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Research article Special Issues

The circular economy model in the agri-food sector: A new strategy for the regional development

  • Received: 27 June 2023 Revised: 25 July 2023 Accepted: 14 August 2023 Published: 04 September 2023
  • It is undeniable that the agri-food system is one of the greatest waste-producing sectors, with the inevitable generation of a certain quantity of scraps due to processing at an industrial level. Circular economy may offer a valid solution to overcome this problem, but the application of the model requires the availability of reliable data about quality and quantity of waste, which are currently missing. For this purpose, the objective of this paper is to address the issue of waste generation in the agri-food industry using a survey questionnaire. In-depth interviews were conducted with the owners or the technicians of selected case studies from the Marche region agri-food sector. Then, mass balance was applied based on primary data collected during the interviews. Moreover, to explore the potentiality of the circular model for the development of a regional agri-food sector, barriers, opportunities and services were also investigated. Results identified the vegetable and olive oil transformation as the most impacting in terms of quantities of waste produced. Food business operators currently find it difficult to give a proper definition of circular economy and envision the implementation of the model soon. However, they are also very enthusiastic and positive in finding alternative solutions to recover the waste. A great support could be provided by establishing a regional database for waste qualification and quantification. This work could be useful for policy makers, helping to understand the hurdles that agribusiness entrepreneurs shall face in this economic transition.

    Citation: Giulia Chiaraluce, Deborah Bentivoglio, Adele Finco. The circular economy model in the agri-food sector: A new strategy for the regional development[J]. AIMS Agriculture and Food, 2023, 8(3): 851-872. doi: 10.3934/agrfood.2023045

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  • It is undeniable that the agri-food system is one of the greatest waste-producing sectors, with the inevitable generation of a certain quantity of scraps due to processing at an industrial level. Circular economy may offer a valid solution to overcome this problem, but the application of the model requires the availability of reliable data about quality and quantity of waste, which are currently missing. For this purpose, the objective of this paper is to address the issue of waste generation in the agri-food industry using a survey questionnaire. In-depth interviews were conducted with the owners or the technicians of selected case studies from the Marche region agri-food sector. Then, mass balance was applied based on primary data collected during the interviews. Moreover, to explore the potentiality of the circular model for the development of a regional agri-food sector, barriers, opportunities and services were also investigated. Results identified the vegetable and olive oil transformation as the most impacting in terms of quantities of waste produced. Food business operators currently find it difficult to give a proper definition of circular economy and envision the implementation of the model soon. However, they are also very enthusiastic and positive in finding alternative solutions to recover the waste. A great support could be provided by establishing a regional database for waste qualification and quantification. This work could be useful for policy makers, helping to understand the hurdles that agribusiness entrepreneurs shall face in this economic transition.



    Agriculture today is one of the major contributors of environmental dilapidation [1], but in respect of major increases in production, more than one billion people globally suffer inadequate food and remain malnourished [2,3,4,5]. Organic farming is often suggested as a way-out to this challenge of attaining viable food security. However, it merely constitutes −1% of universal pastoral land and only supplies −1 to 8% of overall food sales in the majority of European and North American nations [6]. Organic is a brand that is recognised and bought by several shoppers, is the fastest emerging food sector in North America and Europe [7]. Assumed that organic farming is a contemporary and preferably extensive farming method and is one of the few legitimately controlled labels in farming, it is imperative to evaluate its benefits and ascertain how it can be improved in terms of its sustainability.

    Conversely, the advantages of organic farming are universally contested, although certain scholars encourage it by way of reducing poverty among rural households and also as one of the solutions to our sustainable food security challenges [8,9,10], while others see it as a drawback of agriculture that would agammaavate food shortage and ecological destruction [11,12,13,14].

    For instance, evidence shows that the per capital food output in sub-Saharan Africa has declined by twenty percent due to a decline in soil fertility over the past 20 years [15,16,17]. Nevertheless, organic farming offers the chance to improve soil fertility, which in turn will increase food production [18,19]. A similar observation was noted by Schnug et al. [12] on what organic farming can offer; which includes improvement of soil fertility, low cost of production, environmental protection, improve farmers' income and higher prices which serve as a premium for organic products sold in the market.

    Organic farming has a distinctive part to play in helping meet an array of goals like; environmental policy goals, and social capability of the organic systems. The environmental policy goals include those associated to fighting desertification and conserving bio-diversity [20], and balancing the magnitudes of global warming through carbon sequestration [21], while the social capability aspect centres on knowledge intensive that can combine traditional and indigenous farming knowledge [18,22]. As a result, the demand for healthier food, free from synthetic pesticide contamination and genetically modified organisms, is increasing the demand for organically produced foods [23,24]. The increase in the demands is related to certain factors such as concern for health [25], safer food [26], and the environment [27]. Improving the environment with the use of renewable resources is thus imperative in the production of safer food that will in turn have a beneficial effect on an individual's well-being [28].

    Previous reviews [8,10,29,30,31,32,33] have concentrated on the advantages of organic handling practices. However, this review will discuss a more significant question across the following scopes: benefits of organic farming in the context of its sustainability, yield performance and stability, economic performance, food security and environmental benefits of organic farming. Nevertheless, assumed the yields vary, and that the primary aim of agriculture is production, it is imperative to further asses the achievement of farming methods per unit output [34]. Per unit output influences are mostly pertinent to the environmentally friendly scopes. Our assessment is restricted to cropping methods. Therefore, animal wellbeing in precise is not discussed.

    The purpose of this paper is to present a systematic review of literature based on the context reliant of organic farming as a sustainable farming system. To realize this, appropriate research papers were reviewed; after gathering, assessing, and integrating data from an outsized number of sources. The appraisal was actualized systematically using distinct peer-review and non-peer review papers, books, and authorized publications. The basic short phrases used to explore the information were organic farming and sustainability. The terminologies were joined with economic effects, food security and yields, and environmental effects. The aforementioned terms were used in order to find related researches in developing and developed nations. Publications that were not written in English and those that were not from reliable sources are excluded.

    The word sustainability which is increasingly being used by researchers that now centre on the usage of earth's natural resources within a sustainable systems context are either inaccurate or non-existent [35,36]. In the perspective of agricultural production, McNabb [37] describes a viable agriculture as economically sustainable, environmentally friendly, resource- conserving, able of sustaining its efficiency and functionality to society over the long run and socially supportive. Therefore, organic agriculture is said to be an appropriate and sustainable alternative for improving food security [28], increasing farmers' income [38,39] and decreasing input cost [40,41], producing healthy food for household consumption [28] and maintaining an eco-friendly environment [42,43,44].

    There are other facts that should be put into consideration when estimating the viability of the finishing crop produce, which may include the cost-effect performance and dietary aspect that makes organic production sustainable [44]. It is also important to note that organic farming offers some arrays of environmental benefits such as evaporation minimization and water saving, biodiversity conservation, and improved soil component, support adaptation approaches, and lessens greenhouse gas emissions as well as energy efficacy [10,45]. A combination of data from multiple studies by Rahmann [46] indicates that biological diversity in organic holdings is greater than in conventional holdings in that out of a total of 396 related studies, 327 instances revealed greater than in conventional holdings. Similarly, a study by Bengtson et al. [47] in a comprehensive meta-analysis of biodiversity in organic farms reveals that, on average, in organic holdings, animals of the same species multiply in richness by about thirty percent while, the fruitfulness of organisms was fifty percent higher in contrast with conventional methods. Faunas' abundance in birds, predacious insects, plants and soil micro-organisms augmented while non-predacious insects and pest did not increase. However, the soil conservation approaches in organic farms have the capability to rebuild degenerated lands and to stop further degeneration in resistless areas [48].

    The approaches employed to preserve the soil in organic methods include; planting cover crops, moderate or zero tilling of the soil, mulching and contour tilling, and soil coheres as well as terraces [49]. A study by Gattinger et al. [50] indicates that the proportion of organic soil material in organic schemes is remarkably more than in conventional methods. The findings of this research, however, shows that organic material augments water infiltration into the soil and therefore lessen soil disintegration by expanding soil food-webs that enhance the nitrogen (N) sequence within the soil [45], hence conserve water resources. Additionally, in line with the exclusion of manmade manures and pesticides in organic production, the menace of soil, air and water pollutions by synthetic materials is substantially lesser than in conventional methods [51,52]. The organic farming method has a significant benefit with respect to energy use [53,54,55] as compared to conventional methods. For instance, in organic maize production, fossil fuel materials were thirty-one percent lesser than conventional farms and seventeen percent lesser in soybean production [56]. Similarly, a study carried-out by Mader et al. [57] in Central Europe on organic farming revealed that the fertilizer inputs and energy use were lessened by thirty-four percent to fifty-three percent. Ultimately, without doubt, organic farming has proved to be more significant and appropriate for small-scale farmers because of its dual ability for mitigation and adaptation approaches, both of which improve the environs' resilience to climate variability [50].

    Given the rising interest for organically made foods, questions relating to the capability of organic techniques to succeed like the modern and imminent universal agricultural demand have been raised [43,44]. Fess and Benedito [44] argued that some authors often allude to low yield productivity as the main barrier impeding the reliance of agricultural collaborators in the capability of organic techniques to meet up with the necessities of the populace. However, yield is habitually the only facet of crop productivity that is mostly debated when relating entire scheme conventional and organic practices.

    Generally, crop yield is usually regarded by farmers as the ultimate essential achievement in crop production [44]. The variation in crop produces between organic and conventional techniques has long been viewed as the main problem constraining the acceptance of organic production management by either small or large farmers [44]. The extant literature shows that, studies that have pointed out yield gap between organic and conventional crops include; Pimentel et al. [52]; Badgley et al. [9]; De Ponti et al. [58]; Seufert et al. [45]; Lee et al. [59]; Kniss et al. [60]; and Suja et al. [61]. In their various findings, they observed that most of these studies comprise elements that may generate partiality when explaining the results. Pimentel et al. [52]; Badgley et al. [9]; De Ponti et al. [58]; Seufert et al. [45]; Lee et al. [59]; Kniss et al. [60]; and Suja et al. [61] further added that exploratory weaknesses that often affect the cogency of early studies differentiating scheme produces comprised of; the use of crop species established for conventional high-input schemes, which are likely not have the same high quality potential in a resource-restricted condition, as well as uneven utilizations of fertilizer between schemes. Although numerous exploratory partialities are present, the results of Lee et al. [59]; Kniss et al. [60]; and Suja et al. [61] state that crop yield under conventional management is higher when compared to organic systems, especially among grains and horticultural crops. On the other hand, an insignificant number of studies have investigated considerable produces from organic schemes mainly for forage (buckwheat, alfalfa, and rye) and hay (perennial and legumes) crops compared to conventional schemes [44].

    Yields of organic farms in most developing nations are often too low as compared to conventional farms, and this may be a drawback for some farmers in the production system [48,62,63]. Jouzi et al. [48] argued that organic agriculture is advantageous to resource-poor farmers in improving food security and increasing income. The prospective benefits of organic farming depend, conversely, upon a number of vast context specific factors like economic, environmental, social benefits, health and dietary benefits derived in organic foods [37,64,65]. The International Fund for Agricultural Development [IFAD], [66] noted in an assessment conducted in Latin America on small-scale organic farms that these factors require management of a collection of knowledge. However, knowledge should be centred upon farmers' organization, technical support and quality control on food production, which will further contribute to the development of small-scale farmers in ensuring food security, increased income and enhanced livelihoods. Notwithstanding, Table 1, shows a relative evaluation on yield differences between 'organic and conventional' methods as indicated by several scholars.

    Table 1.  Analysis on yield difference between organic and conventional methods.
    Citation Author's conclusions
    [58] Based on yield average, organic was "80%" higher from those of conventional methods.
    The comparative yield of pre-2004 statistics were statistically related to 2004-2010 figures, signifying that relative yield performance of organic system had not changed.
    [45] Across various produces, yields from organic methods were on average "25%" lower as compare to conventional ones.
    Vegetables and cereals from organic production are reported to have a lower yields than conventional crop, "26% and 33%", respectively.
    Organic fruits and oilseed crops show a slight reduction in yields as compared to conventional ones, "3% and 11%" respectively.
    An improved organic realization of "perennial over annual crops, and legumes over non-legumes" was demonstrated.
    The difference in yield between organic and conventional produces in developing nations is higher than in developed nations, "43% and 25%" respectively.
    [67] Yields from organic cotton systems was "42% lesser than conventional ones during the first rotational cycle, while yields were equal in cycle 2".
    Yields from soybean were "7% lesser" in organic systems than conventional systems.
    Yields from wheat in organic fields was "37% lesser" than conventional counterpart during the first rotational system, but equal afterwards.
    [59] Saleable yield was greater in "conventional than organic onion fields, 71.5 and 55.8 t ha", respectively.
    Freshly harvested conventional onion weight "220.2g/plant" was higher than organic onions "175.6g/plant".
    [68] Multiply scientific studies proved that organic yields were "19.2%" lesser than conventional yields ---signifying a lesser yield difference than formerly found.
    Multiple cropping and crop cycle used in organic approaches lessen the yield gap.
    [60] Hay from organic systems had equal yields or greater than conventional hay crops.
    Organic peach, squash, sweet maize, and snap bean yields were equal to conventional counterparts.
    [61] Equal yield attainment of taro in an organic and conventional management practices, "10.61 and 11.12 t ha", respectively.
    Equal yield traits between organic and conventional approaches under "cormel number, yield per plant, and weight and number of mother corms".
    Source: Adapted from Fess and Benidito (2018).

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    The meta-analysis on yield difference from various authors has shown different results on yield performance of organic against conventional farming. The differences in the average yield performance may be attributed to different management practices, region and different agro-ecological zones. The average yield performance of organic farming tends to be higher than conventional as reported by some authors in some regions while others reported a lower yield as compared to conventional ones. Though, in some studies, it was observed that organic yields were equal to conventional ones. In general, the findings of various authors show that organic yields are lower than yields in conventional systems.

    The meta-analysis study of the data presented above report yield over a period of time, showing dissimilarities between systems over time. However, the statistics propose that for the duration of the conversion period, the first three to four years of organic production, which is about the same time necessitated to conclude one full crop cycle, organic techniques are susceptible to lesser produces [44], thereafter by periodic rises as the soil attribute and microbe populations are rebuilt, after which the yield difference is notably lower or no longer prevalent (Table 1). The comparative meta-analysis piloted by Ponisio et al. [68] further showed that multiple cropping and extending rotation cycle can further decrease the yield difference between conventional and organic methods by four to nine percent. Furthermore, it should be noted that nitrogen that is available in organic systems is determined by the level of nitrogen minerals, which is greatly determined by soil temperature. Thus, it is probable that greater yield differences between systems occur for "early season crops" compared to "mid and late season crops" that are sown into warm soils with larger micro-organism activity.

    It is therefore important to note that on yield average, organic crops were eighty percent higher [58], signifying that there is a prospect for small-scale farmers when they convert to organic management. Additionally, yield differences tend to be higher in organic crops, especially in developing nations [45]. This signifies that farmers can produce surplus which in turn can be exported to developed nations resulting into financial gains for the farmers through the export of their produce.

    Yields are considered as a vital harvest to producers, and for that reason it is directly allied to the monetary performance and the utmost aim of the farming process, as well as the livelihood of families and communities involved [44]. It is thus feasible that if the cost-effect achievement of organic schemes is akin to those of conventional practices, then more farmers would think about shifting to organic management system. Fess and Benedito [44] noted that the economic performance of a crop can be evaluated by lessening the overall expense of agricultural inputs required for production from the current market price of the harvest. Fess and Benedito [44] further argue that regardless of the clearly unrelated input practices, a number of current studies specify that the overall expenses related with production were largely comparable. These variations were accredited primarily to the use of labour and synthetic inputs, specifically the control of pest using mechanical method. A number of studies that have compared comparative analysis of organic to conventional crops includes; Crowder and Reganold [69]; Sgori et al. [70]; Bett and Ayieko [71]; and Fess and Benedito [44]. Their studies focused on the financial competiveness of production techniques and found out that labour expenditures were seven percent higher in organic methods as compared to their conventional counterparts. However, the augmented labour expenditures were counterbalanced by the cost related with the use of fertilizers and pesticides in conventional systems. Similarly, Bennett and Franzel [72] noted that the augmented labour force needed for organic production has been recommended as a means to enhance rural firmness in Latin America, Mediterranean area, and Africa, through the reallocation of assets to the underemployed, possibly resulting to economic enhancements for the neighbouring communities. Therefore, the role of organic farming cannot be underestimated as it has been proved to have a positive impact on the economy of a nation, through the provision of increased manpower, leading to rural stability.

    Crowder and Reganold [69] while relating the global competitiveness of organic farming in an innovative meta-analysis, indicate that organic techniques were significantly more cost-effective in spite of lower crop harvests, obtaining twenty-two to thirty-five percent higher net present value (NPV) in contrast to conventional ones. Generally, the economic performance of organic schemes is said to rely on the "premium prices" attained at the market [44]. According to Bett and Ayieko [71], the price of organic produces is usually thirty percent higher than those of the non-organic produces. Nevertheless, the break-even premium entailed to counterpart the economic performance of conventional schemes, factoring in the roughly twenty percent lesser yields of organic fields, demands that premium prices need to be only five to seven percent greater than the price of the conventional ones [69]. Crowder and Reganold [69] also argue that the consistency and economic suitability of organic methods is greater than that of conventional processes. Thus, it is vital to retain ethics that ensue in excellence products to keep consumer trust. However, "premium prices" attached to organic products, coupled with the potential long-term profitability offered by organic produces should provide attractive motivations to organic producers to make the transition to organic production more lucrative. Table 2, shows a relative evaluation of economic performance between organic and conventional cropping methods.

    Table 2.  Economic performance between organic and conventional cropping techniques.
    Citation Author's conclusions
    1. [40] Total revenues for organic systems were higher than conventional ones, US "$286" and "$78" acre, respectively.
    In conventional systems cost-effect risk was higher than organic ones with similar rotation cycle of three years.
    2. [67] Higher gross margin (21%) was observed in conventional systems during the first length of the two years rotation but after the second phase organic gross margin were higher.
    Different variable cost in conventional production (cotton-38%, soybean-66%, and wheat-49%) respectively, was greater compared to organic systems.
    Costs of labour were the same in both production systems.
    3. [73] Overall life progression cost of conventional lemon was higher (€180,533) than organic production (€178,074 ha) respectively.
    Costs of producing conventional oranges were greater compared to organic ones, €154,110 ha, and 133,159 ha, respectively.
    4. [74] Initial and imminent expenses of conventional and organic olive productions were the same.
    Costs of soil management were greater in organic olives compared to conventional ones.
    Earnings were greater in the organic systems than conventional counterparts due to premium price and subsidies applied.
    Organic systems experienced greater internal rate of return [IRR] of 3.51% than conventional counterparts 3.37%.
    5. [69] Costs of labour in organic production were 7% higher than conventional ones.
    NPV of organic farming was lesser 27% than conventional ones 23% when price premiums are not attached.
    When premiums are attached, organic systems were 22-33%, more cost-effective than conventional ones.
    Overall costs, NPV, total revenues, and benefit/cost ratios for organic were higher compared to conventional ones over 40 years study period.
    6. [71] For low input organic agriculture, NPV was higher as compared to conventional ones in Kenya.
    7. [39] Soybeans from organic system were more profitable than conventional ones
    Organic system had a higher mean performance of profitability (11-15%) greater than conventional ones, but was allied with higher risk.
    Source: Adopted from Fess and Benedito (2018).

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    The findings of Crowder and Reganold in the data presented in Table 1, suggest that organic systems were significantly more profitable in spite of their lower yields, attaining twenty-two to thirty-five percent higher net present value (NPV) in contrast to conventional ones. Although, findings show that organic produces are more lucrative as a result of the premium price they attain when selling the products (Table 2). As a result of the premium price in organic production, there is a greater effective net cash flow that resulted to a reduced period of attaining an effective net cash flow. However, if premiums are not applied to these produces, the economic gains of organic production could be lessen below conventional ones. Quite a number of current studies contrasting profitability confirmed that organic systems receive more financial gain than conventional ones. Reliably, higher NPV and IRR have been reported across different crops like field crops and tree fruit grown within the organic system in contrast to conventional system (Table 2). The figures show that the financial gains earned differ based on crop and the country at which they are grown. Notwithstanding, the organic revenues were not consistently sizeable over conventional production, but it was noted that they may offer adequate incitement subject to the financial condition of the producer/farmer, especially for those in developing nations and evolving markets.

    Generally, the financial figures outlined from a number of studies show that the cost-effective achievement of organic systems is dependent on the premium prices attained at the market. At present, the price of organic produces is basically thirty percent higher than those of non-organic ones as highlighted in (Table 2). It is therefore imperative to note that premium prices are significantly higher than the break-even prices. The prospective longstanding profitability offered by organic produces should therefore offer attractive incitements to farmers to make the conversion to organic management.

    At the 1996 Food and Agriculture Organisation (FAO) on World Food Summit, as cited in the work of Pérez-Escamilla [75] the term food security is described as the capability of all individual at all time to have access to adequate, non-toxic, and nourishing food to sustain a healthful and lively life. For all individuals to be food secure; the pillars of food security must be considered. These pillars are summarized into four dimensions as noted by FAO [76]; Aborisade and Bach [77]; and Pérez-Escamilla [75] as food availability, accessibility, utilization or affordability, and stability. Kanu [78] highlighted in a review on organic farming that food accessibility is attained when households and individuals have adequate sources to consume a suitable diet.

    Several studies have indicated that organic farming could add significantly to farmers' food security and enhance farmers' livelihoods [18,50,78,79]. However, if organic farming is to play a significant part in providing sustainable food security and viable incomes, it needs to be accessible to resource-poor farmers. Organic farming by its approach has realised three of the Sustainable Development Goals. These goals are summarized by Setboonsarng and Gregorio [28] in Table 3.

    This approach however, relies on five variables to realize its proposed purpose such as human, natural, physical, social, and financial development, hence supporting and forming these variables will help to mitigate many of the factors that inhibit food security in the world [80].

    Table 3.  Summary of the potential and realized benefits of organic farming in relation to the Sustainable Development Goals.
    Goal Potential contributions
    SDG 1: Eradication of extreme poverty Provide incomes to resource-poor and marginal farmers.
    Low cash costs suitable to resource-poor and marginal farmers.Sustainable production.
    Higher incomes from premiums of organic produce.
    Labour-intensive nature can help absorb excess rural labour and can lower rates of rural-urban migration for work.
    SDG 2: Zero hunger Diversified cropping system, mitigate risks of crop failure.
    More nutritious food.
    Enhance productivity and sustainability of productive bases.
    Helps protect genetic resources.
    SDG 3: Good health and well-being Non exposure to chemicals improves health and promotes healthy lifestyles.
    Source: Adopted from Setboonsarng and Gregorio (2017).

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    Agricultural land use is not only the prime driver of biodiversity loss [81], but methods of producing food that also rely on several guidelines and underpinning ecosystem services like soil nutrient cycling, pest regulation and crop pollination from biodiversity are also some of teeming causes of biodiversity loss [82]. Restoring biodiversity loss in agricultural methods of producing food requires practices such as organic farming handling methods of food production. The advantages of organic handling for biological diversity of flora and fauna on plantations are comprehensible, with a distinct rise in living organism richness of forty to fifty percent across various taxa [20,47]. The impact of organic farming on species richness is less clear, ranging from one to thirty-four percent as indicated by [62]. However, some scholars have asserted that the frequently perceived species abundance upshot [47,83] might be determined by an elementary control group outcome at higher organism compactness [20].

    In general, it appears that plants [83] and bees [84] are more advantageous from organic handling, although other arthropods and birds benefit to a lesser extent [83,85]. It was observed that higher advantages of organic handling are seen in basic landscapes with high agricultural land cover [83] and lesser habitat quality [84] and in regions with intensive agriculture [85]. There is evidence that clearly shows that organic farming has a resilient influence on biodiversity in arable methods (for instance, cereal) as compared to grassland methods [83,85] and a stronger influence based on individual fields than at the farm scale [85].

    Due to the significance of habitat transformation for biodiversity loss, an evaluation of the influence of farming methods on biodiversity has to control yields, which a small number of studies have carried out to date [86,87]. The studies of both Gabriel et al. [86] and Schneider et al. [85] proposed that there are trade-offs between the biodiversity advantages of organic handling yields. However, Gabriel et al. [86] further argued that although previous studies had revealed higher organic advantages for biodiversity per unit area in basic landscapes [50,88,89], in a diverse and low-productivity landscapes, biodiversity per unit efficiency might be of better advantage specially from organic handling practices. Reasons given by these scholars were due to lesser yield variance between organic and its conventional counter-part.

    Soil quality in relation to soil healthiness has frequently remained at the fundamental of organic beliefs [90]. Soil formation and soil mineral replenishment are vital supporting means for producing food [82]. On the other hand, soil dilapidation and soil attrition, which currently have a negative effect on outsized areas of land as a result of the continual use of croplands and rangelands, impend present and imminent ways of producing food and are a crucial sustainability challenge for agriculture [91].

    Various meta-analyses and quantitative studies have revealed that soils under organic management systems have higher organic carbon content [50,88,89,92]. Similarly, studies have also classically identified reduced soil erosion from organic farms due to enriched soil composition [93,94], but more studies are required to quantify these variables [62]. Primary studies for instance, Mäder et al., [57]; Stockdale et al., [95]; Watson et al., [96] have equally revealed enhancements in other soil health and richness specifications such as soil mineral condition and or soil physical properties under organic handling. In spite of these generally positive influences of organic handling on soil specifications, the soil fauna does not appear to be species rich in organic soils [47,83], but it is more rich in soils that are organically managed [47].

    Nevertheless, it is important to note that the amount of organic matter inputs, such as composts or animal manure, has a greater impact on soil organic carbon content [89,50,88]. However, there is poor understanding of other prospective significant drivers, like the presence of legumes in crop rotation [50], or of the influence of organic farming on soil quality per unit output [93,94].

    Agriculture, which is accountable for about 22% of universal anthropogenic greenhouse gas (GHG) emissions, including deforestation [97], is a major contributor to climate change. Agricultural greenhouse gas emissions from croplands and pasture (excluding livestock methods) are mostly in the form of N2O emissions from agricultural soils (from fertilizer and manure application and crop residue management), CH4 emissions from paddy cultivation, and CO2 emissions through energy use for instance, for fertilizer production and machinery use [97].

    Generally, both N2O and total GHG emissions per unit area appear to be lesser under organic handling for most crops [88,98,99]. Studies of organic achievement for CH4 emissions from rice paddy are limited [62]. The review by Skinner et al. [98] is centred on a single-field study. Conversely, the partial proof proposes higher CH4 emissions from organic paddy handling [100]. Overall, organic farming leads to reduced energy use due to avoidance of artificial fertilizers [32,88,99]. Typically, organic agriculture increases soil organic carbon content [50], which is frequently argued to contribute to carbon sequestration [21]. Due to uncertainties about the eventual fate of stored carbon; how long the sequestration will continue; whether it will be permanent and the counterfactual on how the carbon inputs would otherwise have been used, and its potential for climate change mitigation through carbon storage in agricultural soils remains heavily contested [101]. Thus, this study does not consider soil carbon storage as a climate change mitigation option here.

    Due to the importance of land conversion for CH4 emissions that is, deforestation for agriculture represents about 7% of global anthropogenic CH4 emissions [97], per unit output effects are mostly important for climate change mitigation. Emerging evidence on GHG emissions has clearly shown that GHG emissions per unit output mostly comes from modelling and life-cycle analysis studies and show high variability in outcomes [88,99]. On the other hand, N2O emissions per unit output appear to be higher under organic management because of lower yields [98], whereas CH4 emissions from paddy soils per unit output might be even higher than per unit area [100]. However, energy consumption per unit output tends to remain lower in organic management system, but with high variability [32,88,99].

    To date, quite a number of studies have identified background factors driving GHG emissions in organic against conventional systems. Lee et al. [102] revealed that the benefit of organic management in relation to energy consumption is lower for vegetables and fruits, whereas the benefit in terms of GHG emissions was higher in mono-cropping systems compared to multi-cropping and with outcome measures based on area rather than output [102].

    Agriculture centred on organic ethics is fast growing and becoming well known as a promising major contributor towards fighting poverty and hunger, attaining food and nutritional security as well as eco-friendly environment. This is despite the fact that some scholars have criticised it as a drawback to agriculture. Organic farming has some clear advantages and favourable features. For instance, its beneficial impact on local biodiversity, high performance in some conditions, or a livelihood for resource-poor farmers in some circumstances cannot be understated. However, many unresolved questions and concerns remain, like Nitrogen availability, accessibility, and impact on Nitrogen losses from the soil.

    It is also significant to mention that the comparative achievement of organic farming to conventional farming differs substantially. It is highly reliant on context and that estimates of the average performance of organic farming have limited practical use. This study shows superior differences in yield between the two systems, for biodiversity of "plants and pollinators in arable methods and simple landscapes". Conversely, the key factor facing the production of organic food system is the capability of the system to increase yields as compared to conventional schemes. Organic techniques indicate some advantageous system oriented skill, which is essential for enhancing prolonged sustainability and improving biological diversity and is beneficial for farmers who are resource poor.

    The stated goals of organic farming are achieving optimal agro-ecological systems which are socially, ecologically and economically sustainable. In addition, a global shift to organic farming may not only have the prospective to support food production levels but also conserve and improve agricultural soils fertility and health, which in turn increases fauna biodiversity in the soil. Thus, the sustainability and investments of organic farming should be supported by several stakeholders since it can mitigate some of the teeming challenges posed by climate change.

    The authors wish to express gratitude to the University of Fort Hare and also the Govan Mbeki Research and Development Centre of the University of Fort Hare for their support to develop this paper.

    There is no conflict of interest.



    [1] Girotto, F, Alibardi, L, Cossu, R (2015) Food waste generation and industrial uses: A review. Waste Manage 45: 32–41. https://doi.org/10.1016/j.wasman.2015.06.008 doi: 10.1016/j.wasman.2015.06.008
    [2] Thyberg KL, Tonjes DJ (2016) Drivers of food waste and their implications for sustainable policy development. Resour Conserv Recycl 106: 110–123. https://doi.org/10.1016/j.resconrec.2015.11.016 doi: 10.1016/j.resconrec.2015.11.016
    [3] Giordano C, Alboni F, Falasconi L (2019) Quantities, determinants, and awareness of households' food waste in Italy: A comparison between diary and questionnaires quantities. Sustainability 11: 3381. https://doi.org/10.3390/su11123381 doi: 10.3390/su11123381
    [4] Charatsari C, Lioutas ED, De Rosa M, et al. (2022) Technological innovation and Agrifood systems resilience: The potential and perils of three different strategies. Front Sustain Food Syst 6: 872706. https://doi.org/10.3389/fsufs.2022.872706 doi: 10.3389/fsufs.2022.872706
    [5] Agnusdei L, Krstić M, Palmi P, et al. (2023) Digitalization as driver to achieve circularity in the agroindustry: A SWOT-ANP-ADAM approach. Sci Total Environ 882: 163441. https://doi.org/10.1016/j.scitotenv.2023.163441 doi: 10.1016/j.scitotenv.2023.163441
    [6] Faccilongo N, Pellegrini G, La Sala P (2017) Economia circolare e scarti nelle filiere agroalimentari: Prima indagine esplorativa sullo stato dell'arte. L'industria 38: 221–240. https://www.rivisteweb.it/doi/10.1430/87786
    [7] Hall KD, Guo J, Dore M, et al. (2009) The progressive increase of food waste in America and its environmental impact. PloS one 4: e7940. https://doi.org/10.1371/journal.pone.0007940
    [8] Scherhaufer S, Moates G, Hartikainen H, et al. (2018) Environmental impacts of food waste in Europe. Waste Manage 77: 98–113. https://doi.org/10.1016/j.wasman.2018.04.038 doi: 10.1016/j.wasman.2018.04.038
    [9] Tonini D, Albizzati PF, Astrup TF (2018) Environmental impacts of food waste: Learnings and challenges from a case study on UK. Waste Manage 76: 744–766. https://doi.org/10.1016/j.wasman.2018.03.032 doi: 10.1016/j.wasman.2018.03.032
    [10] Venkat K (2012) The climate change and economic impacts of food waste in the United States. Int J Food Syst Dyn 2: 431–446.
    [11] Stancu V, Haugaard P, Lähteenmäki L (2016) Determinants of consumer food waste behaviour: Two routes to food waste. Appetite 96: 7–17. https://doi.org/10.1016/j.appet.2015.08.025 doi: 10.1016/j.appet.2015.08.025
    [12] Rosenberg M (2021) Thoughts about food security, food loss and waste and what has to be done. AIMS Agric Food 6: 797–798. https://doi.org/10.3934/agrfood.2021048 doi: 10.3934/agrfood.2021048
    [13] Hamilton HA, Peverill MS, Müller DB, et al. (2015) Assessment of food waste prevention and recycling strategies using a multilayer systems approach. Envir Sci Tech 49: 13937–13945. https://doi.org/10.1021/acs.est.5b03781 doi: 10.1021/acs.est.5b03781
    [14] Cristóbal J, Castellani V, Manfredi S, et al. (2018) Prioritizing and optimizing sustainable measures for food waste prevention and management. Waste Manage 72: 3–16. https://doi.org/10.1016/j.wasman.2017.11.007 doi: 10.1016/j.wasman.2017.11.007
    [15] Tavill G (2020) Industry challenges and approaches to food waste. Physiol Behav 223: 112993. https://doi.org/10.1016/j.physbeh.2020.112993 doi: 10.1016/j.physbeh.2020.112993
    [16] FAO (2019) The State of Food and Agriculture 2019. Moving forward on food loss and waste reduction. Food and Agriculture Organization of the United Nations, Rome. Licence: CC BY-NC-SA 3.0 IGO. Available from: https://www.fao.org/3/ca6030en/ca6030en.pdf.
    [17] Papargyropoulou E, Lozano R, Steinberger JK, et al. (2014) The food waste hierarchy as a framework for the management of food surplus and food waste. J Cleaner Prod 76: 106–115. https://doi.org/10.1016/j.jclepro.2014.04.020 doi: 10.1016/j.jclepro.2014.04.020
    [18] Ghisellini P, Cialani C, Ulgiati S (2016) A review on circular economy: the expected transition to a balanced interplay of environmental and economic systems. J Cleaner Prod 114: 11–32. https://doi.org/10.1016/j.jclepro.2015.09.007 doi: 10.1016/j.jclepro.2015.09.007
    [19] Teigiserova DA, Hamelin L, Thomsen M (2020) Towards transparent valorization of food surplus, waste and loss: Clarifying definitions, food waste hierarchy, and role in the circular economy. Sci Total Environ 706: 136033. https://doi.org/10.1016/j.scitotenv.2019.136033 doi: 10.1016/j.scitotenv.2019.136033
    [20] Kusumowardani N, Tjahjono B, Lazell J, et al. (2022) A circular capability framework to address food waste and losses in the agri-food supply chain: The antecedents, principles and outcomes of circular economy J Bus Res 142: 17–31. https://doi.org/10.1016/j.jbusres.2021.12.020 doi: 10.1016/j.jbusres.2021.12.020
    [21] Lucia C, Laudicina VA, Badalucco L, et al. (2022) Challenges and opportunities for citrus wastewater management and valorisation: A review. J Environ Manage 321: 115924. https://doi.org/10.1016/j.jenvman.2022.115924 doi: 10.1016/j.jenvman.2022.115924
    [22] Andersen MS (2007) An introductory note on the environmental economics of the circular economy. Sustain Sci 2: 133–140. https://doi.org/10.1007/s11625-006-0013-6 doi: 10.1007/s11625-006-0013-6
    [23] Koumparou D (2017) Circular economy and social sustainability. In: Proceedings of the Solid Waste Management & its Contribution to Circular Economy, Athens, Greece, 14–15.
    [24] Velenturf AP, Purnell P (2021) Principles for a sustainable circular economy. Sustain Prod Consum 27: 1437–1457. https://doi.org/10.1016/j.spc.2021.02.018
    [25] Camilleri MA (2020) European environment policy for the circular economy: Implications for business and industry stakeholders. Sustain Dev 28: 1804–1812. https://doi.org/10.1002/sd.2113 doi: 10.1002/sd.2113
    [26] Eckert E, Kovalevska O (2021) Sustainability in the European Union: Analyzing the discourse of the European green deal. J Risk Financ Manag 14: 80. https://doi.org/10.3390/jrfm14020080 doi: 10.3390/jrfm14020080
    [27] Kuci A, Fogarassy C (2021) European green deal policy for the circular economy opportunities and challenges. Hung Agric Eng 39: 65–73. https://doi.org/10.17676/HAE.2021.39.65 doi: 10.17676/HAE.2021.39.65
    [28] Riccaboni A, Neri E, Trovarelli F, et al. (2021) Sustainability-oriented research and innovation in 'farm to fork' value chains. Curr Opin Food Sci 42: 102–112. https://doi.org/10.1016/j.cofs.2021.04.006 doi: 10.1016/j.cofs.2021.04.006
    [29] Fiore M, Sauvée L, Wiśniewska-Paluszak J (2022) Opportunities and challenges of EU farm-to-fork strategy. Int Food Agribus Man Rev 25: 703–707. https://doi.org/10.22434/IFAMR2022.x001 doi: 10.22434/IFAMR2022.x001
    [30] Esposito B, Sessa MR, Sica D, et al. (2020) Towards circular economy in the agri-food sector. A systematic literature review. Sustainability 12: 7401. https://doi.org/10.3390/su12187401 doi: 10.3390/su12187401
    [31] European Parliament (2008) Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on waste and repealing certain Directives. European Parliament. Available from: https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri = CELEX: 02008L0098-20180705.
    [32] Chiaraluce G (2021) Circular economy in the agri-food sector: A policy overview. Ital Rev Agric Econ 76: 53–60. https://doi.org/10.36253/rea-13375 doi: 10.36253/rea-13375
    [33] Parfitt J, Barthel M, Macnaughton S (2010) Food waste within food supply chains: Quantification and potential for change to 2050. Phil Trans R Soc B 365: 3065–3081. https://doi.org/10.1098/rstb.2010.0126 doi: 10.1098/rstb.2010.0126
    [34] Alamar MDC, Falagán N, Aktas E, et al. (2018) Minimising food waste: A call for multidisciplinary research. J Sci Food Agr 98: 8–11. https://doi.org/10.1002/jsfa.8708 doi: 10.1002/jsfa.8708
    [35] Ioannou A, Georgali PZ, Fokaides PA (2022) Quantification of food waste in an insular island state for all stages of the food supply chain. Resour Conserv Recycl 185: 106486. https://doi.org/10.1016/j.resconrec.2022.106486 doi: 10.1016/j.resconrec.2022.106486
    [36] Ju M, Osako M, Harashina S (2017) Food loss rate in food supply chain using material flow analysis. Waste Manage 61: 443–454. https://doi.org/10.1016/j.wasman.2017.01.021 doi: 10.1016/j.wasman.2017.01.021
    [37] Caldeira C, De Laurentiis V, Corrado S, et al. (2019) Quantification of food waste per product group along the food supply chain in the European Union: A mass flow analysis. Resour Conserv Recycl 149: 479–488. https://doi.org/10.1016/j.resconrec.2019.06.011 doi: 10.1016/j.resconrec.2019.06.011
    [38] Amicarelli V, Bux C, Lagioia G (2020) How to measure food loss and waste? A material flow analysis application. Brit Food J 123: 67–85. https://doi.org/10.1108/BFJ-03-2020-0241 doi: 10.1108/BFJ-03-2020-0241
    [39] CREA (2022) L'agricoltura italiana conta. CREA. Available from: https://www.crea.gov.it/web/politiche-e-bioeconomia/-/agricoltura-italiana-conta.
    [40] Mirabella N, Castellani V, Sala S (2014) Current options for the valorization of food manufacturing waste: A review. J Cleaner Prod 65: 28–41. https://doi.org/10.1016/j.jclepro.2013.10.051 doi: 10.1016/j.jclepro.2013.10.051
    [41] Ncube A, Fiorentino G, Panfilo C, et al. (2022) Circular economy paths in the olive oil industry: A Life Cycle Assessment look into environmental performance and benefits. Int J Life Cycle Assess 2022: 1–21. https://doi.org/10.1007/s11367-022-02031-2 doi: 10.1007/s11367-022-02031-2
    [42] Ktori R, Kamaterou P, Zabaniotou A (2018) Spent coffee grounds valorization through pyrolysis for energy and materials production in the concept of circular economy. Mater Today-Proc 5: 27582–27588. https://doi.org/10.1016/j.matpr.2018.09.078 doi: 10.1016/j.matpr.2018.09.078
    [43] van Keulen M, Kirchherr J (2021) The implementation of the circular economy: Barriers and enablers in the coffee value chain J Cleaner Prod 281: 125033. https://doi.org/10.1016/j.jclepro.2020.125033 doi: 10.1016/j.jclepro.2020.125033
    [44] La Scalia G, Saeli M, Miglietta PP, et al. (2021) Coffee biowaste valorization within circular economy: An evaluation method of spent coffee grounds potentials for mortar production. Int J Life Cycle Assess 26: 1805–1815. https://doi.org/10.1007/s11367-021-01968-0 doi: 10.1007/s11367-021-01968-0
    [45] Mayson S, Williams ID (2021) Applying a circular economy approach to valorize spent coffee grounds. Resour Conserv Recycl 172: 105659. https://doi.org/10.1016/j.resconrec.2021.105659 doi: 10.1016/j.resconrec.2021.105659
    [46] Shrikhande AJ (2000) Wine by-products with health benefits. Food Res Int 33: 469–474. https://doi.org/10.1016/S0963-9969(00)00071-5 doi: 10.1016/S0963-9969(00)00071-5
    [47] Teixeira A, Baenas N, Dominguez-Perles R, et al. (2014) Natural bioactive compounds from winery by-products as health promoters: A review. Int J Mol Sci 15: 15638–15678. https://doi.org/10.3390/ijms150915638 doi: 10.3390/ijms150915638
    [48] Soto ML, Falqué E, Domínguez H (2015) Relevance of natural phenolics from grape and derivative products in the formulation of cosmetics. Cosmetics 2: 259–276. https://doi.org/10.3390/cosmetics2030259 doi: 10.3390/cosmetics2030259
    [49] Kalli E, Lappa I, Bouchagier P, et al. (2018) Novel application and industrial exploitation of winery by-products. Bioresour Bioprocess 5: 1–21. https://doi.org/10.1186/s40643-018-0232-6 doi: 10.1186/s40643-018-0232-6
    [50] Yin RK (2018) Case study research and applications—Design and Methods, 6 Eds., Thousand Oaks, CA: SAGE Publications Inc.
    [51] Noor KBM (2008) Case study: A strategic research methodology. Am J Appl Sci 5: 1602–1604. https://doi.org/10.3844/ajassp.2008.1602.1604 doi: 10.3844/ajassp.2008.1602.1604
    [52] European Commission (2019) Commission Delegated Decision (EU) 2019/1597 of 3 May 2019 supplementing Directive 2008/98/EC of the European Parliament and of the Council as regards a common methodology and minimum quality requirements for the uniform measurement of levels of food waste. European Commission. Available from: https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri = CELEX: 32019D1597.
    [53] Tisserant A, Pauliuk S, Merciai S, et al. (2017) Solid waste and the circular economy: A global analysis of waste treatment and waste footprints. J Ind Ecol 21: 628–640. https://doi.org/10.1111/jiec.12562 doi: 10.1111/jiec.12562
    [54] Morea D, Fortunati S, Cappa F, et al. (2023) Corporate social responsibility as a catalyst of circular economy? A case study perspective in Agri-food. J Knowl Manag 27: 1787–1809. https://doi.org/10.1108/JKM-06-2022-0451 doi: 10.1108/JKM-06-2022-0451
    [55] Berardi PC, Betiol LS, Dias JM (2021) From the vine to the bottle: How circular is the wine sector? A glance over waste. In: Mor RS, Panghal A, Kumar V (Eds.), Challenges and Opportunities of Circular Economy in Agri-Food Sector: Rethinking Waste, Springer, 151–175. https://doi.org/10.1007/978-981-16-3791-9_9
    [56] MIPAAF (2008) Decreto n. 5396 del 27 novembre 2008 Disposizioni di attuazione dei regolamenti CE) n. 479/2008 del Consiglio e (CE) n.555/2008 della Commissione per quanto riguarda l'applicazione della misura della distillazione dei sottoprodotti della vinificazione. Ministero delle Politiche Agricole, Ambientali e Forestali. Available from: https://www.gazzettaufficiale.it/atto/serie_generale/caricaDettaglioAtto/originario?atto.dataPubblicazioneGazzetta = 2008-12-27 & atto.codiceRedazionale = 08A09953 & elenco30giorni = false.
    [57] Presidenza della Repubblica Italiana (1996) Legge 11 novembre 1996, n. 574. Nuove norme in materia di utilizzazione agronomica delle acque di vegetazione e di scarichi dei frantoi oleari. Available from: https://www.gazzettaufficiale.it/atto/serie_generale/caricaDettaglioAtto/originario?atto.dataPubblicazioneGazzetta = 1996-11-12 & atto.codiceRedazionale = 096G0597 & elenco30giorni = false.
    [58] MIPAAF (2005) Decreto 6 luglio 2005 Criteri e norme tecniche generali per la disciplina regionale dell'utilizzazione agronomica delle acque di vegetazione e degli scarichi dei frantoi oleari, di cui all'articolo 38 del decreto legislativo 11 maggio 1999, n. 152. Ministero delle Politiche Agricole, Ambientali e Forestali. Available from: https://www.gazzettaufficiale.it/eli/id/2005/07/19/05A07191/sg.
    [59] Heimerl F, Lohmann S, Lange S, et al. (2014) Word cloud explorer: Text analytics based on word clouds. In: 2014 47th Hawaii international conference on system sciences, IEEE, 1833–1842. https://doi.org/10.1109/HICSS.2014.231
    [60] Nerantzis ET, Tataridis P (2006) Integrated enology-utilization of winery by-products into high added value products. J Sci Tech 1: 79–89.
    [61] Berbel J, Posadillo A (2018) Review and analysis of alternatives for the valorisation of agro-industrial olive oil by-products. Sustainability 10: 237. https://doi.org/10.3390/su10010237 doi: 10.3390/su10010237
    [62] Principato L, Ruini L, Guidi M, et al. (2019) Adopting the circular economy approach on food loss and waste: The case of Italian pasta production. Resour Conserv Recycl 144: 82–89. https://doi.org/10.1016/j.resconrec.2019.01.025 doi: 10.1016/j.resconrec.2019.01.025
    [63] Wen L, Álvarez C, Zhang Z, et al. (2021) Optimisation and characterisation of protein extraction from coffee silverskin assisted by ultrasound or microwave techniques. Biomass Convers Bioref 11: 1575–1585. https://doi.org/10.1007/s13399-020-00712-2 doi: 10.1007/s13399-020-00712-2
    [64] Garrone P, Melacini M, Perego A, et al. (2016) Reducing food waste in food manufacturing companies. J Cleaner Prod 137: 1076–1085. https://doi.org/10.1016/j.jclepro.2016.07.145 doi: 10.1016/j.jclepro.2016.07.145
    [65] FAO (2011) Global food losses and food waste—Extent, causes and prevention. Rome. Available from: https://www.fao.org/3/i2697e/i2697e.pdf.
    [66] Bentivoglio D, Chiaraluce G, Finco A (2022) Economic assessment for vegetable waste valorization through the biogas-biomethane chain in Italy with a circular economy approach. Front Sustain Food Syst 6: 1035357. https://doi.org/10.3389/fsufs.2022.1035357 doi: 10.3389/fsufs.2022.1035357
    [67] Maranesi C, De Giovanni P (2020) Modern circular economy: Corporate strategy, supply chain, and industrial symbiosis. Sustainability 12: 9383. https://doi.org/10.3390/su12229383 doi: 10.3390/su12229383
    [68] Zarbà C, Chinnici G, La Via G, et al. (2021) Regulatory elements on the circular economy: Driving into the agri-food system. Sustainability 13: 8350. https://doi.org/10.3390/su13158350 doi: 10.3390/su13158350
    [69] Mhatre P, Panchal R, Singh A, et al. (2021) A systematic literature review on the circular economy initiatives in the European Union. Sustain Prod Consum 26: 187–202. https://doi.org/10.1016/j.spc.2020.09.008 doi: 10.1016/j.spc.2020.09.008
    [70] Morone P, Koutinas A, Gathergood N, et al. (2019) Food waste: Challenges and opportunities for enhancing the emerging bio-economy. J Cleaner Prod 221: 10–16. https://doi.org/10.1016/j.jclepro.2019.02.258 doi: 10.1016/j.jclepro.2019.02.258
    [71] Osorio LLDR, Flórez-López E, Grande-Tovar CD (2021) The potential of selected agri-food loss and waste to contribute to a circular economy: Applications in the food, cosmetic and pharmaceutical industries. Molecules 26: 515. https://doi.org/10.3390/molecules26020515 doi: 10.3390/molecules26020515
    [72] Rizos V, Behrens A, Kafyeke T, et al. (2015) The circular economy: barriers and opportunities for SMEs. CEPS Working Documents 412.
    [73] Ormazabal M, Prieto-Sandoval V, Puga-Leal R, et al. (2018) Circular economy in Spanish SMEs: Challenges and opportunities. J Cleaner Prod 185: 157–167. https://doi.org/10.1016/j.jclepro.2018.03.031 doi: 10.1016/j.jclepro.2018.03.031
    [74] Mehmood A, Ahmed S, Viza E, et al. (2021) Drivers and barriers towards circular economy in agri‐food supply chain: A review. Bus Strat Dev 4: 465–481. https://doi.org/10.1002/bsd2.171 doi: 10.1002/bsd2.171
    [75] Korhonen J, Honkasalo A, Seppälä J (2018) Circular economy: The concept and its limitations. Ecol Econ 143: 37–46. https://doi.org/10.1016/j.ecolecon.2017.06.041 doi: 10.1016/j.ecolecon.2017.06.041
    [76] Muscio A, Sisto R (2020) Are agri-food systems really switching to a circular economy model? Implications for European research and innovation policy. Sustainability 12: 5554. https://doi.org/10.3390/su12145554 doi: 10.3390/su12145554
    [77] Geissdoerfer M, Savaget P, Bocken NM, et al. (2017) The Circular Economy–A new sustainability paradigm?. J Cleaner Prod 143: 757–768. https://doi.org/10.1016/j.jclepro.2016.12.048 doi: 10.1016/j.jclepro.2016.12.048
    [78] Campos DA, Gómez-García R, Vilas-Boas AA, et al. (2020) Management of fruit industrial by-products—A case study on circular economy approach. Molecules 25: 320. https://doi.org/10.3390/molecules25020320 doi: 10.3390/molecules25020320
    [79] Chiaraluce G, Bentivoglio D, Finco A (2021) Circular economy for a sustainable agri-food supply chain: A review for current trends and future pathways. Sustainability 13: 9294. https://doi.org/10.3390/su13169294 doi: 10.3390/su13169294
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    5. Damilola T Aladesuru, Lukas Cechura, Sebastian Neuenfeldt, Till Kuhn, Zuzana Smeets Kristkova, Zdeňka Žáková Kroupová, Tomas Ratinger, Alexander Gocht, Marc Müller, Hugo Storm, Impacts of agricultural production decisions on the safe and just operating space: A systematic literature review, 2024, 2633-9048, 10.1093/qopen/qoae027
    6. Shivani Garg, Nelson Pynadathu Rumjit, Pooja Arora, Addressing climate change impacts through sustainable agricultural solutions: a review, 2024, 1573-2975, 10.1007/s10668-024-05728-6
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