Abstract
In this paper, 15 farm-scale Green House Gas-based (GHG-based) decision support (DS) tools were evaluated based on a number of criteria (descriptive evaluation), as well as the parameters requested as inputs and the outputs, all of which are considered important for the estimation procedure and the decision support approach. The tools were grouped as emission calculators and tools providing indicators in terms of more than one pillar of sustainability. The results suggest an absence of automatic consultation in decision support in most of the tools. Furthermore, dairy and beef cattle production systems are the most represented in the tools examined. This research confirms a number of important functionalities of modern GHG-based DS tools.
1. Introduction
Nowadays, the need to communicate high-quality estimates of greenhouse gases’ (GHG) emissions as well as the effect of mitigation strategies at the livestock farm level to various stakeholders has become more and more intense [1]. Furthermore, high-quality measurements of GHG emissions at the livestock farm level are, in practical terms, almost impossible. In this respect, the role of farm-scale GHG-based Decision Support Systems (DSSs) is expected to increase in importance [2].
Until today, most of the research that has been conducted provides information about how GHG emissions are estimated and how these are involved in the sustainability assessment of an agricultural system [3]. In this review, various aspects of DSSs related to GHG emissions’ estimation and modeling, their use, as well as the information requested and provided were analyzed. As a result, basic characteristics of a modern GHG-based DSS are suggested.
2. Materials and Methods
A literature search was conducted and resulted in a selection of relevant, previously published review papers [4], papers focusing on specific tools, project reports, and case studies. Fifteen tools with potential for GHG emissions mitigation strategy selection were finally identified and used based on this literature search and proposals from the partners of a European research project. Two evaluation sections can be distinguished: (a) based on descriptive criteria; (b) based on checklists.
3. Results and Discussion
3.1. Evaluation Based on Descriptive Criteria
Table 1 shows the criteria and sub-criteria based on which the studied DS tools were descriptively evaluated.
Table 1.
Decriptive evaluation criteria and their evaluation parameters.
3.2. Checklists
3.2.1. Inputs of DS Tools
Table 2 presents the input categories and the types of inputs whose existence or non-existence was checked for the various DS tools studied.
Table 2.
Input categories and types of inputs checked in the tools evaluated.
3.2.2. Outputs of DS Tools
The categories of outputs that were checked in the DS tools evaluated were the following: (a) Environmental Impact Category Indicators (EICIs); (b) Emission per source; (c) CO2 (emission to air); (d) CH4 (emission to air); (e) N2O (emission to air); (f) Total GHG emissions (in CO2 eq); (g) NH3 (emission to air); and (h) Feed consulting.
3.3. DS Tools’ Evaluation
A short description of the DS tools in the context of the evaluation criteria (Section 3.1) and the inputs and outputs (Section 3.2) is given in Table 3.
Table 3.
Evaluation of the DS tools examined.
The use of scores for sustainability indicators is the major difference in the results presentation between the emission calculators and the all-pillar DS tools. Dairy and beef cattle production seems to be the livestock sub-sector that is most represented in the DS tools examined. Nevertheless, in the majority of these DS tools, stakeholders are not involved in their development. Scenario analysis, contribution analysis and progress monitoring seem to be the decision support approaches that are used by the majority of the DS tools examined. With respect to the provided outputs, a minority of emission calculators further provide livestock feed consultation as a type of output. Furthermore, the evolution to consulting decision support would be innovative and of importance for the wider use of such tools [5].
4. Conclusions
A modern GHG-based DSS for livestock systems would need to include clearly defined system boundaries and recently published emission estimation algorithms (e.g., the 2019 refinement of the IPCC 2006 Guidelines and Tier 2 approaches). It would need to consider GHG and ammonia emissions from all sources at the farm level (including feed crop production in case this in under the control of the livestock farmer) as well as soil carbon sequestration, by respecting the N and C cycles. Inputs from all the categories described for the emission calculator tools would be required in this respect. It would finally need to: (a) have an online user interface; (b) be easily accessible; (c) target inexperienced users and provide detailed guidelines regarding its use (but also be transparent with respect to the methodology followed); (d) provide easily comprehensible errors and easy handling of them; (e) involve stakeholders’ opinions before its release; and (f) have multi-national validity.
Author Contributions
Conceptualization, E.A. and V.A.; methodology, E.A.; investigation, E.A.; writing—original draft preparation, E.A. and V.A.; writing—review and editing, E.A., V.A. and T.B.; supervision, T.B.; project administration, V.A. and T.B.; funding acquisition, T.B. All authors have read and agreed to the published version of the manuscript.
Funding
This research was co-funded by the European Regional Development Fund of the European Union and Greek national funds through the Operational Program Competitiveness, Entrepreneurship and Innovation 2014–2020, under the call “European R&T Cooperation–Action of Granting Greek Bodies that Successfully Participated in Joint Calls for Proposals of the European ERA-NET Networks 2019b” (MELS project-funded under the Joint Call 2018 ERA-GAS, SusAn and ICT-AGRI on ‘Novel technologies, solutions and systems to reduce the greenhouse gas emissions in animal production systems’-project code: T11ΕΡA4-00076).
Data Availability Statement
The study did not report any additional data.
Acknowledgments
The authors would like to acknowledge the contribution of the partners of the MELS project (www.mels-project.eu) in collecting and proposing country-specific GHG-based DS tools to be evaluated.
Conflicts of Interest
The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.
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