly and seasonal. The monthly assessment evaluated whether the SWF performance remained consistent over time (April, May, June, July, August, September, October). The seasonal analysis evaluated the overall forecast performance by averaging both Tmax and Tmin during April–September. This type of analysis uses a combination of the deterministic approach, which uses the SWF ensemble median, and a probabilistic approach, which uses all members of the forecast ensemble. The methodology adopted for each indicator is summarised in Table A1. The average of the six AgERA5 grid points was used as the reference for the comparison.
Analytical and statistical approaches were used to evaluate the precision and reliability of the ECMWF SEAS5 seasonal forecasts for the CIS. The analytical analysis involved producing box and whisker plots showing the forecast ensemble members alongside the reanalysis values for seasonal averages of Tmax, Tmin and Tmean. This approach made it possible to visualise errors in the SWF in relation to reanalysis, and to assess the ability of the forecasts to detect temperature anomalies and trends. In addition to the above mentioned goodness of fit indicators, other statistical performance metrics were used to quantify the accuracy and skill of the SWF for each variable (Tmax, Tmin and Tmean): Bias Percentage (PBIAS), Mean Absolute Error (MAE), Standardised Anomaly Index (SAI) [78,79], Anomaly Correlation Coefficient (ACC) [80] and Continuous Ranked Probability Skill Score (CRPSS) [80,81,82,83,84]. Table A1 summarises the information relative to each indicator.
Significance tests were conducted to evaluate the statistical significance of forecast performance metrics. Pearson’s correlation t-test was used for ACC indicator to assess whether the correlation between reanalysis and forecasted anomalies differed from zero, while one-sample t-tests were applied for MAE and PBIAS to determine whether the mean absolute differences and mean differences (bias), respectively, were significantly different from zero (α = 0.05).

2.3.4. Seasonal Forecasts Indirect Validation Approach

In this study, the performance of SWF was evaluated using an indirect approach by analysing its performance in calculating crop growth stages and cycle length. The time required for a plant to reach a given growth stage is directly related to the amount of temperature accumulation over time [21,85,86]. This relationship is referred to as growing degree-days (GDD). Therefore, the GDD approach was used to determine the length of the crop cycle. In the current study, it was assumed that GDD represents the cumulative sum of temperatures above a baseline threshold (Tbase) required to reach a given growth stage [20], and that development ceases above an upper temperature limit (Tupper) [27,86]. Therefore, GDD values were computed as follows:
G D D = 0 ,     T m e a n T b a s e     T m e a n T b a s e ,       T b a s e < T m e a n < T u p p e r T u p p e r T b a s e ,       T m e a n T u p p e r
The crop cycles for the crops selected for the current study were derived from a thorough analysis of vegetation indices (NDVI) using Google Engine tools (Table 1). This analysis was conducted for the 2017, 2018, and 2019 years across the main production areas of maize, melon, sunflower, and tomato crops within the CIS. These durations represent the mean values of crop cycle durations across all farms within the CIS that cultivated each selected crop. In other words, they are the mean values of the ensemble of farms. The durations were validated using ground truth data provided by the Caia WUA, and some farms were surveyed in 2017. Melon and tomato crops were not identified within the study area in 2018. Further details on image processing can be found in the study by Ferreira et al. [52].
Having determined the length of each growth stage in days, the cumulative growing degree-days (CGDD) requirements were calculated using the observed (weather station) temperature data (Table 1). These CGDD values are within the reference values proposed by Pereira et al. [68] for crops not subject to biotic and abiotic stresses and were applied throughout the study period to determine crop cycles using reanalysis and SWF data.
Two types of analysis were performed. The first was a decadal analysis (2013–2022) that used 2017 GDD data as a reference (Table 2). This reference was maintained in the other years to evaluate the impact of climate variability on the forecast performance for crop cycle prediction. According to the Caia WUA, the sowing/planting and harvesting dates in 2017 are closer to the usual dates in the CIS. Therefore, the results presented in this study refer to 2017. The second analysis focused on the three years with NDVI-derived phenology data and considered CGDD variability across 2017, 2018, and 2019.
The same statistical metrics used in the direct validation were applied to the crop cycle lengths (Table A1) to assess the performance of ECMWF SEAS5 forecasts in accurately predicting the crop cycle length, thus supporting crop management decisions in southern Portugal.

3. Results and Discussion

3.1. Reanalysis Correction and Validation

The analysis showed that the Tmax and Tmin reanalysis data are highly correlated with the weather station observations, with R2 values above 0.98. However, the reanalysis data show a general tendency to underestimate Tmax (b0 = 0.94) and to overestimate Tmin (b0 = 1.15) compared to the observations (Figure 4). Table 3 summarises the accuracy of the reanalysis estimates relative to the observations before and after the simplified bias correction. The results show small errors for Tmax (NRMSE < 10%), while the errors for Tmin are quite high (NRMSE = 26%). The EF values for both Tmax and Tmin are high (>0.80). As Tmax and Tmin have opposite tendencies, the Tmean results are much better, with NRMSE < 6% and EF = 0.98. After the simplified bias correction, based on monthly mean differences between the observed and reanalysis data, the performance of the reanalysis temperature estimates for Tmax, Tmin, and Tmean improves. Initial biases and estimation errors are substantially reduced, particularly for Tmin, with the NRMSE decreasing to 16%. This confirms the validity and appropriateness of the correction approach. The good results obtained for Tmean are further improved after bias correction. This leads to consistent and accurate agreement between the reanalysis and the observed data.
The results of this study are consistent with those reported in the literature, which highlight the good performance of various reanalysis products in reproducing temperature variables, particularly ERA5, for which R2 values are generally above 0.90. Several studies have reported RMSE values around 2 °C when comparing reanalysis data with ground truth data. Examples include the study by Vanella et al. [76], which was carried out at several locations in Italy, including island environments, and the study by Jiménez-Jiménez et al. [87] which was carried out in Mexico. In line with our results, other authors (e.g., [87,88]) have found that reanalysis Tmean generally performs better than Tmax and Tmin, while a better agreement is often found for Tmax than for Tmin [63,75,89]. Several studies have reported that reanalysis datasets tend to slightly underestimate Tmax and overestimate Tmin before bias correction, including studies in Italy [75,77,89], Greece [90], and Portugal [63], as well as studies on a global scale [88]. Simple bias corrections based on monthly regional mean differences between ground-based measurements and reanalysis data may be an effective tool to improve the performance of reanalysis data [89].
In summary, the reduction in RMSE and NRMSE values, together with the increase in the EF values, demonstrates that the applied correction effectively reduced systematic errors and improved agreement with the observed data.

3.2. Seasonal Forecasts Direct Validation

Direct validation involves comparing the ECMWF SEAS5 seasonal temperature forecasts with the AgERA5 gridded data. This allowed the assessment of the forecast system’s performance in predicting temperature at both seasonal and monthly scales over the CIS.

3.2.1. Monthly Validation

As SWF covers a long period of time (seven months), it is important to assess their usefulness not only in terms of overall seasonal performance, but also at different stages within this period. The statistical accuracy indicators do not show a clear tendency for forecast performance to deteriorate with increasing lead time (Table 4). Errors do not consistently increase (or decrease) with the lead time; therefore, the seventh month is not necessarily the worst across all variables, nor is the performance of the first month necessarily the best (although it tends to be the more accurate for Tmin and Tmean). It should be noted that the MAE is significantly different from zero for all variables in all months. However, in the case of PBIAS, although there is a significant bias in all months for Tmin, the same is not true for Tmean, for which there is only a significant bias in the fourth and fifth months (Table 4).
The results also show high dispersion of the SWF-reanalysis temperature pair, particularly after the first lead month. Therefore, the results suggest that forecast accuracy may be influenced not only by the temporal distance from the initialization date of the forecast, but also by other factors, such as the intrinsic climatic characteristics of each target month [91,92,93]. For example, depending on the target variable, regional climate dynamics and variability patterns, mid-summer months such as July and August may be more predictable than transition months such as April. This is true for Tmax but not for Tmin. These results are in line with previous studies. For instance, Lalic et al. [38] reported that temperature forecasts for May and June have a lower RMSE than those for March and April. Similarly, Santos et al. [41] reported lower MAE in summer months compared to transition months such as April or September, despite the forecast lead time.
When analysing the correlation and anomaly prediction capability (ACC) results, a significant decline in performance is evident, at a level of significance (α) of 0.05, from the third month onward (Table 4). A similar pattern is observed for forecast skill, as measured by CRPSS; however, this decline is more evident for Tmin and Tmean. These results suggest that the raw Tmin and Tmean forecasts are mostly useful for the first two lead months, with a sharp decline in performance thereafter. Tmax forecast skill is somewhat erratic, demonstrating poor performance during the first three leading months and in the last month. Bento et al. [42] also reported a clear deterioration in the skill of SEAS5 temperature forecasts after the first month. However, it is noteworthy that, in this study, the seventh month does not perform the worst performing month across all metrics or variables. This supports the idea that other factors can play a significant role in forecast performance beyond the simple effect of lead time.
It should be noted that this analysis is based on raw SWF extracted from a single grid point in the dataset and only considers one initialization month (April). A more extensive spatial and temporal analysis would be necessary to gain a clearer insight into the degradation of forecast performance with lead time. Furthermore, using post-processing techniques, such as bias correction or statistical downscaling, could significantly improve forecast accuracy and potentially extend the temporal range of time over which forecasts are useful. Therefore, these results should be interpreted as a preliminary assessment of raw forecast performance, highlighting the limitations and potential for refinement. However, these issues are beyond the scope of the current study.

3.2.2. Seasonal Validation

Figure 5 shows the results comparing seasonal temperature values from the reanalysis with those from the SWF. The results show that the mean forecast ensemble temperature data are in good agreement with the reanalysis, with no clear tendency to over- or underestimate the Tmean along the considered period. However, the accuracy and skill indicators of the forecast data (Table 5), show that the Tmax forecast slightly underestimates the reanalysis data, while the Tmin forecast strongly overestimates them, as reported by other studies (e.g., [94]). These opposing biases tend to cancel each other out, reducing the overall error in estimating Tmean (Figure 5). The results indicate that the forecasts are more accurate in estimating Tmean than Tmax and Tmin, although a slight overestimation of Tmean remains (Table 5). Nevertheless, the error and bias are significant for all variables at the 95% confidence level (Table 5).
There is a considerable variation in the temperature bias of SWF, depending on the forecast model, season and region. There is no consensus in the literature as some studies report overestimation and others report underestimation. Many studies report that SWF tends to underestimate temperatures. For example, Renan et al. [95] found a cold bias in WRF model simulations applied to New Zealand, particularly during the southern hemisphere summer. Similarly, Ji et al. [96] reported that the WRF model systematically underestimated temperatures in Australia (by 2–3 °C for Tmax and 1–2 °C for Tmin). Ferreira et al. [97] reported a cold bias in SEAS5 for South America. Furthermore, studies in central and southern Europe [17,35,38,39,98] also reported a general underestimation of temperature by seasonal forecasting systems. However, in the present study, the significant overestimation of Tmin prevented a general underestimation of Tmean.
The results also show that the SWF model is more accurate and skilful in forecasting Tmax than Tmin, as evidenced by lower estimation errors and higher R2 values (Table 5). However, the ensemble amplitude, which represents forecast uncertainty, is greater for Tmax than for Tmin (Figure 5).
There was a satisfactory agreement between the SWF anomalies and those of the reanalysis, with ACC > 0.40 (Table 5). This is especially true in the case of Tmax, where there is agreement with a significance level of 0.05. Furthermore, the SWF skill assessed with the SAI (Figure 6) supports these findings, suggesting that the anomaly signal was accurately captured by the forecasts in 80% of the years for Tmax, 60% for Tmin, and 70% for Tmean. Patterson et al. [99] reported good agreement when analysing the summer temperature anomalies in Europe. In contrast, Calì Quaglia et al. [47] reported a negative ACC for winter and a slightly positive value for summer for Portugal using ECMWF seasonal forecasts.
Analysis of the results for the other skill indicator, CRPSS, shows that using SWF data does not provide a significant advantage over the historical average (Table 5). In fact, for Tmin, the forecasts are considerably worse than the historical baseline. Tmean is the only variable with a positive CRPSS; however, all the values of the CRPSS are close to zero, indicating that temperature forecasts provide no meaningful added value compared to the historical average.

3.3. Seasonal Forecast Indirect Validation

Figure 7 shows the results of comparing forecasted and observed (reanalysis) crop cycle duration estimates using the GDD approach (Equation (2)), highlighting key trends and anomalies and reflecting the sensitivity of crop cycle duration estimation to temperature biases in the input data. Table 6 summarises the results of the accuracy and skill indicators used to assess the SWF ability to predict the crop cycle of the selected crops over the 10-year period (2013–2022). The results show that temperature forecasts cannot perfectly replicate the effects of climatic variability during the crop cycle.
Following the results of the SWF Tmean overestimation (Table 5), the results show that, overall, the forecasted crop cycles do not differ substantially from the reference (reanalysis) values but tend to underestimate the cycle duration (positive PBIAS) (Table 6). Notwithstanding, the error and bias are significant (α = 0.05); on average, the underestimation is about one week (i.e., MAE ranging from 4.8 to 8.5 days). Lower accuracy was reported in the study by Yang et al. [36] when using ECMWF SEAS5 forecasts to simulate the phenological development of vineyards in Portugal, with a potential forecast error of up to two weeks and an overall moderate forecast skill. Conversely, Garcia et al. [35] reported that WRF-based seasonal forecasts could lead to significant overestimates, with maize crop cycles in Portugal being extended by up to 60 days due to significant temperature underestimation by the SWF. Similar overestimates were also reported in the same study for wheat and maize in France and Greece. The error obtained in the current study, i.e., one week, can be considered adequate for supporting farmers’ decision-making, particularly since the information is made available at the start of the season, i.e., seven months ahead. This level of estimation error is comparable to that obtained using Earth observation methods to retrieve crop growth stages from vegetation index time series. This is considered one of the most accurate approaches currently available for characterising the crop cycle as the accuracy is limited by the satellite revisit time [100,101]. Thus, the near real-time support also presents lags.
The results for the colder year of the data series (2014) indicate longer crop cycles for all crops. Although the ensemble did not capture the observed value within the interquartile range around the median value, it was able to capture the variability with a wider spread compared to other years. In this year, both the ensemble range and the maximum value were higher, indicating that the seasonal forecasting system was sensitive to some extent to the uncertainty associated with the atypical weather conditions and the nature of the anomaly.
Over the 10-year period, a general trend towards shorter crop cycles is observed (Figure 7), due to the tendency of Tmean to increase, as Espírito Santo et al. [102] reported for Portugal. Various studies confirm this global warming trend [103,104], which significantly impacts the shortening of crop cycles and, consequently, crop yields [25,58,105]. The forecasts effectively capture this trend, and the signal of anomalies are significantly correlated, as indicated by the ACC and SAI metrics (Table 6 and Figure 8). Therefore, these results demonstrate the potential of using SWF to predict crop growth cycles in advance when considering the observed climate trends in the region studied. This renders studies using fixed dates or tabulated crop cycle lengths outdated.
It is important to note that the CRPSS values were positive for three of the four selected crops (Table 6). These results suggest that the ECMWF SEAS5 seasonal temperature forecasts have a reasonable skill and advantage over the historical average at estimating crop cycle duration for the selected crops in the CIS, except for sunflower, for which the CRPSS value was negative, but close to zero (Table 6).
In addition to assessing the ability of the SWF to estimate crop cycle duration by replicating climate variability, the accuracy of estimating the length of crop cycles was also evaluated, taking into account the variability in crop conditions from one year to the next, over the 2017–2019 period. Analysis of Table 7 shows that difference in estimated crop cycle length between the SWF and the AgERA5 data ranged from −12 to 4 days for maize, from −11 to 5 days for melon, from −7 to 1 days for sunflower and −6 to 4 days for tomato. Overall, the SWF once again presents a mean difference of around one week (see Table 6). This is within the range of variation in crop cycle duration observed using satellite data. As shown in Table 1, there is considerable variability in GDD values and cycle lengths across the various years (2017–2019), reflecting differences in both climatic conditions and agronomic practices. Therefore, it can be stated that the SWF has great potential to reduce the errors introduced by using tabulated/fixed crop cycles values, which can be inaccurate by several weeks. This error is lower than the deviations that can result due to the use of different cultivars, or to the use of diverse cultural practices, thus providing good prospects for the use of SWF to support farmers’ decision-making.

4. Conclusions

This study highlights the potential of integrating ground-based observations, Earth observation data, reanalysis datasets and SWF data into GDD tools to support agricultural decision-making under climate variability. The results show that the bias-corrected AgERA5 reanalysis datasets offer accurate temperature estimates, enabling effective upscaling from point (weather station) measurements to irrigation system scale.
Evaluating the ECMWF SEAS5 raw seasonal forecasts (seven months) showed persistent temperature biases, with a tendency to underestimate Tmax and overestimate Tmin, but with small errors in the estimates of approximately 1 °C and 2 °C, respectively. These opposite errors partially offset each other, resulting in improved estimates of Tmean; however, a slight overestimation was observed. When applying the GDD approach, these temperature biases affected accumulation, leading to a consistent underestimation of crop cycle duration for the spring–-summer crops of around eight days for maize, seven days for melon, nine days for sunflower and five days for tomato.
Forecast skill declined non-linearly with lead time, particularly beyond the second month, reflecting the influence of seasonal climate variability. However, the forecasts captured important signals, such as the general warming trend over the period 2013–2022 and interannual variability, particularly for Tmax and Tmean. Skill metrics, including ACC, SAI and CRPSS, indicated that the raw SWF provided marginal added value over historical climatology for most crops.
Overall, the results support the use of uncorrected (raw) seasonal temperature forecasts to inform early season planning and adaptive management practices, such as adjusting planting and harvesting schedules or fertiliser management. Integrating these forecasts into GDD-based decision-support tools could contribute to more informed decisions, promoting yield optimisation and improving the efficiency with which resources are used, particularly water, in water-scarce agricultural regions. Although the presented methodology can be transferred and applied to other regions, the specific results depend on local agro-climatic conditions and should therefore be interpreted in the context of the targeted region. Future work should focus on applying different bias correction methods and further validating the SWF at broader spatial and temporal scales, with the aim of improving its operational value in climate-resilient agriculture.

Author Contributions

Conceptualization, D.G. and P.P.; Methodology, D.G. and P.P.; Software, D.G., N.S. and A.F.; Validation, D.G. and N.S.; Formal analysis, D.G., N.S., A.F. and P.P.; Investigation, J.R. and P.P.; Resources, D.G. and A.F.; Data curation, D.G. and A.F.; Writing—original draft, D.G. and N.S.; Writing—review & editing, D.G., J.R., A.F., J.A.S., M.d.R.C. and P.P.; Visualization, D.G. and N.S.; Supervision, J.R., J.A.S. and P.P.; Project administration, P.P.; Funding acquisition, P.P. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by FCT—Fundação para a Ciência e a Tecnologia, I.P., through the project WaterQB 2022.04553.PTDC (https://doi.org/10.54499/2022.04553.PTDC).

Data Availability Statement

The data presented in this study are available on request from the corresponding authors.

Acknowledgments

The support of FCT—Fundação para a Ciência e a Tecnologia, I.P., under the projects WaterQB 2022.04553.PTDC (https://doi.org/10.54499/2022.04553.PTDC), UIDB/04129/2020 of LEAF-Linking Landscape, Environment, Agriculture and Food, Research Unit, LA/P/0092/2020 of Associate Laboratory TERRA, Centre for the Research and Technology of Agro-Environmental and Biological Sciences CITAB (UID/04033, (https://doi.org/10.54499/UIDB/04033/2020) and Associate Laboratory Inov4Agro (LA/P/0126/2020, https://doi.org/10.54499/LA/P/0126/2020) are also acknowledged.

Conflicts of Interest

The authors declare no conflicts of interest.

Appendix A

Table A1. Performance Metrics for Seasonal Forecast Evaluation.
Table A1. Performance Metrics for Seasonal Forecast Evaluation.
IndicatorEquationDescription
Bias Percentage
(PBIAS)
100 × i n ( R i F i ) i = 1 n R i Ri is the reanalysis based value, Fi is the seasonal forecast based value, in the year i, and n is the number of years. Quantifies the average tendency of the forecast data to overestimate or underestimate the reference values. Positive values indicate forecast underestimation, while negative values indicate forecast overestimation. Deterministic approach using the forecast ensemble median.
Coefficient of Determination
(R2)
i = 1 n ( F ^ i F ¯ ) ² i = 1 n ( F i F ¯ ) ² Fi is the seasonal forecast based value, in the year i, and n is the number of years, F ^ i is the regression line adjusted forecast based value, F ¯ is the mean of forecast based values. Measures the proportion of variance in the reanalysis values explained by the forecast model. Ranges from 0 to 1. Higher R2 values indicate that a large proportion of the variance in reanalysis values is explained by the forecasts. Deterministic approach using the forecast ensemble median.
Mean Absolute Error
(MAE)
i = 1 n F i R i n Ri is the reanalysis based value, Fi is the seasonal forecast based value, in the year i, and n is the number of years. Measures the average magnitude of errors between forecasts and reference values, without considering their direction. Lower values indicate better accuracy. Deterministic approach using the forecast ensemble median.
Root Mean Square Error
(RMSE)
i = 1 n ( R i F i ) ² n Ri is the reanalysis based value, Fi is the seasonal forecast based value, in the year i, and n is the number of years. Measures the square root of the average squared differences between forecasts and reference values. Penalises larger errors more than MAE. Deterministic approach using the forecast ensemble median.
Normalised Root Mean Square Error
(NRMSE)
100 × R M S E R ¯ R ¯ is the mean of reanalysis based values. Provides a dimensionless measure of the model’s relative error. Useful for comparing performance across variables or scales. Deterministic approach using the forecast ensemble median.
Standardised Anomaly Index
(SAI)
T T c σ T is the mean seasonal temperature mean for a given year, Tc is the long-term (2013–2022) mean seasonal temperature, and σ is the standard deviation of the seasonal temperature mean for the long-term dataset. Measures the standardised anomaly of seasonal temperature. Indicates how many standard deviations the seasonal value deviates from the long-term mean. Deterministic approach using the forecast ensemble median.
Anomaly Correlation Coefficient
(ACC)
i = 1 n ( F i F c ) ( R i R c ) n i = 1 n ( F i F c ) 2 n · i = 1 n ( R i R c ) 2 n Ri is the reanalysis based value, Rc the is the long-term (2013–2022) reanalysis mean, Fi is the seasonal forecast based value, Fc is the long-term forecast mean, in the year i, and n is the number of years. Measures the correlation between forecast anomalies and observed anomalies. Ranges from −1 to 1, with positive values indicating agreement between forecast and reanalysis anomalies. Reanalysis anomalies were calculated relative to the 10-year reanalysis dataset, while the forecast anomalies were calculated relative to the 10-year forecast dataset. Deterministic approach using the forecast ensemble median.
Continuous Ranked Probability Skill Score
(CRPSS)
1 C R P S F C R P S R CRPSF and CRPSR are the continuous ranked probability score for the forecast and the reanalysis, respectively. Quantifies the skill of the forecast in relation to the reanalysis based climatology. A CRPSS of 1 means a perfect forecast, 0 means the forecast is as good as the reanalysis historical average, and negative values indicate worse skill than the long-term average. This analysis was performed using the SeaVal: Validation of Seasonal Weather Forecasts R package. Probabilistic approach using all the forecast ensemble members.

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Figure 1. Flowchart with the schematic representation of the seasonal forecast assessment procedure. CIS—Caia Irrigation Scheme; GDD—Growing Degree-Day; SF—Seasonal Weather Forecasts.
Figure 1. Flowchart with the schematic representation of the seasonal forecast assessment procedure. CIS—Caia Irrigation Scheme; GDD—Growing Degree-Day; SF—Seasonal Weather Forecasts.
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Figure 2. Localization of the Caia Irrigation Scheme, Elvas, Portugal, weather station, reanalysis, and SWF grids.
Figure 2. Localization of the Caia Irrigation Scheme, Elvas, Portugal, weather station, reanalysis, and SWF grids.
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Figure 3. Long-term (2002–2021) historical meteorological characterisation of the Caia Irrigation Scheme (38°53′27″ N, 07°08′23″ W, 208 m a.s.l.), Elvas, Portugal. (Blue bars—precipitation; orange line—Tmax; pink line—Tmean; green line—Tmin).
Figure 3. Long-term (2002–2021) historical meteorological characterisation of the Caia Irrigation Scheme (38°53′27″ N, 07°08′23″ W, 208 m a.s.l.), Elvas, Portugal. (Blue bars—precipitation; orange line—Tmax; pink line—Tmean; green line—Tmin).
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Figure 4. Comparison of ground truth (observed) and reanalysis (predicted) maximum () and minimum () temperature data (left) before correction and (right) after correction.
Figure 4. Comparison of ground truth (observed) and reanalysis (predicted) maximum () and minimum () temperature data (left) before correction and (right) after correction.
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Figure 5. Box and whisker plots representing seasonal forecast ensemble of temperature data for April–September mean maximum (Tmax), minimum (Tmin), and mean (Tmean) temperatures, with dots and red squares representing the reanalysis mean of the temperature data.
Figure 5. Box and whisker plots representing seasonal forecast ensemble of temperature data for April–September mean maximum (Tmax), minimum (Tmin), and mean (Tmean) temperatures, with dots and red squares representing the reanalysis mean of the temperature data.
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Figure 6. Standardised anomaly index (SAI) of temperature over the 2013–2022 period. Black-dashed lines represent SWF estimates; red solid lines correspond to reanalysis-based values. (a) Tmax; (b) Tmin; (c) Tmean.
Figure 6. Standardised anomaly index (SAI) of temperature over the 2013–2022 period. Black-dashed lines represent SWF estimates; red solid lines correspond to reanalysis-based values. (a) Tmax; (b) Tmin; (c) Tmean.
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Figure 7. Box and whisker plots for the crop cycle duration when estimated using the seasonal forecasts and the reanalysis (red dots) for: (a) maize; (b) melon; (c) sunflower; (d) tomato.
Figure 7. Box and whisker plots for the crop cycle duration when estimated using the seasonal forecasts and the reanalysis (red dots) for: (a) maize; (b) melon; (c) sunflower; (d) tomato.
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Figure 8. Standardised anomaly index (SAI) of crop cycle duration for maize, melon, sunflower, and tomato, over the 2013–2022 period in the Caia Irrigation Scheme. Black-dashed lines represent SWF estimates; red solid lines correspond to reanalysis-based values.
Figure 8. Standardised anomaly index (SAI) of crop cycle duration for maize, melon, sunflower, and tomato, over the 2013–2022 period in the Caia Irrigation Scheme. Black-dashed lines represent SWF estimates; red solid lines correspond to reanalysis-based values.
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Table 1. Crop cycle characteristics derived from NDVI satellite data (2017–2019).
Table 1. Crop cycle characteristics derived from NDVI satellite data (2017–2019).
CropYearSowing/
Planting
HarvestLengthCGDD
Maize2017Apr 25Sep 81371929
2018May 7Sep 111281668
2019Apr 12Sep 81501827
Melon2017Apr 30Aug 291221753
2018Not available
2019May 7Aug 211071366
Sunflower2017May 20Sep 231272155
2018Apr 27Aug 221181619
2019Apr 12Aug 111221619
Tomato2017Apr 25Sep 11302173
2018Not available
2019Apr 2Aug 111321784
Table 2. Temperature and CGDD requirements to complete each crop growth stage and for the total crop season for maize, melon, sunflower, and tomato in Caia Irrigation Scheme, Portugal (Adapted from Ferreira et al. [52]).
Table 2. Temperature and CGDD requirements to complete each crop growth stage and for the total crop season for maize, melon, sunflower, and tomato in Caia Irrigation Scheme, Portugal (Adapted from Ferreira et al. [52]).
CropSowing/
Planting
Length (Days)Tbase
(°C)
Tupper (°C)Initial
CGDDini
Develop.
CGDDdev
Mid-Season
CGDDmid
Harvest
CGDDlate
Total CGDD
Maize25 Apr 137 10321363428565961929
Melon30 Apr 122 10383564285254451753
Sunflower20 May 127 8303925747384512155
Tomato25 Apr 130 7283476469442362173
Tbase is the base temperature (°C); Tupper is the cut-off temperature (°C); CGDD is the cumulative growing degree-day; Develop.—development stage.
Table 3. Statistical comparison between observed maximum, minimum, and mean temperature and the AgERA5 reanalysis (±standard deviation) (2013–2022).
Table 3. Statistical comparison between observed maximum, minimum, and mean temperature and the AgERA5 reanalysis (±standard deviation) (2013–2022).
Maximum TemperatureMinimum TemperatureMean Temperature
IndicatorsBefore Bias CorrectionAfter Bias CorrectionBefore Bias CorrectionAfter Bias CorrectionBefore Bias CorrectionAfter Bias Correction
b00.94 ± 0.011.01 ± 0.011.15 ± 0.021.00 ± 0.021.02 ± 0.011.01 ± 0.00
RMSE (°C)1.89 ± 0.081.21 ± 0.402.52 ± 0.251.57 ± 0.121.02 ± 0.040.98 ± 0.03
NRMSE (%)7.62 ± 0.325.58 ± 0.1725.88 ± 2.5216.13 ± 1.185.88 ± 0.215.63 ± 0.19
EF0.95 ± 0.010.97 ± 0.000.80 ± 0.040.92 ± 0.010.98 ± 0.000.98 ± 0.00
b0 is the regression coefficient; RMSE is the root mean square error; NRMSE is the normalised RMSE; EF—Nash and Sutcliff [74] model efficiency.
Table 4. Seasonal forecasts’ monthly temperature accuracy and skill assessment.
Table 4. Seasonal forecasts’ monthly temperature accuracy and skill assessment.
VariableStatistical
Indicator
1st
Month
(April)
2nd
Month
(May)
3rd
Month
(June)
4th
Month
(July)
5th
Month
(August)
6th
Month
(September)
7th
Month
(October)
TmaxPBIAS (%)8.54 *9.20 *1.49−0.031.092.1110.27 *
MAE (°C)1.91 *2.73 *1.53 *1.68 *1.15 *1.70 *2.70 *
RMSE (°C)2.163.041.941.931.341.863.24
NRMSE (%)9.7811.106.165.393.745.9112.29
R20.520.480.000.300.090.060.07
ACC0.72 *0.69 *0.060.540.30−0.240.27
CRPSS−0.40−0.16−0.050.190.090.01−0.61
TminPBIAS (%)−10.01 *−10.33 *−14.41 *−17.38 *−17.22 *−16.09 *−11.28 *
MAE (°C)0.81 *1.22 *2.23 *2.87 *2.83 *2.42 *1.34 *
RMSE (°C)0.951.642.473.233.002.611.70
NRMSE (%)11.7814.8517.2619.5718.2317.8514.89
R20.710.310.000.060.010.200.00
ACC0.84 *0.56−0.030.24−0.09−0.440.03
CRPSS0.050.06−0.92−1.15−2.59−1.76−0.39
TmeanPBIAS (%)3.433.59−3.44−5.56 *−4.72 *−3.423.76
MAE (°C)0.70 *1.37 *1.63 *1.91 *1.44 *1.28 *1.08 *
RMSE (°C)0.881.571.822.271.731.541.48
NRMSE (%)5.838.177.938.666.606.687.81
R20.620.420.000.100.010.050.06
ACC0.79 *0.65 *−0.040.32−0.08−0.220.24
CRPSS0.280.25−0.13−0.07−0.34−0.030.08
* PBIAS, MAE, ACC statistical significance (α = 0.05).
Table 5. Temperature seasonal forecast accuracy and skill assessment.
Table 5. Temperature seasonal forecast accuracy and skill assessment.
VariablePBIASR2MAERMSENRMSEACCCRPSS
Tmax3.48 *0.441.07 *1.254.050.66 *−0.30
Tmin−15.01 *0.162.03 *2.0815.360.40−4.33
Tmean−2.17 *0.380.57 *0.703.170.610.06
* PBIAS, MAE, ACC statistical significance (α = 0.05).
Table 6. Seasonal forecast accuracy and skill assessment for the crop cycle duration estimation of selected cereal and vegetable crops, during 2013–2022 at the Caia Irrigation Scheme.
Table 6. Seasonal forecast accuracy and skill assessment for the crop cycle duration estimation of selected cereal and vegetable crops, during 2013–2022 at the Caia Irrigation Scheme.
CropPBIAS
(%)
R2MAE
(Days)
RMSE
(Days)
NRMSE
(%)
ACCCRPSS
Maize4.5 *0.467.70 *9.446.50.68 *0.15
Melon4.1 *0.397.10 *8.316.40.630.16
Sunflower6.2 *0.438.50 *10.888.10.66 *−0.08
Tomato2.10.464.80 *5.313.90.67 *0.26
* PBIAS, MAE, ACC statistical significance (α = 0.05).
Table 7. Difference in crop cycle length derived from NDVI satellite data, reanalysis AgERA5 data and SEAS5 seasonal forecast data (SF) (2017–2019).
Table 7. Difference in crop cycle length derived from NDVI satellite data, reanalysis AgERA5 data and SEAS5 seasonal forecast data (SF) (2017–2019).
CropYearLengthLength
AgERA5
Length
SF
Difference
(SF-AgERA5)
Maize20171371351394
2018128128117−11
2019150148136−12
Melon20171221201255
2018Not available
201910710594−11
Sunflower20171271251261
2018118118109−9
2019122120113−7
Tomato20171301291334
2018Not available
2019132130124−6
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Garcia, D.; Silva, N.; Rolim, J.; Ferreira, A.; Santos, J.A.; Cameira, M.d.R.; Paredes, P. Prediction of Crops Cycle with Seasonal Forecasts to Support Decision-Making. Agronomy 2025, 15, 1291. https://doi.org/10.3390/agronomy15061291

AMA Style

Garcia D, Silva N, Rolim J, Ferreira A, Santos JA, Cameira MdR, Paredes P. Prediction of Crops Cycle with Seasonal Forecasts to Support Decision-Making. Agronomy. 2025; 15(6):1291. https://doi.org/10.3390/agronomy15061291

Chicago/Turabian Style

Garcia, Daniel, Nicolas Silva, João Rolim, Antónia Ferreira, João A. Santos, Maria do Rosário Cameira, and Paula Paredes. 2025. "Prediction of Crops Cycle with Seasonal Forecasts to Support Decision-Making" Agronomy 15, no. 6: 1291. https://doi.org/10.3390/agronomy15061291

APA Style

Garcia, D., Silva, N., Rolim, J., Ferreira, A., Santos, J. A., Cameira, M. d. R., & Paredes, P. (2025). Prediction of Crops Cycle with Seasonal Forecasts to Support Decision-Making. Agronomy, 15(6), 1291. https://doi.org/10.3390/agronomy15061291

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