1. Introduction
The environmental impact of agricultural production systems has become an increasing concern for scholars in recent decades [
1]. Such emphasis reflects the growing global concerns about sustainability and the urgent necessity for policy frameworks with the potential to address the various challenges arising in agriculture [
2]. Agriculture is among the sectors imposing the greatest pressure on the environment, both through direct impacts on ecosystems and through indirect effects that are transmitted along supply chains [
3,
4].
Modern agriculture affects the environment not only via land use and irrigation water withdrawals, but also through greenhouse-gas emissions, disruptions of biogeochemical cycles, and pressures on environmental quality associated with the use of chemical inputs—such as pesticides and fertilizers—and with production intensification, which can entail deforestation, destruction of natural habitats, and consequent biodiversity loss [
5,
6,
7]. In addition, some components of the environmental footprint attributable to agricultural production do not originate solely from on-farm cropping or livestock activities, but rather arise across the broader supply chain [
8]. Illustrative examples encompass the industrial production of agrochemicals, including pesticides, fertilizers, and antibiotics, and the post-harvest storage and transportation to processing facilities or final consumers. This complexity and intersectoral interconnectedness imply that analytical approaches confined solely to on-farm activities may underestimate overall environmental impacts, as they neglect the upstream burdens embodied in intermediate inputs and transmitted across supply chains [
5,
9]. These interconnections are notably evident when examining climate change and the environmental burden of agriculture: a significant portion of emissions associated with agrifood products derive from indirect processes occurring along the value chain, rendering footprint assessments highly sensitive to the delineation of system boundaries [
10,
11]. Similarly, assessments of water use in agriculture must be beyond direct withdrawals by the agrifood sector; this has led to the growing prominence of concepts such as the water footprint and virtual water, which quantify the water embedded in traded commodities and thereby reveal the spatial redistribution of water demand and associated environmental pressures across geographic regions and economic sectors [
12,
13,
14,
15]. In this regard, environmentally extended accounting studies indicate that agricultural production and the food industry often dominate both the intensity and the overall magnitude of the water footprint, and that part of the virtually embodied water in produced goods is exported through trade flows—reinforcing the need for analytical tools capable of capturing the economic system as a whole, rather than focusing solely on the point of production [
16,
17].
This emerging need aligns with the systems approach that is increasingly promoted internationally to transform agrifood systems. The FAO has explicitly advocated this perspective, underscoring that a systems approach is essential to analyze and manage intersectoral interdependencies, cascading effects, and trade-offs among environmental, economic, and social objectives [
18,
19]. Such an approach recognizes that interventions at one stage of the value chain can propagate and generate unexpected consequences elsewhere in the production system and across other sectors [
20]. In doing so, there is a clear need for analytical tools able to capture intersectoral interdependencies by tracking production from its origin to final consumption. Among the available models, Environmentally Extended Input–Output (EEIO) models provide a framework capable of representing intersectoral linkages while attributing environmental pressures not only to direct production processes but also to the indirect supply-chain activities activated by final demand [
21,
22,
23]. Indeed, EEIO analysis originated from extending Wassily Leontief’s 1930s input-output economic model by attaching environmental data—such as resource use or pollutant emissions—to industrial sectors. It evolved to bridge the gap between traditional monetary economic transactions and physical environmental flows, enabling analysis of environmental impacts across supply chains. In the agrifood context, this approach helps clarify how agrifood production and consumption activate energy, chemical, and material inputs across the entire supply chain, and how these inputs contribute to emissions, resource use, and overall pollution [
5,
16]. Consequently, the use of EEIO models is now well established for footprint estimation and environmental accounting, and is widely applied to analyze emissions embodied along global value chains [
24,
25]. EEIO approaches enable the analysis of material flows embodied in goods by reconstructing all stages of the supply chain and identifying the points at which environmental pressures are generated most intensively [
26,
27]. Such studies highlight the pivotal role of agriculture in the use of water and land, whereas construction and industrial activities are often responsible for higher energy requirements—creating trade-off configurations that require intersectoral analytical tools to be interpreted correctly. In addition, the relevance of EEIO models is further reinforced by growing interest in the Water–Energy–Food (WEF) nexus, which seeks to investigate interdependencies among water resources, energy systems, and food production and consumption [
28].
Despite the maturity of EEIO modelling and its expanding application across sectors, there remains a need to clarify how EEIO approaches have been applied to agricultural systems and how these applications have evolved over time. The growing corpus of studies on footprints, the water–energy–food nexus, and related themes makes it timely to map EEIO applications in order to identify dominant research topics, methodological shifts, and emerging trajectories shaped by recent empirical and technical developments. At the same time, the rising demand for economy-wide analyses to inform international policy agendas underscores the importance of understanding how EEIO has been used—and how it can be further used—as a systems-oriented tool to support the sustainable transformation of agrifood systems. In this respect, bibliometric studies are especially useful, as they provide a structured way to monitor the development of a research field and to trace how scholarly debates have evolved. The main objective of this study is to analyze the literature on EEIO applications to agricultural systems through a bibliometric approach. Specifically, the study aims to reconstruct the evolution of scientific output in this domain, identify the key authors and institutions that have shaped it, map the thematic and methodological trajectories that have defined the use of EEIO approaches in agriculture, and—through keyword co-occurrence analysis combined with thematic clustering of the assembled literature—identify the principal domains in which EEIO methodologies are currently applied within agricultural contexts (emissions trading, water management, energy-climate impacts, and agri-food chain sustainability). In fulfilling these aims, the analysis clarifies how EEIO evidence has been generated and how it can more effectively support research and policy for the sustainable transformation of agrifood systems.
The remainder of the paper is organized as follows.
Section 2 introduces the EEIO framework that forms the analytical foundation of the study.
Section 3 outlines the methodological approach and describes the data sources utilized in the analysis.
Section 4 presents the empirical results, followed by
Section 5, which interprets the findings and situates them within the broader literature and policy context.
Section 6 concludes the paper by summarizing the key contributions and identifying directions for future research.
2. Environmentally Extended Input-Output Models: A General Overview
The Input-Output model, introduced by Nobel Prize winner Wassily Leontief at the end of the thirties [
29,
30], analyzes economic systems by quantifying the direct and indirect interdependencies among sectors in satisfying final demand [
31]. By tracing flows of goods and services from primary inputs through successive stages of intermediate production to final consumption, the model enables the reconstruction of economic value chains. When extended to incorporate environmental or resource accounting—often termed environmentally extended input-output analysis—it can adopt a “cradle-to-grave” perspective, following economic activity from raw material extraction to end-use disposal. The primary concept of this analysis lies in the definition of the economic system as a set of sectors that produce goods and services, with each sector purchasing production inputs from the other sectors that make up the economic system [
32,
33]. The classical IO approach supposes that the inputs used in production are in fixed proportions and consequently there are constant returns to scale. This assumption leads to the definition of the matrix of technical coefficients
and to express the system as
, where
is the vector of the outputs and
is the vector of the final demand. Rearranging the terms yields the fundamental Leontief equation:
where
is the Leontief inverse, conventionally denoted by
in the literature. This matrix captures the whole production needs, both direct and indirect, necessary to satisfy any final demand shock [
22].
The IO framework is widely used to measure, to understand sectoral interdependencies and analyze the effects that new policies or exogenous demand shocks can have on the economic system and how these propagate within the various sectors with which the economy is described [
34,
35,
36]. Despite its analytical power, the monetary-only IO framework proved insufficient for capturing biophysical realities such as resource scarcity and environmental pressures—a limitation that motivated scholars in the 1960s–70s to integrate physical flows of energy, materials, and emissions into the model. This extension yielded EEIO analysis, which quantifies the direct and indirect ecological burdens associated with economic activity [
37,
38]. The EEIO model links environmental satellite accounts to the economic structure of the IO model that allow to estimate the environmental impact of all production sectors and consequently also the impact that can be generated by any demand shocks with the same mechanism explained in the previous studies.
In the EEIO implementation, the direct environmental intensities are represented by the coefficients
,which constitute the intensity matrix
. Its each element quantifies the amount of environmental pressure
—such as cubic meters of water consumed, hectares of land occupied, or tons of CO
2 emitted—generated per monetary unit of output by sector
[
22]. By combining the direct environmental intensity matrix
—whose elements
represent environmental pressure
per monetary unit of sector
output—with the Leontief inverse
, the EEIO framework captures both direct and indirect environmental impacts embedded in final demand. The product
yields the matrix of total environmental intensities, where each element reflects the full supply-chain burden (direct plus upstream indirect) associated with one unit of final demand. Hence, multiplying
by a final demand vector
gives the total environmental pressure
attributable to that demand; i.e.,
[
39].
The EEIO model is particularly well-suited for assessing environmental implications across the entire economy precisely because it accounts for sectoral interdependencies. By tracing supply-chain linkages through the Leontief inverse, the model captures both direct and upstream indirect impacts, thereby providing a comprehensive and accurate quantification of the environmental footprint embedded in production and final demand [
26]. In the literature, the EEIO model is widely used to calculate impact coefficients for emissions propagating them throughout the production chain [
40], for example an application on the economy of Croatia reflects how the carbon footprint changes when emissions are attributed to sectoral output compared to when they are attributed to final demand, highlighting the role played by indirect emissions that are incorporated in the intermediate inputs used for the production of the final output needed to meet final demand [
41]. Moreover, recent research demonstrates that EEIO-based footprint estimates, with their economy-wide coverage, effectively complement bottom-up approaches by capturing upstream supply-chain impacts that would otherwise be omitted or truncated in process-based assessments [
42].
When the analytical focus shifts to agri-food systems, the value of a framework capable of estimating aggregate environmental pressures becomes evident. Agricultural production draws heavily on natural capital and is tightly integrated with energy, chemical, manufacturing and logistics activities; consequently, a systems-level perspective that quantifies embodied resource use and emissions is essential [
43]. The EEIO model permits estimation of water, energy, land and pollutant burdens embedded in intersectoral flows associated with production, processing, transport, distribution and final consumption, thereby furnishing a rigorous basis for policy appraisal across the food supply chain [
44,
45]. Empirical applications attest to the method’s versatility; for instance, EEIO studies have quantified the water consumption and greenhouse-gas emissions embodied in food waste, providing an evidential foundation for assessing anti-waste interventions [
46]. In another related work, ref. [
47] reconstructed virtual grey-water flows within interprovincial agricultural exchanges, enabling the identification of critical nodes for water-quality management. Investigations of urban supply chains that integrate carbon and water accounting reveal that agriculture often displays a high intensity of embodied water even when aggregate emission profiles are dominated by other sectors, thereby underscoring the necessity of multi-indicator evaluations [
48,
49]. Therefore, the primary contribution of this review is to provide a consolidated, evidence-based roadmap that both clarifies how EEIO has been employed in agri-food research and guides future methodological refinement and policy translation. These findings aim to inform researchers and decision-makers on where EEIO analysis can most effectively support sustainable food-system governance and where further methodological development is required.
3. Research Methodology
3.1. Methods
Bibliometric analysis is a highly useful tool for researchers, as it allows us to quantitatively examine the evolution of scientific production and to assess techniques, methodologies and research trends within a given topic. Through the systematic analysis of publications over time, it enables the identification of correlations, collaboration networks, development trajectories and emerging trends, thereby offering a clear and structured overview of the state of the art in a specific field. One of the main advantages of these approaches, as highlighted by [
50], is their capacity to facilitate reproducible and dependable processes, thereby minimizing errors associated with manual and qualitative analyses of extensive datasets. Bibliometric analysis also supports the definition of research objectives, the delimitation of the field of inquiry and the identification of atypical results or gaps and trajectories that warrant further investigation. Building on these advantages, this study employs a bibliometric methodological framework to offer a comprehensive analysis of publication trends over time, identify the most influential authors, journals, and articles, and perform citation, collaboration, and keyword analyses.
3.2. Data Collection, Cleaning and Preprocessing
A systematic literature search for studies applying EEIO models in agriculture was conducted using two major bibliographic databases: Web of Science and Scopus. These complementary resources were chosen to maximize coverage across disciplines and publication venues, given their extensive, heterogeneous collections and established editorial standards. Results retrieved from both platforms were merged and deduplicated using Digital Object Identifiers (DOIs) so that each study was represented only once in the final corpus. This approach reduced redundancy and helped ensure the integrity of the dataset used to characterize the contemporary research landscape [
51,
52]. The PRISMA framework was used to report transparently the identification and selection of bibliographic records included in the final dataset. In this bibliometric review, PRISMA served to outline the main stages of the workflow rather than to support a qualitative appraisal of the full text of individual studies. These stages comprised database identification, application of eligibility filters, removal of duplicate records, and final inclusion.
Figure 1 summarizes the record selection process and provides an overview of how the bibliometric dataset was assembled.
The final bibliometric corpus used for the analyses was constructed on the basis of predefined inclusion and exclusion criteria. Only records retrieved through the search strategies applied in Web of Science and Scopus were retained, provided they were written in English and classified as articles or reviews in the field of agricultural systems. This approach is consistent with the scope of the study, which maps EEIO-based research across the broader agricultural and agri-food domain, including trade- and policy-oriented contributions insofar as they operationally employ an input–output or EEIO framework. Furthermore, Records were excluded if they appeared in both databases, were published in a language other than English, or belonged to document types other than articles and reviews. Accordingly, relevance was determined at the bibliographic record level through search strings and database filters rather than through manual full-text screening. This approach is consistent with the bibliometric design of the study, although it may have allowed a small number of borderline records to remain in the dataset. Since the two databases are different, it was necessary to develop two separate search queries, as Web of Science and Scopus rely on different syntaxes for searches within their respective platforms. We begin with the analysis conducted in Web of Science. The query, based on the Topic Search (TS) field, was as follows:
TS = ((((Environment*-Extended OR Environment* OR Extended) AND (Input-Output analysis OR Input-Output table* OR Input-Output matri* OR Input-Output model*)) OR (EEIO OR EE-IO OR EE-IOT OR EE-IOTs)) AND (agricultur*)).
This query returned 730 records. The results were then refined by applying inclusion criteria that limited the set to papers and review articles written in English, yielding a final sample of 675 English-language articles and reviews retrieved from Web of Science. Asterisks are used at the end of certain terms in the query to ensure that all words sharing the same root as the preceding string are captured. This device allows the query to be streamlined while at the same time avoiding the loss of potential synonyms, thereby enabling the selection of the largest possible number of relevant articles.
In Scopus, given its slightly different search system, the query had to be adapted. Instead of Topic Search, we used the field TITLE-ABS-KEY, which allows searching within titles, abstracts and keywords. The query used in Scopus was:
TITLE-ABS-KEY ((((Environment*-Extended OR Environment* OR Extended) AND (“Input-Output analysis” OR “Input-Output table*” OR “Input-Output matri*” OR “Input-Output model*”)) OR (EEIO OR “EE-IO” OR EE-IOT OR EE-IOTs)) AND (agricultur*)).
This search identified a total of 683 documents. The results were then refined by applying inclusion criteria that limited the set to papers and review articles written in English, yielding a final sample of 588 English-language articles and reviews retrieved from Scopus.
Across the two database searches, a total of 1263 English-language articles and reviews were initially identified. Following the removal of duplicate records through a data-cleaning procedure conducted in R, based on identical DOI entries, 350 duplicates were excluded, resulting in a dataset of 913 unique publications. Subsequently, a manual screening was performed to remove papers not relevant to the research topic. After this selection process, the final corpus consisted of 647 English-language articles and reviews.
This search and screening strategy enabled the construction of a temporal and geographical overview of EEIO-based research in the agricultural domain, while also facilitating the identification of the most research-active countries, the authors exerting the greatest scholarly influence, and the journals most central to the dissemination of EEIO-related studies. In addition, keyword co-occurrence analysis combined with thematic clustering of the assembled literature revealed the principal domains in which EEIO methodologies are currently applied within agricultural contexts. These domains arise directly from the intersection of EEIO techniques and agriculture-specific terms. They encompass studies on emissions trading that examine the integration of agricultural sectors into carbon markets, offset schemes, and the economic consequences of emission permits under EEIO frameworks; research on water management that applies EEIO analysis to evaluate virtual water flows, water footprints, and scarcity effects linked to agricultural production and trade; investigations of energy-climate impacts that quantify energy consumption patterns and broader greenhouse gas emissions—extending beyond trading mechanisms—arising from agricultural activities and supply chains; and assessments of agri-food chain sustainability that explore the overall environmental performance of food systems, including multi-regional supply linkages, waste management practices, and circular economy indicators in the agricultural sector. In this way, the approach offers a structured portrayal of the field’s evolution and underscores the key contributions that have shaped the use of EEIO models in analyzing agricultural systems across these critical areas.
3.3. Data Analysis and Visualization
All analyses were conducted in R (R Core Team, 2025) using R version 4.4.3 (28 February 2025), with the Bibliometrix package introduced by [
53] in the R statistical computing environment. The final dataset covered the period 1978–2025, and the bibliometric analyses presented here therefore reflect the entire study period. Bibliometrix supports text mining and science-mapping procedures, enabling the systematic examination and visualization of complex bibliometric data.
In this study, we combined conceptual structure analysis based on co-occurrence with author-specified keywords to examine EEIO applications in the agricultural sector, identify the main thematic areas, and detect emerging research frontiers. Overall, this bibliometric approach provides a comprehensive and in-depth view of the research landscape on the use of EEIO methodology in agriculture and supports evidence-based strategic research planning and decision-making.
5. Discussions
This study systematically reconstructs the evolution of the EEIO framework as applied to the agricultural sector and moves beyond a mere bibliometric account. Over the past decade the literature shows a marked increase in EEIO adoption, reflecting a clear demand for methods that represent the economy as an integrated system rather than as a collection of isolated sectors. By explicitly modelling intersectoral linkages and environmental flows across full supply chains [
101], EEIO approaches provide policymakers with robust quantitative instruments to design and assess sustainability strategies for agrifood systems. This methodological expansion has occurred in tandem with intensified global concern for environmental degradation, climate-change mitigation, the Sustainable Development Goals (SDGs), and the stewardship of increasingly scarce natural resources.
A review of keyword clusters and prevailing themes in EEIO studies applied to agricultural systems points to several research directions that currently guide the field. One prominent direction relates to climate change and is increasingly reinforced by public investment, particularly within Europe, aimed at developing analytical frameworks capable of assigning responsibility along complete production chains [
97]. A critical interpretation of these clusters reveals significant implications for the future development of EEIO research in agriculture. The prominence of Cluster 1 (Carbon, trade, and environmental policy) and Cluster 3 (Energy and climate impacts) suggests that the field is transitioning from static environmental accounting toward dynamic driver analysis. The increasing frequency of keywords such as “structural decomposition analysis” and “structural path analysis” indicates that future research must prioritize identifying the specific socioeconomic drivers of environmental pressure rather than merely quantifying footprints. This has encouraged a growing body of work on emissions embodied in intermediate inputs and on the distinction between production- and consumption-based impact accounting, which is central to the formulation of effective mitigation policies for agriculture [
102]. Similarly, the convergence of EEIO with LCA observed in the keyword trends points to a necessary methodological evolution: hybrid modeling. Future research should aim to reconcile the sectoral breadth of EEIO with the process-level detail of LCA to address the limitations of sectoral aggregation, particularly in heterogeneous agricultural systems. A second direction reflects the consolidation of the Water–Energy–Food nexus as both an analytical lens and a policy-oriented framework [
49]. From this perspective, EEIO models are especially valuable because they allow interconnections among resources and sectors to be examined within a single, coherent structure [
63,
103]. A third direction is linked to the expanding attention given to global value chains, which necessitates multi-country assessments of agricultural impacts. Recognition that a considerable share of environmental pressures is embedded in intersectoral and international exchanges highlights the relevance of EEIO for capturing cross-border effects and for framing agrifood sustainability within an increasingly globalized economy characterized by fragmented production processes [
80,
104]. The bibliometric findings also offer explicit insights into how EEIO trends relate to sustainability policies and agri-food system transformation. The observed exponential increase in publications post-2015 correlates strongly with the Paris Agreement and the adoption of the SDGs, suggesting that EEIO is increasingly utilized as a monitoring tool for Nationally Determined Contributions (NDCs) and international climate commitments. Furthermore, the strong association between “international trade” and “carbon footprint” keywords reflects the growing policy relevance of consumption-based accounting in the context of emerging regulations such as Carbon Border Adjustment Mechanisms (CBAM). The geographical analysis further elucidates divergent policy priorities: the European cluster’s focus aligns with the EU Green Deal and CAP, emphasizing regulatory harmonization and cross-border data sharing. In contrast, China’s dominance in the literature reflects policy priorities centered on domestic food security and supply-chain resilience. This dichotomy suggests that future EEIO applications must be context-sensitive, tailored to either support regulatory compliance in developed economies or enhance supply-chain stability in emerging economies. Within this context, the main application areas that emerge—such as emissions embodied in trade, water-resource use, energy and climate-related impacts, and the sustainability of agrifood supply chains—can be understood as methodological responses to these broader strategic demands [
94,
105]. Assessments of embodied emissions, for instance, are closely linked to evaluating climate-policy outcomes and to identifying situations in which apparent reductions in one region are offset by increased pressures elsewhere. Similarly, the strong emphasis on water-related analyses reflects the central role of agriculture in water security and system resilience, while illustrating the capacity of EEIO approaches to operationalize concepts such as water footprints in a manner that remains consistent with underlying economic structures and international trade relations.
With respect to energy and broader environmental impacts, energy is a fundamental determinant of agricultural performance and supply-chain outcomes: shifts in energy use, efficiency, or sourcing can substantially alter environmental results across production stages [
106,
107]. The literature increasingly documents trade-offs whereby productivity gains that lower impacts in one segment may amplify pressures elsewhere through greater fertilizer inputs, higher overall energy demand, and increased emissions from transport and logistics. Environmentally extended input–output analysis is well-suited to reveal these dynamics because it explicitly represents indirect and upstream linkages that single-sector methods typically overlook. By quantifying both direct and indirect flows, EEIO enables more reliable assessments of whether proposed interventions produce genuine net improvements or simply relocate environmental burdens across sectors or regions [
108].
The analysis of scientific-community structure and collaboration patterns indicates that the EEIO analysis in agricultural research is entering a phase of consolidation. A small set of well-established hubs coexists with a widening periphery of emerging contributors, a pattern that reflects both the recognition of EEIO as a standard analytical tool and the entry of new research groups responding to novel policy questions and increasingly detailed datasets. This diversification of contributors—drawn from a range of disciplinary backgrounds—underscores the cross-cutting nature and growing relevance of the framework. Nonetheless, the application of EEIO to agricultural systems encounters several important methodological limitations that must be acknowledged when interpreting results for policy use [
45]. First, core modelling assumptions—fixed technical coefficients, linear relationships, and homogeneous sectoral technologies—constrain the capacity of EEIO to capture intra-sectoral heterogeneity, structural change, and adaptive responses to external shocks [
109,
110]. Second, the sectoral aggregation embedded in conventional IO tables tends to mask variation among the disparate activities included within the agricultural sector [
111]. Third, environmental extensions are vulnerable to uncertainty, data inconsistencies, and researcher choices in accounting methods, all of which reduce comparability across studies [
112,
113]. However, a transparent assessment requires acknowledging limitations inherent to both the EEIO framework and this bibliometric study. Regarding the bibliometric methodology, the geographical distribution of publications is heavily skewed, with China accounting for a disproportionate volume of the literature, which may reflect specific national funding priorities rather than a global consensus. Additionally, the reliance on English-language databases may exclude significant local policy studies, and the correlation between publication spikes and policy events remains observational rather than causal. These constraints do not negate the value of EEIO; rather, they indicate where careful qualification and transparent reporting are required when using EEIO outputs to inform policy [
114].
These limitations also delineate a targeted research agenda that is closely aligned with the main themes identified in this review. Future studies should first use structural decomposition and structural path analysis to isolate the socioeconomic drivers behind embodied emissions, water use, and energy demand, rather than only reporting aggregate footprints. They should also develop hybrid EEIO–LCA frameworks, ideally tested on specific agrifood commodities or supply chains, to combine EEIO’s sector-wide coverage with the process-level detail needed to reduce aggregation bias. In parallel, multi-regional EEIO tables with higher sectoral and spatial resolution are needed to better represent international trade, supply-chain fragmentation, and regional heterogeneity, particularly in the context of climate policy and carbon border measures. Because environmental extensions and accounting choices can materially affect results, future work should apply formal uncertainty analysis, including stochastic simulation and sensitivity testing, to identify which assumptions most influence outcomes. Another priority is to extend EEIO into dynamic formulations that can capture technological change, substitution effects, and policy scenarios over time. Finally, EEIO should be coupled more systematically with land-use, ecological, and socio-economic models to examine feedbacks, trade-offs, and distributional effects across the water–energy–food nexus, while greater use of open data, harmonized indicators, and transparent reporting standards would improve reproducibility and cross-study comparability. Advancing these directions would make EEIO applications in agrifood systems more robust, policy-relevant, and actionable.
6. Conclusions
This study synthesizes how EEIO models have been deployed to study agricultural systems, based on a systematic corpus of 647 publications retrieved from Scopus and Web of Science covering 1978–2025. The bibliometric and keyword analyses show a clear acceleration of research since 2015, reflecting broader uptake of EEIO as a method for tracing economy-wide interdependencies and their environmental consequences. Four principal application domains emerge from the literature: emissions embodied in trade, water resource management, energy and climate-related impacts, and the sustainability of agri-food supply chains. At the country level, China is both the most prolific contributor and a central node in international collaboration networks.
These results confirm the practical value of EEIO for framing system-level questions in agriculture, while also underscoring well-documented methodological constraints. Fixed technical coefficients, coarse sectoral aggregation, and uncertainty in environmental extensions limit the capacity of standard EEIO results to resolve farm-scale or crop-specific processes. Consequently, findings based on EEIO demand careful interpretation when used to inform strategic decision making or policy design. To strengthen the evidence base and policy relevance of future work, we recommend three complementary directions. First, improve data resolution and harmonization by developing higher spatial and sectoral disaggregation and by standardizing environmental extension methods across databases. Second, integrate EEIO with higher resolution approaches, such as process-based life cycle assessment, farm-level surveys, remote sensing and agent-based models, to reconcile economy-wide accounting with production system detail. Third, adopt robust uncertainty and sensitivity analyses together with scenario exploration to make policy inferences more transparent and defensible. Additional priorities include expanding multi-regional EEIO frameworks to better capture trade-mediated impacts, and enhancing engagement with stakeholders and policymakers so that model outputs are interpretable and actionable.
In sum, EEIO remains a powerful framework for analyzing the complex interactions between agricultural production, intermediate demands and environmental pressures. Its capacity to inform a sustainable transition of agrifood systems will be greatest where improved data, methodological pluralism and explicit treatment of uncertainty are used to link economy-wide insights to the realities of specific crops, supply chains and governance contexts.