Abstract
Energy costs are the main concerns of the agricultural stakeholders, because of their economic, environmental, and social impacts on the farms and the development of interrelated activities. In fact, it is important to save costs with the energy use to improve the profitability of the farms, but the level of these costs is often interlinked with the options to manage the energy consumption and the respective implications on sustainability. This framework highlights the importance of good management and planning for energy utilisation in the farming sector, namely to promote a balanced and integrated rural development. Considering these perspectives, this research intends to identify which factor, and how, impacted the energy costs in the European Union farms over the last decades. To achieve these objectives data from the Farm Accountancy Data Network database were considered for the European Union agricultural regions and the period 2013–2021. This statistical information was analysed through machine learning approaches following the procedures proposed by the software IBM SPSS Modeler. The linear support vector machine, regression, random forest, random trees, and the classification and regression tree are the most accurate models. On the contrary, the level of production, the size of farms, the economic and financial structure, and policy measures are the most important predictors. The findings here may be important insights for the European Union farming stakeholders, specifically to allow the design of policies for a more adjusted energy resources management.
1 Introduction
There is growing concern about social and territorial equilibrium, which calls for new approaches to managing territories and the various socio-economic activities that take place there [1]. Agriculture and the corresponding agricultural policies play an important role in territorial balance in rural areas [2]. It is therefore important to ensure the rational and appropriate use of resources by the agricultural sector in order to promote more sustainable rural development. Energy sources and the related farming costs are examples of how more rational management of these resources will lead to interesting gains in terms of sustainability.
The framework understanding of energy use in the farming sector is fundamental to supporting the farmers’ decisions and the policy design for better agricultural management. The digital transition and the respective approaches brought innovations that may contribute significantly to more sustainable development in different fields [3], including the agrifood chains. This is mainly essential to assess and implement more eco-friendly practices and processes, such as those related to circular economy [4] and bioeconomy. This transition is also central to supporting the development of new biotechnology fields [5].
These new methodologies may have a relevant added value, for example, in the following contexts: tomato disease identification through the deep convolutional neural network [6] and tea leaf disease prediction at the early phase [7]; assessing the potential for bioenergy production [8] and agricultural biomass use in the energy supply [9]; unmanned aerial vehicles challenges management [10]; solar energy prediction through neural networks in precision agriculture [11]; internet of things application [12]; leaf area index evaluation in vineyards considering small unmanned aerial systems [13]; contributions for the food, energy, and water frameworks understanding [14]; energy management approaches for vehicles used in agriculture [15]; farming production efficiency [16]; and corn production prediction [17].
These innovative technologies, associated with the concept of smart farming [18], allow us to collect of data with alternative approaches (unmanned aerial vehicles, for example), transmitting (through the Internet of Things innovations) the information in real-time to be assessed and process these data with methodologies of artificial intelligence (with higher accuracy). The implementation of smart farming methods promotes improvements in the quality of agricultural products and consequently increases the profitability of the farmers [19].
The relevance of the digital transition for agricultural and forestry activities seems to have acceptance in the scientific community [20]. Nonetheless, there is still some work to do [21], particularly to improve the efficiency of the related methodologies and consequently to reduce the costs associated with their application. Energy efficiency, network period and model accuracy have been concerns for the researchers [22] who work with the new technologies and procedures.
Considering this scenario, this study aims to analyse factors that influence the energy costs in the European Union farming sector, considering microeconomic data for the period 2013–2021 obtained from the Farm Accountancy Data Network (FADN) [23] database for the agricultural regions. The statistical information is presented in this database for representative farms of each European Union agricultural region. These data were assessed through machine learning approaches following the IBM SPSS Modeler [24] procedures and taking into account the findings of Martinho [25,26]. For the literature review the most relevant documents were identified (for the topics “energy,” “agricultur*,” and “machine learning”) through bibliometric analysis [27] and considering the VOSviewer [28,29,30] software procedures for bibliographic data and bibliographic coupling links. The selection of these topics, on 24 February 2024, for the bibliometric assessment was based on a compromise between obtaining a reasonable number of studies for the literature survey and their relation with the objectives of this research. Panel data regression techniques were also taken into account following Stata software [31,32,33] procedures, Torres-Reyna [34] suggestions, and developments of Hoechle [35]. To better understand the relationships between some variables a Spearman’s rank correlation [36] matrix was obtained. The assessments carried out using these methodologies took into account potential problems related, among others, to multicollinearity, data partitioning, cross-validation, the most important metrics for evaluating the models used. These analyses were made following the procedures proposed by the software used (IBM SPSS Modeler and Stata).
The main contribution and innovation of this study lies in the consideration of machine learning approaches to identify the best-fitting models and the most important predictors of energy costs on farms in the agricultural regions of the European Union, using microeconomic information from the FADN. The perspective here is that more rational uses of energy resources in agriculture will ensure greater sustainability in the sector and promote better territorial balance. The scientific literature available on the topics addressed, namely agricultural energy, machine learning approaches, and FADN data is scarce and warrants new contributions.
2 Literature review
The several dimensions related to energy use in diverse socio-economic activities and processes, particularly in agriculture, have motivated different researchers over time. More recently, the relevance of artificial intelligence in these fields has been the focus of a significant number of studies. Some of these scientific contributions have given special attention, for example, to the following domains:
Data analysis and the supply chain planning [37];
Pest detection in precision agriculture [38];
Crop production assessment [39];
Internet of Things vulnerabilities [40];
Cattle behaviour analysis [41];
Privacy and trustworthiness on Internet of Things systems [42];
Spray management in vineyards [43];
Robustness of Internet of Things data transmission [44];
Triboelectric nanogenerators and Internet of Things [45];
Farm monitoring [46];
Mapping the soil [47];
Net radiation estimation [48];
Greenhouse climate regulation [49];
Crop landscape mapping [50];
Solid fuels classification [51];
Artificial neural networks applications in greenhouse [52];
Photosynthetic capacities estimation [53];
Solar energy use in greenhouses [54];
Sorghum biomass prediction [58];
Well-organised agrophotovoltaic structure [59];
Weed control [60];
Environmental implications of corn farms [61];
Rubber tree evolution [62];
Irrigated areas mapping [63];
Deep learning constraints [64];
Agricultural practices and food security [65];
Wireless sensor network and precision agriculture [66];
Drought forecast [67];
Variety temperature forecast [68];
Soil moisture prediction [69]; and
Wireless sensor networks quality in terms of efficiency, privacy, and security [70].
These studies focused on the trustworthiness of the new approaches related to artificial intelligence, specifically on the collection and transmission of data through the Internet of Things technologies and wireless sensor networks. The prediction and mapping of the resources needed for agricultural production is another motivation for the researchers, as well as the farming yield forecast. The use of these new methodologies for a more adjusted management and planning of the activities inside the farms was also highlighted in the scientific literature.
The use of artificial intelligence opens, indeed, new opportunities for the different socio-economic sectors; nonetheless, some constraints may compromise, in some cases, the effective adoption of these innovations. Some of these limitations are related to the complexity of the methodologies, the needed resources, skills requirements, and some distrust of the society about these approaches (namely because of the use of non-humans in some jobs) [71].
In any case, the use of smart farming approaches may be a plausible solution to deal with the current challenges created for the agricultural sector by climate change and the increased need for food for the world population, which has been growing. In these frameworks, water use is a concern for the agricultural stakeholders, and here, smart irrigation answers may bring relevant added value [72] for more sustainable agricultural management. Wireless sensor network plays a relevant role in smart farming innovation [73]. Global warming also brings new worries with the air and soil temperature forecast [74,75]. Data analysis is another motivation for the scientific community where digital innovations may contribute significantly [76].
The agricultural sector has specificities, and some of them need complex approaches to be managed. In these contexts, the contributions of novel solutions may support the decisions of the stakeholders for better options related, for instance, with the insemination practices in dairy cattle [77], energy use on dairy farms [78], food supply chain analysis [79], and agricultural land management [80].
Disease and pest control, crop selection, and water use are among the most critical decisions for farmers, and this requires innovative approaches for more adjusted agricultural plan design [81]. The application of new technologies for more sustainable water use in agriculture has attracted the interest of researchers [82,83,84], as well as crop productivity [85] and fruit harvesting [86].
3 Data analysis
On average, the energy cost/total input cost ratio in the European Union with 27 countries, after Brexit in 2020 (EU27_2020), presents a decreasing tendency over the period considered (2013–2021) and represents around 8% (Figure 1). This trend may represent good news, signifying a propensity for a more sustainable development; nonetheless, there are here several factors that may impact this evolution and need to be properly and deeper analysed in this research and future studies.

Weight of energy costs in total input costs for the EU27_2020 representative farms over the period 2013–2021.
Table 1 shows the results for the average energy costs in the European Union agricultural regions over the period 2013–2021. It should be noted that in these values, not all years have statistical information for the agricultural regions of Hamburg and Martinique.
Energy costs on average for the European Union agricultural regions over the period 2013–2021
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Note: The red cells represent the ten higher values, and the green ones are relative to the ten agricultural regions with the lower average energy costs.
Czechia, a relevant number of German agricultural regions, The Netherlands, and Slovakia agricultural regions have higher energy costs per representative farm, in some cases because of the dimension of the farms, in other cases due to the requirements of energy of the agricultural systems adopted and in other circumstances because of the economic conjuncture.
Some regions of Croatia, Greece, Poland, Portugal, Romania, and Spain have lower energy costs per farm. These findings need, however, to be further analysed to try to understand if these costs are a consequence of the prices, for example, or derived from the level of consumption related to the dynamics of the farm (or lower efficiency in the energy use). In particular, it is important to understand the importance of factors such as the type of crop and the size of the farm.
4 Machine learning approaches to identify important predictors of energy costs and accurate models
Linear support vector machine (LSVM), regression, random forest, random trees, and classification and regression (C&R) tree approaches are the most accurate models, considering the relative error (lower results) for the testing set (Table 2). The relative error is the way considered by the software used (IBM SPSS Modeler) to analyse the accuracy of the models tested. In any case, this way of analysing accuracy is considered the most relevant [87]. The higher accuracy of these models to predict the energy costs in the European Union farming regions is confirmed by Figure 2 for the relationships among the observed values and the predicted ones. The statistical information considered was obtained from the European Union FADN, and the results of the models were found using IBM SPSS Modeler procedures. LSVM is specifically relevant for datasets with a large number of variables. The regressions are common linear regressions, and the random forest is a tree model implemented in Python. Random trees are models characterised by multiple decision trees, and C&R tree is a classification and predictive method [24].
Accurate models to predict the energy costs in the European Union agricultural regions over the period 2013–2021
Model | Build time | Correlation | Number fields used | Relative error |
---|---|---|---|---|
LSVM | 4 | 1.000 | 168 | 0.000 |
Regression | 4 | 0.999 | 135 | 0.003 |
Random forest | 4 | 0.991 | 168 | 0.018 |
Random trees | 4 | 0.986 | 168 | 0.028 |
C&R tree | 4 | 0.982 | 52 | 0.039 |

Relationships between the observed energy costs and the predicted ones in the European Union agricultural regions over the period 2013–2021.
The most important predictors identified are, for example, the following (Table 3): cereals output, long and medium-term loans, total liabilities, cows’ milk production, total utilised agricultural area, total assets, and decoupled subsidies.
Important predictors of energy costs in the European Union regions over the period 2013–2021
Nodes | Importance |
---|---|
(SE155) Sugar beet (€/farm) | 0.025 |
(SE160) Oil-seed crops (€/farm) | 0.025 |
(SE630) Decoupled payments (€) | 0.034 |
(SE436) Total assets (€) | 0.038 |
(SE025) Total Utilised Agricultural Area (ha) | 0.040 |
(SE216) Cows’ milk and milk products (€/farm) | 0.048 |
(SE485) Total liabilities (€) | 0.057 |
(SE256) Other output (€/farm) | 0.059 |
(SE490) Long and medium-term loans (€) | 0.068 |
(SE140) Cereals (€/farm) | 0.069 |
These results reveal the importance of some productions for the level of energy costs in the European Union representative farms, as well as the dimension of these farms and their economic and financial structures. Another interesting finding is the relevance of the Common Agricultural Policy (CAP) instruments to explain and predict energy costs. This means that the CAP measures may be considered to mitigate some of these costs.
In the following subsections, the findings for each one of the five models with higher accuracy will be presented, considering the most important predictors identified.
4.1 Linear support vector machine results
Table 4 summarises the linear support vector machine model information, considering the energy costs as the target field and ten predictors input. Table 5 shows the importance of the total utilised agricultural area to predict the energy costs in the European Union agricultural regions (in the period 2013–2021), as well as the level of output of some specific productions. This is confirmed in Figure 3 for the relative importance of the predictors. The summary records of the model are highlighted in Table 6.
LSVM model information to predict energy costs in the European Union agricultural regions, over the period 2013–2021
Model information | |
---|---|
Target field | (SE345) Energy (€) |
Model building method | Linear SVM |
Number of predictors input | 10 |
Number of predictors in final model | 8 |
Regularisation type | L2 |
Penalty parameter (Lambda) | 0.1 |
Regression precision (Epsilon) | 0.1 |
LSVM parameter estimates to predict energy costs in the European Union agricultural regions, over the period 2013–2021
Parameter | Estimates |
---|---|
Intercept | 1072.519 |
(SE025) Total Utilised Agricultural Area (ha) | 40.442 |
(SE140) Cereals (€/farm) | 0.038 |
(SE155) Sugar beet (€/farm) | −0.018 |
(SE160) Oil-seed crops (€/farm) | 0.044 |
(SE216) Cows’ milk and milk products (€/farm) | 0.053 |
(SE256) Other output (€/farm) | 0.187 |
(SE436) Total assets (€) | 0.003 |
(SE485) Total liabilities (€) | 0.001 |
(SE490) Long and medium-term loans (€) | −0.005 |
(SE630) Decoupled payments (€) | 0.015 |

Predictor importance of the energy costs in the European Union agricultural regions, over the period 2013–2021, considering LSVM model.
LSVM records summary to predict energy costs in the European Union agricultural regions over the period 2013–2021
Records | Number | Percentage |
---|---|---|
Included | 579 | 99.66 |
Excluded | 2 | 0.34 |
Total | 581 | 100 |
4.2 Regression model findings
The results for the regression model confirm the importance of some farming productions and the dimension of the farms to predict the energy costs (Tables 7 and 8). Another relevant finding is the relative importance of the decoupled payments to predict the energy costs in the European Union farms. This means that the CAP instruments may be taken into account to improve the efficiency in energy use and in this way mitigate the respective costs that represent about 8%, on average (for the representative farms and over the period here considered) in the total input costs.
Predictor importance of the energy costs in the European Union agricultural regions, over the period 2013–2021, considering a regression model
Nodes | Importance |
---|---|
(SE155) Sugar beet (€/farm) | 0.000 |
(SE490) Long and medium-term loans (€) | 0.000 |
(SE140) Cereals (€/farm) | 0.019 |
(SE485) Total liabilities (€) | 0.049 |
(SE160) Oil-seed crops (€/farm) | 0.077 |
(SE436) Total assets (€) | 0.121 |
(SE216) Cows’ milk and milk products (€/farm) | 0.128 |
(SE630) Decoupled payments (€) | 0.166 |
(SE025) Total utilised agricultural area (ha) | 0.207 |
(SE256) Other output (€/farm) | 0.233 |
Regression coefficients to predict energy costs in the European Union agricultural regions over the period 2013–2021
Unstandardised coefficients | Standard error | Standardised coefficients | t | Significance | |
---|---|---|---|---|---|
(Constant) | 390.694 | 181.179 | 2.156 | 0.031 | |
(SE025) Total utilised agricultural area (ha) | 35.802 | 5.490 | 0.220 | 6.521 | <0.001 |
(SE140) Cereals (€/farm) | 0.007 | 0.010 | 0.022 | 0.723 | 0.470 |
(SE155) Sugar beet (€/farm) | −0.028 | 0.030 | −0.010 | −0.958 | 0.338 |
(SE160) Oil-seed crops (€/farm) | 0.084 | 0.017 | 0.104 | 4.838 | <0.001 |
(SE216) Cows’ milk and milk products (€/farm) | 0.062 | 0.004 | 0.177 | 13.862 | <0.001 |
(SE256) Other output (€/farm) | 0.149 | 0.008 | 0.291 | 18.702 | <0.001 |
(SE436) Total assets (€) | 0.005 | 0.001 | 0.167 | 8.671 | <0.001 |
(SE485) Total liabilities (€) | 0.004 | 0.005 | 0.069 | 0.915 | 0.360 |
(SE490) Long and medium-term loans (€) | −0.014 | 0.005 | −0.192 | −2.824 | 0.005 |
(SE630) Decoupled payments (€) | 0.115 | 0.028 | 0.181 | 4.118 | <0.001 |
4.3 Random forest results
Figure 4 also highlights the relative importance of the following predictors: decoupled payments, total utilised agricultural area, long and medium-term loans, total assets, and cereals output. Nonetheless, considering the results from the regression model, the long and medium-term loans predict the energy costs in the farming context of the agricultural regions in the European Union member-states with a negative relationship.

Predictor importance of the energy costs in the European Union agricultural regions, over the period 2013–2021, considering a random forest model.
4.4 Random tree findings
For this model, the results reveal that the most important predictors are in decreasing order as follows (Figure 5): oil-seed crops output, total assets, cows’ milk output, long and medium-term loans, decoupled payments, sugar beet output, and cereals output. The total utilised agricultural area appears for this approach with a lower relative importance. In this model, the levels of output of some productions and the economic and financial structures have higher importance.

Predictor importance of the energy costs in the European Union agricultural regions, over the period 2013–2021, considering a random trees model.
4.5 C&R tree results
Considering the results presented in Figure 6, node 1 contains the observations when a representative farm of the European Union agricultural region has an oil-seed crop output lower, or equal, to 40,749 euros. A random European Union agricultural region has a 97% probability of belonging to this node with a predicted value for energy costs of 7809 euros. Terminal node 6 reveals that farms with higher oil-seed crop output have greater energy costs, and terminal node 21 presents that farms with lower oil-seed crop output, lower long and medium-term loans, lower hectares, and lower total assets have inferior energy costs.

C&R tree results to predict the energy costs in the European Union agricultural regions, over the period 2013–2021.
5 Regression results with panel data
To bring more insights into the energy cost explanation in the representative farms of the European Union agricultural regions, it seems interesting to simulate, through panel data approaches, the relationships between the energy costs in these farms and the variables identified in the previous sections to predict these costs. The independent variables were selected, taking into account the findings obtained before with machine learning methodologies and the variance inflation factor (VIF) test for multicollinearity.
In general, Table 9 shows that the energy costs in the European Union farming regions have strong (and statistically significant) correlations with the dimension of the farms, the level of output of some agricultural activities, the financial structure, and the amount of decoupled subsidies. When the total utilised agricultural area, oil-seed crops output, cows’ milk output, and total assets, in these farms, increase by 1%, the energy costs increase, respectively 0.42, 0.04, 0.11, and 0.50% (Table 10). To deal with statistical problems related to heteroscedasticity and autocorrelation, Prais–Winsten regressions were considered.
Spearman’s rank correlation matrix between energy costs and important predictors in the European Union agricultural regions over the period 2013–2021
(SE345) Energy (€) | (SE025) Total utilised agricultural area (ha) | (SE140) Cereals (€/farm) | (SE155) Sugar beet (€/farm) | (SE160) Oil-seed crops (€/farm) | (SE216) Cows’ milk and milk products (€/farm) | (SE256) Other output (€/farm) | (SE436) Total assets (€) | (SE485) Total liabilities (€) | (SE490) Long and medium-term loans (€) | (SE630) Decoupled payments (€) | |
---|---|---|---|---|---|---|---|---|---|---|---|
(SE345) Energy (€) | 1.000 | ||||||||||
(SE025) Total utilised agricultural area (ha) | 0.817 | 1.000 | |||||||||
(0.000) | |||||||||||
(SE140) Cereals (€/farm) | 0.792 | 0.844 | 1.000 | ||||||||
(0.000) | (0.000) | ||||||||||
(SE155) Sugar beet (€/farm) | 0.475 | 0.403 | 0.593 | 1.000 | |||||||
(0.000) | (0.000) | (0.000) | |||||||||
(SE160) Oil-seed crops (€/farm) | 0.623 | 0.721 | 0.897 | 0.556 | 1.000 | ||||||
(0.000) | (0.000) | (0.000) | (0.000) | ||||||||
(SE216) Cows’ milk and milk products (€/farm) | 0.738 | 0.640 | 0.623 | 0.469 | 0.469 | 1.000 | |||||
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | |||||||
(SE256) Other output (€/farm) | 0.844 | 0.632 | 0.624 | 0.471 | 0.500 | 0.677 | 1.000 | ||||
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | ||||||
(SE436) Total assets (€) | 0.799 | 0.621 | 0.593 | 0.493 | 0.406 | 0.751 | 0.791 | 1.000 | |||
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | |||||
(SE485) Total liabilities (€) | 0.860 | 0.790 | 0.700 | 0.485 | 0.599 | 0.730 | 0.817 | 0.750 | 1.000 | ||
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | ||||
(SE490) Long and medium-term loans (€) | 0.854 | 0.766 | 0.683 | 0.490 | 0.567 | 0.766 | 0.822 | 0.785 | 0.985 | 1.000 | |
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | |||
(SE630) Decoupled payments (€) | 0.868 | 0.934 | 0.880 | 0.517 | 0.739 | 0.725 | 0.715 | 0.736 | 0.798 | 0.791 | 1.000 |
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) |
Panel data regression results, through a linearised model with logarithms, for the European Union agricultural regions over the period 2013–2021
Prais–Winsten regression, heteroskedastic panels corrected standard errors, ln((SE345) Energy (€)) | Coefficient | Standard error | z | P > |z| |
---|---|---|---|---|
ln((SE025) Total utilised agricultural area (ha)) | 0.423 | 0.025 | 17.140 | 0.000 |
ln((SE155) Sugar beet (€/farm)) | −0.008 | 0.006 | −1.290 | 0.196 |
ln((SE160) Oil-seed crops (€/farm)) | 0.040 | 0.013 | 3.030 | 0.002 |
ln((SE216) Cows’ milk and milk products (€/farm)) | 0.111 | 0.013 | 8.530 | 0.000 |
ln((SE436) Total assets (€)) | 0.500 | 0.021 | 24.180 | 0.000 |
_cons | −0.458 | 0.204 | −2.240 | 0.025 |
VIF | 3.570 | |||
Hausman test | 6.050 (0.417) | |||
Modified Wald test for groupwise heteroskedasticity | 1.6 × 1029 (0.000) | |||
Wooldridge test for autocorrelation | 58.856 (0.000) |
To analyse the potential effects of inflation over the period considered and the differences in the prices between the European Union countries, the values in euros were deflated through the harmonised indices of consumer prices (HICP, all-items, 2015 = 100) and adjusted with the price level indices (PLI, gross domestic product, EU27_2020 = 100). These indices were obtained from the Eurostat [88]. Generally, the results for Spearman’s rank correlation coefficients (Table 11) and the panel data regressions (Table 12) are not so different from those presented in Tables 9 and 10, showing a non-relevant impact in these relationships from the prices.
Spearman’s rank correlation matrix between energy costs and important predictors in the European Union agricultural regions, over the period 2013–2021, with the variables in euros deflated with the HICP and corrected with the PLI
(SE345) Energy (€) | (SE025) Total utilised agricultural area (ha) | (SE140) Cereals (€/farm) | (SE155) Sugar beet (€/farm) | (SE160) Oil-seed crops (€/farm) | (SE216) Cows’ milk and milk products (€/farm) | (SE256) Other output (€/farm) | (SE436) Total assets (€) | (SE485) Total liabilities (€) | (SE490) Long and medium-term loans (€) | (SE630) Decoupled payments (€) | |
---|---|---|---|---|---|---|---|---|---|---|---|
(SE345) Energy (€) | 1.000 | ||||||||||
(SE025) Total utilised agricultural area (ha) | 0.814 | 1.000 | |||||||||
(0.000) | |||||||||||
(SE140) Cereals (€/farm) | 0.792 | 0.795 | 1.000 | ||||||||
(0.000) | (0.000) | ||||||||||
(SE155) Sugar beet (€/farm) | 0.462 | 0.395 | 0.577 | 1.000 | |||||||
(0.000) | (0.000) | (0.000) | |||||||||
(SE160) Oil-seed crops (€/farm) | 0.675 | 0.670 | 0.913 | 0.537 | 1.000 | ||||||
(0.000) | (0.000) | (0.000) | (0.000) | ||||||||
(SE216) Cows’ milk and milk products (€/farm) | 0.689 | 0.633 | 0.569 | 0.472 | 0.456 | 1.000 | |||||
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | |||||||
(SE256) Other output (€/farm) | 0.767 | 0.631 | 0.554 | 0.463 | 0.467 | 0.637 | 1.000 | ||||
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | ||||||
(SE436) Total assets (€) | 0.707 | 0.629 | 0.554 | 0.513 | 0.429 | 0.703 | 0.736 | 1.000 | |||
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | |||||
(SE485) Total liabilities (€) | 0.829 | 0.800 | 0.662 | 0.488 | 0.584 | 0.715 | 0.797 | 0.714 | 1.000 | ||
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | ||||
(SE490) Long- and medium-term loans (€) | 0.818 | 0.780 | 0.642 | 0.498 | 0.553 | 0.753 | 0.806 | 0.752 | 0.985 | 1.000 | |
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | |||
(SE630) Decoupled payments (€) | 0.847 | 0.921 | 0.883 | 0.502 | 0.784 | 0.667 | 0.630 | 0.655 | 0.767 | 0.752 | 1.000 |
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) |
Panel data regression results, through a linearised model with logarithms, for the European Union agricultural regions, over the period 2013–2021, with the variables in euros deflated with the HICP and corrected with the PLI
Prais–Winsten regression, heteroskedastic panels corrected standard errors, ln((SE345) energy (€)) | Coefficient | Standard error | Z | P > |z| |
---|---|---|---|---|
ln((SE025) Total utilised agricultural area (ha)) | 0.347 | 0.023 | 15.030 | 0.000 |
ln((SE155) Sugar beet (€/farm)) | −0.004 | 0.006 | −0.720 | 0.470 |
ln((SE160) Oil-seed crops (€/farm)) | 0.062 | 0.013 | 4.980 | 0.000 |
ln((SE216) Cows’ milk and milk products (€/farm)) | 0.106 | 0.011 | 9.670 | 0.000 |
ln((SE436) Total assets (€)) | 0.466 | 0.023 | 20.030 | 0.000 |
_cons | −3.260 | 0.106 | −30.720 | 0.000 |
VIF | 2.980 | |||
Hausman test | 3.690 (0.718) | |||
Modified Wald test for groupwise heteroskedasticity | 5.7 × 1030 (0.000) | |||
Wooldridge test for autocorrelation | 83.887 (0.000) |
Tables 13 and 14 present the results for the values in euros corrected with the HICP and PLI and considering the ratio (SE345) Energy (€)/(SE025) total utilised agricultural area (ha) instead of the variable (SE345) energy (€). The intention is to assess the energy costs corrected by the dimensions of the representative farms. In this case, Spearman’s rank correlation coefficients among the ratio and the other variables are all negative (Table 13), and the strongest correlations were found for the total utilised agricultural area (−0.607) and the decoupled payments (−0.419). When the total utilised agricultural area increases by 1%, the energy costs by hectare decrease by 0.62% (Table 14). The impacts from the other independent variables are similar to those verified before.
Spearman’s rank correlation matrix between energy costs/total utilised agricultural area and important predictors in the European Union agricultural regions, over the period 2013–2021, with the variables in euros deflated with the HICP and corrected with the PLI
(SE345) Energy (€)/(SE025) Total utilised agricultural area (ha) | (SE025) Total utilised agricultural area (ha) | (SE140) Cereals (€/farm) | (SE155) Sugar beet (€/farm) | (SE160) Oil-seed crops (€/farm) | (SE216) Cows’ milk and milk products (€/farm) | (SE256) Other output (€/farm) | (SE436) Total assets (€) | (SE485) Total liabilities (€) | (SE490) Long and medium-term loans (€) | (SE630) Decoupled payments (€) | |
---|---|---|---|---|---|---|---|---|---|---|---|
(SE345) Energy (€)/(SE025) total utilised agricultural area (ha) | 1.000 | ||||||||||
(SE025) Total utilised agricultural area (ha) | −0.607 | 1.000 | |||||||||
(0.000) | |||||||||||
(SE140) Cereals (€/farm) | −0.261 | 0.795 | 1.000 | ||||||||
(0.000) | (0.000) | ||||||||||
(SE155) Sugar beet (€/farm) | −0.026 | 0.395 | 0.577 | 1.000 | |||||||
(0.370) | (0.000) | (0.000) | |||||||||
(SE160) Oil-seed crops (€/farm) | −0.182 | 0.670 | 0.913 | 0.537 | 1.000 | ||||||
(0.000) | (0.000) | (0.000) | (0.000) | ||||||||
(SE216) Cows’ milk and milk products (€/farm) | −0.142 | 0.633 | 0.569 | 0.472 | 0.456 | 1.000 | |||||
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | |||||||
(SE256) Other output (€/farm) | −0.044 | 0.631 | 0.554 | 0.463 | 0.467 | 0.637 | 1.000 | ||||
(0.135) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | ||||||
(SE436) Total assets (€) | −0.134 | 0.629 | 0.554 | 0.513 | 0.429 | 0.703 | 0.736 | 1.000 | |||
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | |||||
(SE485) Total liabilities (€) | −0.270 | 0.800 | 0.662 | 0.488 | 0.584 | 0.715 | 0.797 | 0.714 | 1.000 | ||
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | ||||
(SE490) Long- and medium-term loans (€) | −0.259 | 0.780 | 0.642 | 0.498 | 0.553 | 0.753 | 0.806 | 0.752 | 0.985 | 1.000 | |
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | |||
(SE630) Decoupled payments (€) | −0.419 | 0.921 | 0.883 | 0.502 | 0.784 | 0.667 | 0.630 | 0.655 | 0.767 | 0.752 | 1.000 |
(0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) | (0.000) |
Panel data regression results, through a linearised model with logarithms, for the European Union agricultural regions, over the period 2013–2021, with the variables in euros deflated with the HICP and corrected with the PLI
Prais–Winsten regression, heteroskedastic panels corrected standard errors, ln((SE345) Energy (€)/(SE025) Total Utilised Agricultural Area (ha)) | Coefficient | Standard error | z | P > |z| |
---|---|---|---|---|
ln((SE025) Total utilised agricultural area (ha)) | −0.618 | 0.029 | −21.220 | 0.000 |
ln((SE155) Sugar beet (€/farm)) | 0.006 | 0.011 | 0.510 | 0.612 |
ln((SE160) Oil-seed crops (€/farm)) | 0.061 | 0.020 | 3.110 | 0.002 |
ln((SE216) Cows’ milk and milk products (€/farm)) | 0.070 | 0.011 | 6.390 | 0.000 |
ln((SE436) Total assets (€)) | 0.444 | 0.026 | 17.020 | 0.000 |
_cons | −3.256 | 0.169 | −19.310 | 0.000 |
VIF | 2.980 | |||
Hausman test | 3.690 (0.718) | |||
Modified Wald test for groupwise heteroskedasticity | 3.8 × 1030 (0.000) | |||
Wooldridge test for autocorrelation | 83.887 (0.000) |
6 Discussion
The energy costs represent a relevant part of the total inputs in the European Union farms, and in this perspective, it is important to bring more knowledge for a better understanding of these frameworks, namely to highlight the main predictors and variables that may explain the level of these costs. Another dimension is related to the identification of accurate models and algorithms to assess the associated contexts. In these conditions, this study aims to bring more insights into the explanation and prediction of the energy costs in the European Union agriculture, taking into account statistical information from the FADN and Eurostat databases, as well as machine learning approaches and panel data methodologies. The period of 2013–2021 was the period considered for the assessment here presented. The intention was to consider a period after the last enlargement of the European Union.
The literature review highlighted the relevant contribution of the digital transition for a better understanding of several socio-economic dimensions, particularly for a better analysis of the energy use in the farming sector [54]. An efficient use of energy resources is crucial for more sustainable development in the farming sector. The new technologies associated with era 4.0 have contributed to the different fields of energy use in the farms, since a more accurate prediction of the crop’s diseases until a more adjusted management of the related supply chains. This may contribute to improving the profitability of the farmers and increase the quality if the agrifood supply chains. Nonetheless, the use of smart farming approaches has not only advantages; there are also some concerns of the stakeholders with the use of these new techniques, and some of them are linked with the Internet of Things vulnerabilities, for example. The privacy and trustworthiness of the systems, particularly in the transmission of data, have concerned the scientific community. In addition, the competition of these approaches with the humans in some jobs, the skills and resources needed and the complex structure of these systems are other focus of discussion for the researchers [71].
The data analysis shows that for the period considered, the energy costs represented around 8% of the total input costs in the European Union farms. On the contrary, the farms from Czechia, Slovakia, The Netherlands, and some German agricultural regions have higher energy costs, because of the dimension of these agricultural units, the farming systems implemented, and the specificities of the economic/financial context of the countries. Inversely, agricultural regions from Croatia, Greece, Poland, Portugal, and Romania have inferior energy costs in their respective farms.
The assessment of the data through machine learning approaches highlighted the accuracy of the LSVM, regression, random forest, random trees, and C&R tree models to predict the energy costs in the farms of the European Union agricultural regions. The important predictors identified are related to the level of output of some productions (cereals, for example), the dimension of the farms (total utilised agricultural area), economic and financial structure (total assets and liabilities), and policy measures (this means that the CAP instruments may be eventually adjusted to mitigate energy costs).
The regressions carried out with panel data methodologies confirmed the importance of the total utilised agricultural farms of the farms to explain the energy costs, as well as the level of output of some farming productions and the level of total assets, including when the variables in euros were corrected for the inflation and the differences in the level of prices between the diverse European Union member-states. When the energy costs are adjusted by the dimension of the farms (energy costs/hectare), the strongest and negative Spearman’s rank correlation coefficients appeared for the number of hectares and the decoupled payments. Again, the CAP instruments appear here as a tool that may be reanalysed to better deal with the energy costs in the European Union agricultural regions.
7 Conclusions
In terms of practical implications, for a more efficient use of energy resources and to mitigate energy costs, the farms of some European Union agricultural regions, particularly the bigger and more dynamic ones, need to identify innovative approaches to make compatible these dimensions with a more sustainable development. Without a harmonious development of the agricultural sector, the consequence will be the abandonment of the activity with the risk of desertification of the most disadvantaged rural areas. Another implication will be the appearance of new focuses on territorial asymmetries due to inappropriate land management and incorrect definitions of policy instruments. For policy recommendations, it is suggested to adjust the CAP instruments (namely the decoupled payments) to promote the strongest sustainability in the European Union farms. For future research, it could be interesting to analyse further the impacts of the CAP measures on the energy costs of the farms, to better rethink them. It would be important, also, to make more inferences with the results, namely validate them with the context of each country.
Acknowledgments
Furthermore, we would like to thank the CERNAS Research Centre and the Polytechnic Institute of Viseu for their support.
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Funding information: This work was funded by National Funds through the FCT – Foundation for Science and Technology, I.P., within the scope of the project Refª UIDB/00681 (https://doi.org/10.54499/UIDP/00681/2020). This work was developed under the Science4Policy 2023 (S4P-23): annual science for policy project call, an initiative by PlanAPP - Competence Centre for Planning, Policy and Foresight in Public Administration in partnership with the Foundation for Science and Technology, financed by Portugal s Recovery and Resilience Plan.
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Author contribution: The author confirms the sole responsibility for the conception of the study, presented results and manuscript preparation.
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Conflict of interest: Vítor João Pereira Domingues Martinho, who is the author of this article, is a current Editorial Board member of Open Agriculture. The author states no conflict of interest.
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Data availability statement: The datasets generated during and/or analysed during the current study are available from the corresponding author on reasonable request.
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Articles in the same Issue
- Research Articles
- Optimization of sustainable corn–cattle integration in Gorontalo Province using goal programming
- Competitiveness of Indonesia’s nutmeg in global market
- Toward sustainable bioproducts from lignocellulosic biomass: Influence of chemical pretreatments on liquefied walnut shells
- Efficacy of Betaproteobacteria-based insecticides for managing whitefly, Bemisia tabaci (Hemiptera: Aleyrodidae), on cucumber plants
- Assessment of nutrition status of pineapple plants during ratoon season using diagnosis and recommendation integrated system
- Nutritional value and consumer assessment of 12 avocado crosses between cvs. Hass × Pionero
- The lacked access to beef in the low-income region: An evidence from the eastern part of Indonesia
- Comparison of milk consumption habits across two European countries: Pilot study in Portugal and France
- Antioxidant responses of black glutinous rice to drought and salinity stresses at different growth stages
- Differential efficacy of salicylic acid-induced resistance against bacterial blight caused by Xanthomonas oryzae pv. oryzae in rice genotypes
- Yield and vegetation index of different maize varieties and nitrogen doses under normal irrigation
- Urbanization and forecast possibilities of land use changes by 2050: New evidence in Ho Chi Minh city, Vietnam
- Organizational-economic efficiency of raspberry farming – case study of Kosovo
- Application of nitrogen-fixing purple non-sulfur bacteria in improving nitrogen uptake, growth, and yield of rice grown on extremely saline soil under greenhouse conditions
- Digital motivation, knowledge, and skills: Pathways to adaptive millennial farmers
- Investigation of biological characteristics of fruit development and physiological disorders of Musang King durian (Durio zibethinus Murr.)
- Enhancing rice yield and farmer welfare: Overcoming barriers to IPB 3S rice adoption in Indonesia
- Simulation model to realize soybean self-sufficiency and food security in Indonesia: A system dynamic approach
- Gender, empowerment, and rural sustainable development: A case study of crab business integration
- Metagenomic and metabolomic analyses of bacterial communities in short mackerel (Rastrelliger brachysoma) under storage conditions and inoculation of the histamine-producing bacterium
- Fostering women’s engagement in good agricultural practices within oil palm smallholdings: Evaluating the role of partnerships
- Increasing nitrogen use efficiency by reducing ammonia and nitrate losses from tomato production in Kabul, Afghanistan
- Physiological activities and yield of yacon potato are affected by soil water availability
- Vulnerability context due to COVID-19 and El Nino: Case study of poultry farming in South Sulawesi, Indonesia
- Wheat freshness recognition leveraging Gramian angular field and attention-augmented resnet
- Suggestions for promoting SOC storage within the carbon farming framework: Analyzing the INFOSOLO database
- Optimization of hot foam applications for thermal weed control in perennial crops and open-field vegetables
- Toxicity evaluation of metsulfuron-methyl, nicosulfuron, and methoxyfenozide as pesticides in Indonesia
- Fermentation parameters and nutritional value of silages from fodder mallow (Malva verticillata L.), white sweet clover (Melilotus albus Medik.), and their mixtures
- Five models and ten predictors for energy costs on farms in the European Union
- Effect of silvopastoral systems with integrated forest species from the Peruvian tropics on the soil chemical properties
- Transforming food systems in Semarang City, Indonesia: A short food supply chain model
- Understanding farmers’ behavior toward risk management practices and financial access: Evidence from chili farms in West Java, Indonesia
- Optimization of mixed botanical insecticides from Azadirachta indica and Calophyllum soulattri against Spodoptera frugiperda using response surface methodology
- Mapping socio-economic vulnerability and conflict in oil palm cultivation: A case study from West Papua, Indonesia
- Exploring rice consumption patterns and carbohydrate source diversification among the Indonesian community in Hungary
- Determinants of rice consumer lexicographic preferences in South Sulawesi Province, Indonesia
- Effect on growth and meat quality of weaned piglets and finishing pigs when hops (Humulus lupulus) are added to their rations
- Healthy motivations for food consumption in 16 countries
- The agriculture specialization through the lens of PESTLE analysis
- Combined application of chitosan-boron and chitosan-silicon nano-fertilizers with soybean protein hydrolysate to enhance rice growth and yield
- Stability and adaptability analyses to identify suitable high-yielding maize hybrids using PBSTAT-GE
- Phosphate-solubilizing bacteria-mediated rock phosphate utilization with poultry manure enhances soil nutrient dynamics and maize growth in semi-arid soil
- Factors impacting on purchasing decision of organic food in developing countries: A systematic review
- Influence of flowering plants in maize crop on the interaction network of Tetragonula laeviceps colonies
- Bacillus subtilis 34 and water-retaining polymer reduce Meloidogyne javanica damage in tomato plants under water stress
- Vachellia tortilis leaf meal improves antioxidant activity and colour stability of broiler meat
- Evaluating the competitiveness of leading coffee-producing nations: A comparative advantage analysis across coffee product categories
- Application of Lactiplantibacillus plantarum LP5 in vacuum-packaged cooked ham as a bioprotective culture
- Evaluation of tomato hybrid lines adapted to lowland
- South African commercial livestock farmers’ adaptation and coping strategies for agricultural drought
- Spatial analysis of desertification-sensitive areas in arid conditions based on modified MEDALUS approach and geospatial techniques
- Meta-analysis of the effect garlic (Allium sativum) on productive performance, egg quality, and lipid profiles in laying quails
- Review Articles
- Reference dietary patterns in Portugal: Mediterranean diet vs Atlantic diet
- Evaluating the nutritional, therapeutic, and economic potential of Tetragonia decumbens Mill.: A promising wild leafy vegetable for bio-saline agriculture in South Africa
- A review on apple cultivation in Morocco: Current situation and future prospects
- Quercus acorns as a component of human dietary patterns
- CRISPR/Cas-based detection systems – emerging tools for plant pathology
- Short Communications
- An analysis of consumer behavior regarding green product purchases in Semarang, Indonesia: The use of SEM-PLS and the AIDA model
- Effect of NaOH concentration on production of Na-CMC derived from pineapple waste collected from local society