Next Article in Journal
Exploring Pre-Service STEM Teachers’ Capacity to Teach Using a Gender-Responsive Approach
Previous Article in Journal
Modeling Climate Regulation of Arable Soils in Northern Saxony under the Influence of Climate Change and Management Practices
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Progress of the Agricultural Sector toward Climate Neutrality: Identification of Essential Stages

Institute of Energy Systems and Environment, Riga Technical University, 12/1 Azenes Street, LV1048 Riga, Latvia
*
Author to whom correspondence should be addressed.
Sustainability 2023, 15(14), 11136; https://doi.org/10.3390/su151411136
Submission received: 16 June 2023 / Revised: 4 July 2023 / Accepted: 11 July 2023 / Published: 17 July 2023
(This article belongs to the Section Sustainable Management)

Abstract

:
The agricultural sector’s progress toward climate neutrality is of great importance not only in the climate, but also in economic and social contexts. Climate-neutral agriculture is highly dependent on innovations that ensure maximum efficient farming, which not only reduces emissions but also ensures competitiveness in the market; all of this is fundamentally influenced by well-considered policies. Due to the complicated structure of the sector, it tends to be very difficult or even impossible to determine the real obstacles that delay the progress of sustainable farming. Therefore, this research aims to create a system dynamics model using Latvia as a case study, which would not only provide an insight into the system’s structure, but also identify the system’s weak links and allow for the development of recommendations. The model can calculate not only the generated emissions per unit of production, but also the investments required to reduce 1 kt of CO2eq generated, and results could help policymakers in any country to make rational, non-controversial decisions simultaneously in the context of economic and Green Deal objectives. The results of the study demonstrate that to increase economic competitiveness and reduce emissions in agriculture, the most important aspect is the ability to invest in innovations and new technologies that would achieve not only the lowest emissions, but also high productivity and competitiveness in the market. The research shows that the strategic documents emphasize manure management and improvement of feed quality, but there is an important element missing—an emphasis on thermoregulation improvements for animals. By improving feed quality, manure management, and thermoregulation all together, there was a 60% GHG emission reduction without reducing—and even significantly increasing—milk yield. In addition, in a comprehensive improvement of the new innovations, the case study company managed to increase milk yield by 69%.

1. Introduction

The agriculture sector keeps an essential role both globally and in Latvia’s economy, and is crucial to economic growth. However, rural areas often have enormous, but rarely fully realized economic potential. Energy efficiency trends in the agricultural sector also point to necessary improvements in the whole EU [1]. To increase energy efficiency, it is necessary to introduce energy management, which is a reasonable and efficient use of energy to maximize profits by reducing costs. In addition, energy management is related not only to the economic aspects, but also the environmental aspects, in order to eliminate inefficient use of resources, which in turn causes global warming [2]. However, the main problem is the large proportion of hard-to-reduce greenhouse gas (GHG) emission sources, which is the main characteristic of this sector [3]. Both in Europe and Latvia, the agricultural sector is one of the largest sectors producing GHG emissions (382.45 and 0.1 million tons of CO2eq), with high potential for productivity and efficiency improvements [4,5]. Although agriculture captures carbon dioxide in the process of plant growth, emissions are also generated in many processes; for instance, intestinal fermentation processes of farm animals, manure management, agricultural soil treatment, liming and urea use, fuel use for field cultivation, energy use in various processes, etc. [6].
Agriculture is in the most direct contact with natural resources—water, land, plants, animals, natural minerals, energy—and is directly and indirectly linked to all other sectors [7]. Not only does it connect with other sectors and all kinds of resources, but the diversity of its activity also makes it a very complex, difficult sector to organize. Nevertheless, it is a very important investment both in terms of environmental and also in economic development [8,9]. Inclusive, sustainable, growth-promoting, and equitable development of all sub-sectors of agriculture could have a large impact not only on the agricultural sector itself, but also other sectors, in which it is necessary to reduce GHG emissions [10,11]. As many of the resources used in agriculture are depletable, it is crucial to find methods to ensure their efficient management, sustainability, and availability in the future [12]. It is crucial to implement energy efficiency and resource efficiency measures without simultaneously reducing productivity [13]. However, these energy efficiency measures in the agricultural sector often require large investments in new technologies, and saving on factors such as lighting intensity, heat energy consumption, and the economy of various resources is not possible, as it could potentially threaten the existence of companies due to reduced or possibly even non-existent harvests. Agriculture is a sector subject to technological processes whose application has a direct impact on the production of competitive products with higher added value [14].
Undeniably, the adopted policy has a great influence on the direction of agriculture. Although the goal and meaning of the green course are unified [15], common agricultural policy is developed individually by the member states [16]. The new common agricultural policy envisages making EU agriculture fairer, greener, more results-oriented, as well as guaranteeing stable incomes for farmers and protection against bad harvest years and market price fluctuations [17]. The direction of the transformation is influenced by different strategies.
Climate Neutrality Strategy 2050 aims to achieve climate neutrality by 2050 through improvements in key GHG-emitting sectors [18]. The action measures to achieve the goal planned in the strategy are to achieve resource-efficient agriculture that produces products with high added value and high productivity, and to increase agricultural investment in bioenergy. The “Farm to Fork” strategy aims to make food systems environmentally friendly (neutral or even positive impact); not only help to mitigate climate change, but also adapt to it; reverse the loss of biodiversity; ensure food security and equity; foster competitiveness; and promote a fair trade [19]. It sets specific targets, such as halving the use of pesticides, reducing fertilizers by at least 20%, increasing the area of organic farming by 25%, and reducing antimicrobials used on farm animals by 50%. Another one is the new Biodiversity Strategy for 2030, which is a comprehensive, systemic, and ambitious long-term plan to protect nature, stop ecosystem degradation, and restore degraded ecosystems [20]. In the light of the Green Deal and its ‘Farm to Fork’ and ‘Biodiversity’ strategies, the EU aims to find new ways to decrease GHG emissions through a new approach for Europe—the EU Carbon Farming initiative—stating that farming practices that remove CO2 from the atmosphere should be rewarded in line with the development of new EU business models [21]. Furthermore, within the framework of the National Energy and Climate Plan (NECP) for 2030, there is a desire to achieve sustainable land management, sustainable farming of agricultural crops and farm animals, respect for the climate, nature protection, improved economic and social aspects, and to make a significant contribution to bioenergy in the field, all without endangering food security and CO2 sequestration, as well as following the cascade principle; in order to achieve high productivity through the efficient use of bio-resources (including land resources) [22]. NECP’s planned measures related to animal husbandry are to improve the manure management system for more efficient use of fertilizers, which is essential regarding both the plant yield and the environmental aspect; to implement manure fermentation biogas reactors, which have the potential to reduce GHG emissions to a minimum in large farms, ensuring efficient manure management and production of renewable energy and valuable fertilizer for crops; to improve animal feeding—various methods are known and used around the world for determining the digestibility of fodder, as well as for determining and analyzing the amount of gases released by animals. Balanced and appropriate feed affects the rate of N release from manure, which has a positive effect on the reduction of N2O emissions. Meanwhile, improving feed quality increases feed digestibility and reduces CH4 emissions. Thoughtful, sustainable management would improve the rural population and the well-being of the inhabitants; in addition, the fertility of the land would not be reduced, the yield of crops would be increased, and the demand for energy from external resources would be reduced. It would not only reduce the impact on the environment, but also promote the competitiveness of local companies in the market by reducing expenses. This produces products with higher added value, making full use of all available resources. However, unprofessionally adopted policies that focus only on specific agricultural sub-sectors or groups of companies may not only prevent these goals, but also even delay them. It should be taken into account that agriculture is a very complex system in which simple saving measures and knowledge are not enough, because various innovations and technologies are needed in order to achieve these savings and productivity [23].
Although the planned measures are theoretically very promising, there is a huge resistance among farmers, where the prevailing concern is about the inequality and destruction of business in the agricultural sector, and the inability to compete. Due to the complicated structure of the sector, it tends to be very difficult or even impossible to determine the real obstacles and mistakes that delay the progress of sustainable farming. Therefore, this research aims to create a system dynamics model using Latvian dairy farming as a case study, which was chosen due to the existing dairy crisis in Latvia, evident by the low profitability indicators of animal husbandry [1]. It would not only provide an insight into the system’s structure but also identify the system’s weak links and allow for the development of recommendations.

1.1. Specifics of Dairy Farming

In animal husbandry, thermoregulation—heating, conditioning, lighting, and ventilation—is particularly important for animals kept indoors [24]. The quality of air, food, and water has the greatest impact directly on the health of animals, and therefore also on productivity, which is the most important indicator in animal husbandry [25].
Today, ranchers are increasingly using robots and algorithms in production to optimize their farm management decisions [26]. The development of technology creates a new automation system that provides smarter and more flexible work opportunities in animal husbandry [27]. These technologies provide livestock farmers with data-based insight into economic activity, which allows them to provide the necessary animal care and increase productivity, and provides them an opportunity to manage the farm more easily.
One of the biggest consumers of electricity, next to lighting, is ventilation, which often accounts for at least a fifth of the barn’s maintenance costs [28], so that harmful gases such as ammonia and carbon dioxide do not exceed their critical permissible concentrations [29]. Some solutions to increase efficiency is modern building construction or innovations such as green roofs and walls to reduce indoor temperatures [27,30]. The main goal is to successfully combine mechanical ventilation and thermal insulation with natural alternatives, and such engineering solutions help to reduce energy by up to 50% [28], increasing milk productivity by at least 10–15% [31]. The most important aspect is to pay attention to thermoregulation because it will result in higher animal productivity; if dairy cows suffer from overheating during summer for about 6–15 h a day, it can result in a loss of 3.5 L of milk per day due to heat stress. Often, if all resource saving and energy efficiency measures have been taken, it is important to start thinking directly about the possibilities of installing renewable energy sources on the farm.
Development has also taken place in feeding animals. Computer programs have been developed that cover each stage of feeding: feed preparation, mixing and dosing, and feed distribution. They make it easier to plan the rations needed by the animal and give the ability to supplement the feed with fatty substances. Efficient use of feed can reduce methane gas emissions as well as give the ability to obtain the biggest yield. Furthermore, a sensor has been created that reads the movement of the animal’s jaw to determine whether it digests the food completely.
One of the biggest threats in animal farming is disease, as it can spread very quickly between animals. Sickness of an animal has an economic impact on the farm, so it is important to detect the disease in its first days. Doing so reduces the cost of treatment, reduces the mortality rate, and improves production efficiency. It is possible to determine the state of health of animals by their behavior, body condition, and food intake, so companies have created programs based on the acquisition and analysis of data parameters. To obtain data from the animal, sensors are installed on it—the task of which is to collect data about the animal’s condition and pass it on to analysis points [32].

1.2. Case Study of a Dairy Farm in Latvia

In Latvia, a significant part of the population lives in rural areas, which account for approximately 84% of the total area of Latvia [33]. Although field crops are responsible for more than half of agricultural emissions in Latvia, other agricultural sectors such as vegetable growing and animal husbandry—which have the lowest profitability—should not be forgotten, especially because animal husbandry is responsible for the remaining agricultural emissions, which amount to about 45% [1].
Although the farming practices of Latvian farmers can be assessed as positive not only because of the high quality products, but also because of productivity, the energy efficiency trends of the agricultural sector point to necessary improvements [34]. This is because energy efficiency has not reached the EU average over the last 8 years [32]. Furthermore, Latvia’s indicators show much larger fluctuation both in the turnover of the produced products and in the energy efficiency of the agricultural sector [32].
Sub-sectors such as cereal and berry farming has been expanding in Latvia, while other sub-sectors are experiencing rather slow development or stagnating [35]. The total number of dairy farms in 2021 has decreased by 10% compared to 2020, and the total number of dairy cows has decreased by 3%, bringing the number of registered dairy cows to 131,207 [35,36]; the density of farm animals in Latvia is one of the lowest in Europe [37]. The production of milk has almost reached the EU’s average milk yield, which is an important indicator of livestock welfare [38]. Additionally, the value of primary production per hectare of agricultural land in Latvia is one of the lowest in the EU, despite good climatic conditions and available water resources [39].
The system dynamics model was created based on the operating principles and data of one of the largest and most modern agricultural enterprises. Its main product is milk. There are about 470 dairy cows, and the average milk yield is 10,184 kg per cow per year, while the total milk production is 4736 tons per year. In total, there are three barns in the dairy complex where all the necessary animal welfare regulations and environmental requirements are observed. To execute the construction of cowsheds, the owner has implemented several projects of the European Agricultural Fund for Rural Development, which has enabled the introduction of innovations in the farm. This therefore increases the efficiency of farming, as well as provides the most suitable conditions for all ages of the livestock. Several projects were implemented, but the most important of them were:
  • Construction of the new barn, in 2012, which cost EUR 2,641,915 with a payback time of 10 years,
  • Construction of liquid manure storage in 2015, which cost 135,435 EUR with a payback time of 8 years,
  • Construction of a new livestock shed in 2020, which cost EUR 1,864,564 with a payback time of 9 years,
  • Purchase of a Siloking feed mixer/distributor in 2020, which cost 190,000 EUR with a payback time of 5 years.
Based on the operating principles of the farm, it can be safely stated that this company can serve as a positive benchmark for the Green Deal goals of the future.

2. Methodology

To obtain all the necessary information, a literature analysis was carried out, in which scientific articles mainly from SCOPUS, ScienceDirect databases, Google, Google Scholar, and statistics and policy documents like European Commission reports and Latvia’s national plans, reports and strategies were analyzed. A combination of the following search requirements were used in the process of finding relevant information and articles: “Agriculture”, “Latvia”, “Europe”, “Climate neutral”, “Sustainable”, “Carbon farming”, “Green Deal”, “Greenhouse gas”, “Renewable”, “Strategy”, “Energy”, “Production”, “Efficiency”, “National Energy and Climate plan”, “Guidelines”, “Economic”, “Technical”, “Technology”, “Livestock”, “Dairy farming”, “Manure”, “Production”, “Policy”, “Innovation”, “Feed”, “Quality”, “Investment”, “Thermoregulation”, “Feed”, “Yield”, “Improvement”, “Management”, etc. Priority was given to the most recent articles and papers of relevance, scientific articles published in peer-reviewed journals in English. Then, one of the biggest and most modern dairy farms in Latvia was surveyed, which has already implemented several innovations for precise management, livestock welfare, modern technologies, and energy efficiency measures, while achieving a yield that significantly exceeds the average annual milking yield of a cow in Latvia and Europe. The farm owner was asked questions such as: Opinion on the Common Agricultural Policy, Carbon Farming and Support Mechanisms; Information about the company’s specifics, boundaries, affiliated companies, their cooperation, the importance of cooperatives, the impact of innovations on the company’s energy consumption, and the effectiveness of welfare implementation in relation to milking yield; the point of view of industry professionals on the biggest obstacles, as well as the experience of overcoming them; History of the company, its development, etc. These questions were mainly used to expand the research not only with the theoretical knowledge, but also with field professional knowledge who practically work in this field daily, while later connecting practical and theoretical knowledge by making calculations with data obtained from a real company to be able to draw the most objective conclusions and avoid any blind spots. Data were obtained from this farm and processed, such as data on energy consumption and milk yields by years, the introduced innovations and their specifics, the amount of manure produced and its processing, the amount of feed consumed, changes in number of cows and other related data; then, calculations were made. Subsequently, a system dynamics model using Latvia as a case study was made, which would not only provide an insight into the system’s structure, but also identify the system’s weak links and allow for the development of recommendations. The flow chart of the research development is shown in Figure 1.
The Stella Architect modeling tool was used to create a simulation model to present in a simplified mathematical way an agricultural sub sector—dairy farming. It was chosen because it not only shows the structure visually, but also includes numbers, equations, and mutual interactions of various influences. It includes economic, environmental, and technological aspects. To create a transparent insight into the structure of the dairy farm linked to the research objectives and focus, a simplified scheme was created (Figure 2).
The main schemes were shown in a simplified way and included both thermoregulation and the impact of feed quality not only on yield, but also on animal health, which in turn affects mortality, expenses, product price, and thus competitiveness. The impact of support mechanisms and the amount of sold volume were also considered, which affects savings, and in turn later allows or prevents investments in new, modern technologies that would reduce expenses and increase energy efficiency, yield, and total income. Manure processing is also included as an integral part of animal husbandry. The impact of these processes on the generated emissions is also indicated, and the investments required to reduce them are included.
Model data input comes from two sources—literature analysis and data obtained from the specific company’s survey. Data such as the number of cows, electricity and heat consumption, investments in various technologies and modernization, and milk yield were used for the case study.
The purpose of the model is to create the operation model of the dairy farm, which reflects the importance of investment implementation both in an economic and environmental context, where it is possible to observe the amount of emission reduction. It is possible to predict the importance of the implementation of investments and changes in emissions considering several interrelated influencing factors in the dairy farm model.

3. Results and Discussion

To identify the main drivers and weak links, it was necessary to model the importance of investment implementation and the change in emissions. In general, the model was divided into four sectors:
-
Dairy cows;
-
Investment in dairy farming;
-
Economic factors;
-
Emissions.
For the construction of the base model to be as close as possible to the real-life situation, it is necessary to look at several sectors in more detail so that the model is not based on assumptions, but on real data. One of the sectors that needs to be further divided into sub-sectors is investments in the improvements of dairy farming, where it is also necessary to consider separately the investments in the improvements of feed quality, thermoregulation, and manure management. Another sector is the economic factors, where it is necessary to study in more detail both how the savings are generated, which is a key factor needed to make the investment, and the cost of capital, which determines the total one-time costs needed to cover, for example, the construction of a new barn.
Each sector was modelled so it could be used for each emission scenario. Once the boundaries of the model study were defined, it was determined that the emissions generated would be viewed in two ways:
-
Generated emissions, which will be measured in kt CO2eq. year,
-
Generated emissions per product, which will be measured in kt CO2eq. to the annual production volume.
It was further determined that the change in emissions in the model would be determined for three scenarios:
  • The dairy farmer does not invest in any of the dairy farm performance improvement measures.
  • The dairy farmer invests only in improving manure management.
  • The dairy farmer invests in all farm improvement measures.
The scenarios were created since dairy farmers have more pressure from the state to invest in manure management than in feed quality and thermoregulation. From the first two scenarios, changes in emissions were observed, while in the third one, changes in emissions to produced production will be observed. It should be mentioned that although the model structure is created for the third scenario, it has the possibility to disable some parameter behaviour, thus creating some other scenario.
So that the data obtained by the model could be compared with the real-life situation and conclusions could be drawn, it was chosen to simulate the model in the period from 2012 to 2022. All data used in the model are obtained from dairy data, adopted considering the opinion of sector experts and literature analysis.

3.1. Dairy Cows

Dairy cows are the most important element in a dairy farm, as the obtained raw milk is the main product that brings profit to the company. Dairy cows are mostly at least two years old and have reached their first lactation. The cow sector in the model consists of two main stocks: dairy cows and sick cows (Figure 3).
Dairy cow stock has both outgoing and incoming flow. To increase the number of cows, the owner buys new dairy cows or grows heifers. If a cow’s milk production drops, it is sold. Sick cows are treated, but when the treatment is unsuccessful and requires a lot of resources that would affect not only the costs, but also the yield, they are usually sent to the slaughterhouse or die naturally. Livestock health is particularly affected by the availability of high-quality feed, living conditions, and thermoregulation.
The incoming flow of the stock of dairy cows was determined considering the maximum number of beds for cows in the barn. But the outflow of the stock “sales” is determined by multiplying the sales ratio by the number of milking cows.
A similar principle applies to the cure and mortality flows of the sick cow stock, but the inflow of sick cows is affected by the level of feed quality. The effect of feed quality on morbidity is derived from a non-linear relationship in which the feed quality rating is used as an argument. The effect on morbidity ranges from 0 to 1.
Cows also produce manure from their digestive system. Manure can be divided into liquid and litter (solid). Litter manure is cow excrement with/without litter and fodder remains, and liquid manure—with urine and/or water admixture. The total amount of manure produced was calculated as tons/year.
The quantity of milk produced and sold [ton] depends on the number of cows and the average yield of one cow.
In general, milk yield per cow is influenced by several parameters, including the effect of thermoregulation level and feed quality on milk yield. Both the effect of feed quality and the effect of thermoregulation on hunger are characterized by a non-linear relationship that varies in the range from approximately 0 to 1, in which the rating of feed quality or thermoregulation level is used as an argument. In the model, the average milk yield at the beginning of 2012 is taken from the data of the reviewed dairy farm, to then be able to compare how investing in thermoregulation and feed quality improvement technologies increases milk yield.
The necessary data were obtained from the dairy farm, available statistical data, and scientific literature analysis. System dynamics model parameters for the cow sector can be seen in Table 1.

3.2. Emissions

The emission sector in the model represents emissions from the company, as well as emissions per unit of production. It is necessary to calculate the emissions to be able to evaluate the progress towards climate neutrality. In dairy farming, the main GHG emissions come from intestinal fermentation and manure management. Although in the documentation, the calculation of emissions from fuel consumption, electricity, and heat production is below the energy and transport sector, it is important to include it. In the model, the emission sector has two main stocks and two main flows (Figure 4).
Methane emissions from intestinal fermentation processes, GHG emissions generated to produce the consumed electricity and heat energy, as well as GHG emissions generated due to fuel consumption were calculated. Manure emissions were also calculated; however, several parameters must be considered when calculating manure. Organic matter and water make up most of the composition of manure. Manure emits both methane and nitrogen oxide emissions. How much methane is released from manure depends on its oxygenation, water content, pH level, and feed digestibility [40]. How much nitrous oxide is produced depends on climate, pH, and manure management. To be able to perform a unified accounting of emissions, it is necessary to switch to CO2eq. In general, both dairy farm data and predetermined constants were taken for the calculation (Table 2).
Electricity and heat consumption are currently represented as constant values in the model. It is also necessary to calculate the emitted emissions per production quantity, which can be calculated by dividing the generated emissions by the produced production quantity.

3.3. Economic Factors

It is important to look into the economic sector as it is one of the determinants of investment and savings, providing a safety net and a sense of security for a farmer that the company will have a better chance of getting out of financial difficulties after taking risks on new investments [41]. In dairy farming, the biggest expenses come from electricity consumption charges, dairy cow treatment costs, and capital costs, while income comes from milk production and sales, where they are affected by the amount of milk sold, which depends on the yield obtained from the cow. Cow and milk prices determined by the cooperative, additional income also comes from the sale of culled cows, where the price per cow depends on the market. Income is exactly the factor that contributes to the accumulation of profit, because even if the expenses are very high, if there is a large income, the accumulated profit will also be within the norm. A feedback loop is also created from the amount of accumulated profit because investment decisions are made from the amount of accumulated profit and own available financing. If a decision is made to make investments, then the reduction in retained earnings is determined by the channeling of funding to investments and the self-financed part (Figure 5).
The capital cost sector consists of one main stock—capital cost, the increase of which is determined by making capital investments, which is affected by the discount rate, bank loan, and the loan repayment period, while the reduction of the stock is affected by the repayment period, the capital investor, and the capital costs themselves. A dairy company needs to take a loan from a bank to cover the costs needed to make improvements to the farm which are not compensated for by the support offered by the state.
For the sector to work in the model, it is necessary to enter data; therefore, the input data used in the savings and capital expenditure sector are summarized in Table 3.

3.4. Investment in Dairy Farming

To manage dairy cow manure, it is possible to use different management methods. Each type of manure management in the model is evaluated in points, where they determine the level of management on the farm. Each type of management has its own determined emission factor (Table 4).
The model considers the time required to implement improvements at the management level (Figure 6). The improvement of the level is also influenced by the ratio between the funding diverted for improvement and the investment required to improve manure management by one point. The necessary investment for improvement per cow is determined by the necessary investment for raising the quality indicator by one point, the difference between the maximum and management level in the farm, as well as the available support measures. To determine whether it is worth investing in the improvement of manure management, the time implementation of improvement measures is determined by whether the improvement of manure management contributes to an increase in income. If the manure is used to produce biogas, it is possible for the dairy farmer to receive payment for the manure sold to the biogas plant, unless the farmer himself has invested in the biogas plant.
Feed quality is included because it affects milk yield, the health of cows, generated emissions, and the farm’s profit (Figure 7). The most important indicator by which feed quality is determined is feed digestibility (%). In the model, feed quality is measured on a scale of 1 to 10, where 1 is the worst feed quality indicator and 10 is the best. However, to achieve high feed quality, it is necessary to invest in technologies to achieve the set goal. The effect of feed quality on milk yield varies between approximately 0.1 and 1 and is derived from a non-linear relationship using the feed quality score as the argument. The model also examines how income could increase as feed quality increases to determine the payback period. The increase in feed quality is affected by the time it takes to introduce a new technology, as well as the ratio between the funding diverted to improve quality and the investment needed to improve quality by one point. The necessary investment for improvement per cow is determined by the necessary investment for raising the quality indicator by one point, the difference between the maximum and the existing level of feed quality on the farm, as well as the available support measures.
It is crucial to make improvements in thermoregulation to improve the well-being of livestock, which would also affect the milk yield significantly and reduce diseases. In the model, the level of thermoregulation is evaluated on a scale from 1 to 10, where 1 is the worst thermoregulation, and 10 is the best. The effect of thermoregulatory level on yield varies between 0.1 and 1, and is derived from a non-linear relationship using the thermoregulatory level score as an argument. The model also explores how earnings could increase if the level of thermoregulation is increased to determine the payback period (Figure 8).
The increase in the quality of thermoregulation is also affected by the time it takes to implement a new technology, as well as the ratio between the funding diverted to improve thermoregulation and the investment to improve by one point. The necessary investment for improvement per cow is determined by the necessary investment for improving thermoregulation by one point, the difference between the maximum and existing levels in the farm, as well as the available support measures. For the model to function, the data reflected in Table 5 were entered.

3.5. Results from the Case Study and the System Dynamics Model

By the calculations based on the data of the dairy company, it was found that it is possible to achieve several improvements by investing:
By building a new barn, the company:
-
reduced electricity consumption by 7000 kWh/year, which is a 46% reduction,
-
increased milk yield from one cow by 2129 kg/cow/year, which is a 25% improvement compared to the year of making the investment,
-
increased milk yield from one cow by 3987 kg/cow/year, which is a 42% improvement, compared to the 10-year average milk yield before the investments.
By investing in feed feeding technologies, the company increased milk yield by 174 kg/cow/year, which is a 2% improvement compared to the year of making the investment.
From the system dynamics model, it was determined that the generation of emissions in both the first and second scenario is characterized by a linear curve (Figure 9a). The number of generated emissions increases every year as the number of cows increases, which thus increases the number of emissions generated from intestinal fermentation processes. However, because of the introduction of innovations, it is possible to observe a reduction in emissions, as a higher level of manure management reduces emissions from manure.
When comparing the emissions created in these scenarios, 2017 and 2022 were taken as reference points, and it was determined that with the help of the 2nd scenario, compared to the first scenario, emissions are reduced by 0.1% in 2017 and by 10% in 2022.
Then, the generated emissions per produced quantity, which is the most essential and objective indicator in agriculture, was examined. Figure 9b shows the emissions per produced amount of production, which is measured in kt CO2eq/kt of milk produced. In general, it can be observed that the 1st scenario also produces the highest emissions for the production, while the 2nd scenario produces less emissions than the 1st scenario only from 2015, but in the 3rd scenario, significant changes can be observed compared to the other two scenarios.
When comparing the generated emissions between the scenarios, 2022 was taken as a reference point. It was found that by implementing the second scenario (when investments only in manure management technology development are made), compared to the first scenario (when no improvements are made), it is possible to achieve a reduction in emissions by 8% (2.32 ktCO2eq/kt of milk) in 2022.
When comparing the generated emissions between the second scenario (where improvements only in manure management are made) and third scenario (where improvements in manure management, thermoregulation and feed improvement are made), it was found that by implementing the third scenario, it is possible to achieve a reduction in emissions by 57% (15.28 CO2eq/kt of milk) in 2022.
When comparing the generated emissions between the first scenario (where no improvements are made) and third scenario (where improvements in manure management, thermoregulation and feed improvement are made), it was found that by implementing the third scenario, it is possible to achieve a reduction in emissions by 60% (17.59 CO2eq/kt of milk) in 2022.
The increase in the number of cows occurs up to and including 2016, but remains constant thereafter. Comparing the year 2013 with the year 2022, it can be determined that the number of cows has increased by 23%.
The initial milk yield per cow was 6.377 tons/cow, which remains unchanged in the first and second scenario, but in the third scenario, it is possible to observe an increase in milk yield in the maximum average milk yield per cow, which is 15.870 t/cow per year. Comparing the first year of the third scenario with the last one, it is possible to observe an increase of 69% (5261.45 t more), but comparing the third and first scenarios of 2022, it can be concluded that by investing in the improvement of the farm, it is possible to achieve a 60% higher amount of production, which is 4550.99 t more (Figure 10).

4. Conclusions

The strategic documents emphasize manure management and improvement of feed quality, but an important missing element is visible—a section on improving the thermoregulation of animals. All these elements (manure management, feed quality, and thermoregulation) are an integral part that must work in one system, because their improvement significantly improves productivity, reduces energy consumption, improves resource efficiency, and reduces direct and indirect emissions not only in agriculture, but also in the energy and transport sectors.
It should be noted that the larger the volume of production, the lower the number of emissions produced per unit of production. However, in agriculture, it is possible to achieve it mainly through investments in new, modern technologies, because an ill-considered economy of energy or resources can result in yield losses, which would not be a sustainable solution at the company or at the state level. Agriculture cannot focus only on energy efficiency and greenhouse gas emission reduction without consideration of aspects such as the impact of the activities on yield, technology, free available funds, market stability, state support, and others. It is important to look at ways to increase productivity while introducing energy-efficient and resource-efficient methods—a thoughtful management model. Only that way would it be possible to achieve sustainability from both an environmental point, and also from an economic point.
However, such technologies require investments, which are directly affected by the company’s income and savings, and in turn are affected by the volume sold and the price of the product in the market, support mechanisms, existing technological level, and efficiency. To ensure the sale of the product on the market at a sufficiently high price for the company to develop innovation, it is important to develop a national policy that guarantees sales of the local producer’s products. This is very important, because if there is more support and protection for agricultural enterprises in competing countries, not only will the price be competitive, but the safety of selling the products on the market will also fall. Ill-considered local policy fail to promote opportunities for local producers’ innovation development comparing to competing countries’ companies. This is especially critical now, when adapting to climate change and trying to fulfill the Green Deal goals; failing to develop sustainable policies risks destroying the local market’s ability to compete and exist.
The created system dynamics model allows us both to understand and to model possible scenarios; to calculate not only the impact of a given company or sector on the environment by calculating the generated emissions per unit of production, but also to calculate the investments required to reduce 1 kt of CO2eq generated in the company. Such a model makes it possible to make sustainable decisions not only at the level of the company, but also at the level of state policy, to simultaneously promote environmental goals, economic growth, and the development of the national economy.

Author Contributions

Methodology, E.M. and A.G.; Investigation, K.B.; Writing—original draft, K.B. and E.M.; Writing—review and editing, K.B.; Visualization, E.M.; Supervision, K.B., J.P. and D.B. All authors have read and agreed to the published version of the manuscript.

Funding

This research is funded by the European Social Fund within Project No 8.2.2.0/20/I/008 “Strengthening of PhD students and academic personnel of Riga Technical University and BA School of Business and Finance in the strategic fields of specialization” of Specific Objective 8.2.2 “To Strengthen Academic Staff of Higher Education Institutions in Strategic Specialization Areas” of the Operational Programme “Growth and Employment”.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data from publicly available databases and scientific publications, as well as the company, which was used as a case study. The sources of all data used are referenced I the text.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Rutkovska, A. Agriculture Is a Complex Industry with a Big ‘BUT’|Macroeconomics. 2022. Available online: https://www.makroekonomika.lv/lauksaimnieciba-ir-sarezgita-nozare-ar-lielo-bet#1-lauk (accessed on 16 March 2023).
  2. Rodríguez, C.M.; Rodas, C.F.R.; Muñoz, J.C.C.; Casas, A.F. A multi-criteria approach for comparison of environmental assessment methods in the analysis of the energy efficiency in agricultural production systems. J. Clean. Prod. 2019, 228, 1464–1471. [Google Scholar] [CrossRef]
  3. Ministry of Economics of the Republic of Latvia. Latvia’s National Energy and Climate Plan for 2021–2030; Ministry of Economics of the Republic of Latvia: Riga, Latvia, 2021.
  4. EU Economy Emissions in 2021: −22% Since 2008—Products Eurostat News—Eurostat. Available online: https://ec.europa.eu/eurostat/web/products-eurostat-news/w/ddn-20221221-1 (accessed on 20 March 2023).
  5. Latvian Ministry of Agriculture. Latvian Agriculture 2020; Ministry of Economics of the Republic of Latvia: Riga, Latvia, 2021; pp. 1–207.
  6. 2022 Greenhouse Gas Inventory Summary. 2022. Available online: https://am.lrv.lt/uploads/am/documents/files/Klimato_kaita/NIR_2022%2003%2015%20FINAL.pdf (accessed on 15 June 2023).
  7. EEA. National Climate Policy Program Project ‘Environment and Agriculture’. Available online: https://ips-dc.org/climate-policy-program/ (accessed on 15 June 2023).
  8. Ma, L.; Long, H.; Tang, L.; Tu, S.; Zhang, Y.; Qu, Y. Analysis of the spatial variations of determinants of agricultural production efficiency in China. Comput. Electron. Agric. 2021, 180, 105890. [Google Scholar] [CrossRef]
  9. Maraseni, T.; An-Vo, D.-A.; Mushtaq, S.; Reardon-Smith, K. Carbon smart agriculture: An integrated regional approach offers significant potential to increase profit and resource use efficiency, and reduce emissions. J. Clean. Prod. 2020, 282, 124555. [Google Scholar] [CrossRef]
  10. Welfle, A.; Chingaira, S.; Kassenov, A. Decarbonising Kenya’s domestic & industry Sectors through bioenergy: An assessment of biomass resource potential & GHG performances. Biomass Bioenergy 2020, 142, 105757. [Google Scholar]
  11. Ersoy, E.; Ugurlu, A. The potential of Turkey’s province-based livestock sector to mitigate GHG emissions through biogas production. J. Environ. Manag. 2020, 255, 109858. [Google Scholar] [CrossRef] [PubMed]
  12. Kour, D.; Rana, K.L.; Yadav, A.N.; Yadav, N.; Kumar, M.; Kumar, V.; Vyas, P.; Dhaliwal, H.S.; Saxena, A.K. Microbial biofertilizers: Bioresources and eco-friendly technologies for agricultural and environmental sustainability. Biocatal. Agric. Biotechnol. 2020, 23, 101487. [Google Scholar] [CrossRef]
  13. Yu, L.; Qin, H.; Xiang, P.-A. Incentive mechanism of different agricultural models to agricultural technology information management system. Sustain. Comput. Inform. Syst. 2020, 28, 100423. [Google Scholar]
  14. Van Bueren, E.L.; Verhoog, H.; Tiemens-Hulscher, M.; Struik, P.; Haring, M. Organic agriculture requires process rather than product evaluation of novel breeding techniques. NJAS—Wagening. J. Life Sci. 2007, 54, 401–412. [Google Scholar] [CrossRef] [Green Version]
  15. European Commission. Agriculture and the Green Deal. Available online: https://commission.europa.eu/strategy-and-policy/priorities-2019–2024/european-green-deal/agriculture-and-green-deal_lv (accessed on 20 February 2023).
  16. Council of the European Union. Common Agricultural Policy. Available online: https://www.consilium.europa.eu/lv/policies/cap-introduction/ (accessed on 20 February 2023).
  17. Council of the European Union. Common Agricultural Policy 2023–2027 for the Year—Consilium. Available online: https://www.consilium.europa.eu/lv/policies/cap-introduction/cap-future-2020-common-agricultural-policy-2023-2027/ (accessed on 20 February 2023).
  18. Development The Ministry of Environmental Protection and Regional. Latvia’s Strategy for Achieving Climate Neutrality by 2050; Development The Ministry of Environmental Protection and Regional: Riga, Latvia, 2019.
  19. European Comission. Farm to Fork Strategy. Available online: https://food.ec.europa.eu/horizontal-topics/farm-fork-strategy_lv (accessed on 20 February 2023).
  20. European Commission. Biodiversity Strategy for 2030. Available online: https://environment.ec.europa.eu/strategy/biodiversity-strategy-2030_en (accessed on 20 February 2023).
  21. Bumbiere, K.; Sanchez, F.A.D.; Pubule, J.; Blumberga, D. Development and Assessment of Carbon Farming Solutions. Environ. Clim. Technol. 2022, 26, 898–916. [Google Scholar] [CrossRef]
  22. Order of the Cabinet of Ministers, No. 46. About Latvia’s National Energy and Climate Plan 2021–2030. 2020. Available online: https://likumi.lv/ta/id/312423-par-latvijas-nacionalo-energetikas-un-klimata-planu-20212030-gadam (accessed on 20 February 2023).
  23. Dhamodharan, K.; Konduru, T.; Kannan, M.; Malyan, S.K. Techno-economic feasibility and hurdles on agricultural waste management. In Emerging Trends to Approaching Zero Waste; Elsevier: Amsterdam, The Netherlands, 2022; pp. 243–264. [Google Scholar]
  24. Costantino, A.; Fabrizio, E.; Ghiggini, A.; Bariani, M. Climate control in broiler houses: A thermal model for the calculation of the energy use and indoor environmental conditions. Energy Build. 2018, 169, 110–126. [Google Scholar] [CrossRef]
  25. Yeo, U.-H.; Lee, I.-B.; Kim, R.-W.; Lee, S.-Y.; Kim, J.-G. Computational fluid dynamics evaluation of pig house ventilation systems for improving the internal rearing environment. Biosyst. Eng. 2019, 186, 259–278. [Google Scholar] [CrossRef]
  26. Neethirajan, S. The role of sensors, big data and machine learning in modern animal farming. Sens. Bio-Sens. Res. 2020, 29, 100367. [Google Scholar] [CrossRef]
  27. Firfiris, V.; Martzopoulou, A.; Kotsopoulos, T. Passive cooling systems in livestock buildings towards energy saving: A critical review. Energy Build. 2019, 202, 109368. [Google Scholar] [CrossRef]
  28. Mondaca, M.R.; Cook, N.B. Modeled Construction and Operating Costs of Different Ventilation Systems for Lactating Dairy Cows—ScienceDirect. Available online: https://www-sciencedirect-com.resursi.rtu.lv/science/article/pii/S002203021830972X#bib17 (accessed on 2 February 2021).
  29. Zhao, Y.; Shepherd, T.A.; Li, H.; Xin, H. Environmental assessment of three egg production systems–Part I: Monitoring system and indoor air quality. Poult. Sci. 2015, 94, 518–533. [Google Scholar] [CrossRef] [PubMed]
  30. Galama, P.; Ouweltjes, W.; Endres, M.; Sprecher, J.; Leso, L.; Kuipers, A.; Klopčič, M. Symposium review: Future of housing for dairy cattle. J. Dairy Sci. 2020, 103, 5759–5772. [Google Scholar] [CrossRef] [PubMed]
  31. West, J.W. Effects of Heat-Stress on Production in Dairy Cattle. J. Dairy Sci. 2003, 86, 2131–2144. [Google Scholar] [CrossRef] [PubMed]
  32. Statistics|Eurostat. Available online: https://ec.europa.eu/eurostat/databrowser/view/sdg_07_30/default/table?lang=en (accessed on 20 February 2023).
  33. Gancone, A.; Bumbiere, K.; Pubule, J.; Blumberga, D. Sustainable biogas application in energy sector. In Proceedings of the 2020 IEEE 61th International Scientific Conference on Power and Electrical Engineering of Riga Technical University (RTUCON), Riga, Latvia, 5–7 November 2020. [Google Scholar]
  34. European Commission. The Environmental Implementation Review 2019; European Commission: Brussels, Belgium, 2019. [Google Scholar]
  35. The Ministry of Agriculture of Republic of Latvia. Agriculture in Latvia 2021; The Ministry of Agriculture of Republic of Latvia: Riga, Latvia, 2022.
  36. Leimane, I.O.I.; Krieviņa, A.; Ceriņa, S.; Auziņš, A.; Lakovskis, P.; Dreijere, S.; Gulbe, I. Developing a Strategy for a Sustainable and Multifunctional Dairy Sector in Latvia. 2021. Available online: https://www.llu.lv/lv/projekti/apstiprinatie-projekti/2021/strategijasizstrade-noturigas-un-multifunkcionalas-piena (accessed on 15 June 2023).
  37. FAOSTAT Database. Crops and Livestock Products. Available online: https://www.fao.org/faostat/en/#data/QCL (accessed on 3 April 2023).
  38. Average Milk Yield from One Cow, kg—Time Period. Available online: https://data.stat.gov.lv/pxweb/lv/OSP_PUB/START__NOZ__LA__LAL/LAL070/table/tableViewLayout1/ (accessed on 7 October 2022).
  39. Latvian Ministry of Agriculture. Latvian Bioeconomy Strategy 2030; Latvian Ministry of Agriculture: Riga, Latvia, 2018.
  40. Hassanat, F.; Benchaar, C. Methane emissions of manure from dairy cows fed red clover- or corn silage-based diets supplemented with linseed oil. J. Dairy Sci. 2019, 102, 11766–11776. [Google Scholar] [CrossRef] [PubMed]
  41. Maison, D.; Marchlewska, M.; Sekścińska, K.; Rudzinska-Wojciechowska, J.; Łozowski, F. You don’t have to be rich to save money: On the relationship between objective versus subjective financial situation and having savings. PLoS ONE 2019, 14, e0214396. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  42. The Intergovernmental Panel on Climate Change. Module 4. Agriculture. Revised 1996 IPCC Guidelines for National Greenhouse Gas Inventories: Workbook; The Intergovernmental Panel on Climate Change: Geneva, Switzerland, 1996. [Google Scholar]
Figure 1. Flow chart of the research development.
Figure 1. Flow chart of the research development.
Sustainability 15 11136 g001
Figure 2. Simplified operation scheme of the dairy farm.
Figure 2. Simplified operation scheme of the dairy farm.
Sustainability 15 11136 g002
Figure 3. Structure of the cow model.
Figure 3. Structure of the cow model.
Sustainability 15 11136 g003
Figure 4. Structure of the emission model.
Figure 4. Structure of the emission model.
Sustainability 15 11136 g004
Figure 5. Structure of the economic model.
Figure 5. Structure of the economic model.
Sustainability 15 11136 g005
Figure 6. Structure of the investment in manure management model.
Figure 6. Structure of the investment in manure management model.
Sustainability 15 11136 g006
Figure 7. Structure of the investment in feeding quality model.
Figure 7. Structure of the investment in feeding quality model.
Sustainability 15 11136 g007
Figure 8. Structure of the investment in the thermoregulation model.
Figure 8. Structure of the investment in the thermoregulation model.
Sustainability 15 11136 g008
Figure 9. (a) The total amount of emissions produced in several scenarios; (b) The total amount of emissions generated per the amount of output produced in several scenarios.
Figure 9. (a) The total amount of emissions produced in several scenarios; (b) The total amount of emissions generated per the amount of output produced in several scenarios.
Sustainability 15 11136 g009
Figure 10. Milk production in the first, second, and third scenarios.
Figure 10. Milk production in the first, second, and third scenarios.
Sustainability 15 11136 g010
Table 1. System dynamics model parameters for the cow sector.
Table 1. System dynamics model parameters for the cow sector.
ParameterUnit of Measure
Mortality rateDimensionless
Increase in the number of cows ratioDimensionless
Cow sales ratioDimensionless
Cow cure ratioDimensionless
The amount of liquid manure produced per cowtons/year
The amount of litter manure produced per cowtons/year
Number of milking cowsNumber of cows
Maximum number of cow places in the barnNumber of cows
Maximum milk yield per cowtons/cow/year
Table 2. Input data for the emission sector in the model.
Table 2. Input data for the emission sector in the model.
ParameterUnit of Measure
Heat energy consumptionMWh/year
Fuel consumptionlitre/year
Diesel fuel combustionMWh/ton
Electricity consumptionkWh/year
Global warming potential of CH4Dimensionless
Global warming potential of CO2Dimensionless
Table 3. The input data in the savings and capital expenditure sector.
Table 3. The input data in the savings and capital expenditure sector.
ParameterUnit of Measure
Heat energy costsEUR/MWh
Fuel costsEUR/liter
Cow cure costsEUR/year
Cow costsEUR/cow
Voluntary related support for milking cowsEUR/cow
Share of own financingDimensionless
Intensity of support measuresDimensionless
Table 4. Manure management method, level and factor.
Table 4. Manure management method, level and factor.
Management MethodManagement Level, PointsEmission Factor [42]
Deep bedding + mixing10.07
Solid storage20.02
Liquid systems30.0005
Anaerobic lagoon40.001
Biogas production50.0006
Biomethane production60
Table 5. Input data for the technology development.
Table 5. Input data for the technology development.
ParameterUnit of Measure
Time to implementYears
Manure priceEUR/ton
Max levelPoints
Initial levelPoints
Investments for technology improvement for one pointPoints
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Bumbiere, K.; Meikulane, E.; Gravelsins, A.; Pubule, J.; Blumberga, D. Progress of the Agricultural Sector toward Climate Neutrality: Identification of Essential Stages. Sustainability 2023, 15, 11136. https://doi.org/10.3390/su151411136

AMA Style

Bumbiere K, Meikulane E, Gravelsins A, Pubule J, Blumberga D. Progress of the Agricultural Sector toward Climate Neutrality: Identification of Essential Stages. Sustainability. 2023; 15(14):11136. https://doi.org/10.3390/su151411136

Chicago/Turabian Style

Bumbiere, Ketija, Edite Meikulane, Armands Gravelsins, Jelena Pubule, and Dagnija Blumberga. 2023. "Progress of the Agricultural Sector toward Climate Neutrality: Identification of Essential Stages" Sustainability 15, no. 14: 11136. https://doi.org/10.3390/su151411136

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop