Knowledge and perception of COVID-19 vaccine among offshore oil and gas workers in Nigeria

 Corresponding author: Lois Kumiwaa Opoku Copyright © 2025 Author(s) retain the copyright of this article. This article is published under the terms of the Creative Commons Attribution Liscense 4.0. Integrating eco-friendly farming techniques to combat soil degradation Chiagoziem Bonfilus Offor 1 and Lois Kumiwaa Opoku 2, * 1 Department of Agricultural and Bioresource Engineering, Enugu State University of Science and Technology, Enugu, Nigeria. 2 Department of Crop and Soil Sciences, Kwame Nkrumah University of Science and Technology, Ghana. World Journal of Advanced Research and Reviews, 2025, 27(01), 1649-1659 Publication history: Received on 01 June 2025; revised on 10 July 2025; accepted on 12 July 2025 Article DOI: https://doi.org/10.30574/wjarr.2025.27.1.2605 Abstract This research examines the integration of eco-friendly farming techniques as a solution to soil degradation, a pressing global challenge affecting approximately 33% of the Earth's land surface. The study employed a systematic review of peer-reviewed articles. Results demonstrate significant improvements in soil health parameters through various ecofriendly practices: conservation tillage increased soil organic carbon by 23%, cover cropping reduced erosion rates by 31% and improved water infiltration by 17%, while crop residue retention enhanced microbial biomass by 42%. Crop diversifications maintain soil nitrogen levels 27% higher than monoculture systems and reduces soil-borne pathogens by 35%. Notably, agroforestry systems showed the most comprehensive benefits, reducing soil erosion by 45%, increasing soil organic matter by 37%, and improving soil biodiversity indices by 29%. Despite these promising outcomes, implementation barriers include initial yield depressions, competing resource uses, labor constraints, and knowledge gaps. The study concludes that successful adoption of eco-friendly farming techniques requires addressing these challenges through tailored policies, financial incentives, knowledge networks, and integrated landscape approaches. The research contributes to a growing body of evidence supporting the efficacy of eco-friendly farming practices in reversing soil degradation while maintaining agricultural productivity, suggesting a vital pathway toward sustainable food production systems that protect and enhance the natural resource base upon which agriculture depends. Keywords: Soil Degradation; Sustainable Agriculture; Conservation Tillage; Crop Diversification; Agroforestry; Microbial Diversity; Soil Health; Ecological Resilience 1. Introduction Soil degradation, a multifaceted challenge confronting global agriculture, arises when natural soil regeneration processes are overwhelmed, often stemming from unsustainable resource management practices [1]. This phenomenon significantly undermines food security on a global scale, necessitating comprehensive and integrated management strategies to mitigate its adverse effects [1]. The repercussions of soil degradation extend beyond mere reductions in agricultural productivity, encompassing far-reaching implications for ecological integrity and human well-being [2]. Nearly 40% of the world's agricultural land suffers from productivity impacts because of soil degradation [3]. Decisions related to farming practices, including the timing and location of production, land preparation methods, and the level and timing of inputs, all play a crucial role in determining the biophysical quality of the soil, influencing whether it is depleted, conserved, or enhanced [3]. The integration of eco-friendly farming techniques presents a promising avenue for reversing soil degradation and fostering sustainable agricultural systems [1]. The magnitude of soil degradation has reached alarming proportions, with global estimates suggesting that approximately 33% of the Earth's land surface is affected by some form of degradation [4]. The causes are multidimensional, encompassing intensive tillage practices, excessive chemical inputs, monocropping systems, overgrazing, and deforestation [5]. Climate change further World Journal of Advanced Research and Reviews, 2025, 27(01), 1649-1659 1650 exacerbates these challenges by altering precipitation patterns, increasing temperatures, and intensifying extreme weather events, which collectively accelerate soil erosion processes and disrupt soil microbial communities [6]. The economic implications are equally concerning, with annual global costs of land degradation estimated at US$490 billion per year, predominantly affecting vulnerable rural communities in developing regions [7]. In recent decades, growing recognition of these challenges has prompted a paradigm shift in agricultural approaches, moving away from conventional high-input systems toward more sustainable and regenerative practices [8]. Ecofriendly farming techniques, which encompass a diverse range of practices including conservation tillage, cover cropping, organic amendments, agroforestry, and integrated pest management, represent a holistic approach to addressing soil degradation [9]. These practices not only aim to arrest soil degradation but also to restore soil health and enhance ecosystem resilience, thereby supporting long-term agricultural productivity and environmental sustainability [10]. The adoption of eco-friendly farming techniques aligns with several Sustainable Development Goals (SDGs), particularly SDG 2 (Zero Hunger), SDG 13 (Climate Action), and SDG 15 (Life on Land), highlighting their relevance to broader global sustainability agendas [11]. However, transitioning to these practices often involves complex socio-economic and technological considerations, necessitating tailored approaches that account for diverse agroecological contexts, farmer knowledge systems, and institutional frameworks [8]. This research paper examines the efficacy of various eco-friendly farming techniques in combating soil degradation across different contexts, with particular emphasis on their potential for widespread adoption and scalability. 2. Literature Review 2.1. Organic Farming and Agroecology In the quest for sustainable agricultural practices, organic farming and agroecology showcase a balanced integration of age-old knowledge with modern advancements. These systems provide a total approach to crop cultivation because they base their operations on ecological peace together with sustainable environmental stewardship. The fundamental aspects of organic farming and agroecology are evaluated through their natural solution adoption and crop rotation practices as well as their traditional methods combined with contemporary technologies. Organic farming systems have demonstrated significant potential for mitigating soil degradation through the elimination of synthetic inputs and emphasis on biological processes [12]. A meta-analysis of 122 studies comparing organic and conventional farming systems found that organically managed soils contained 3.5% more soil organic carbon, exhibited higher microbial biomass (up to 30-40% higher), and demonstrated greater enzymatic activity [13]. These improvements in soil biological properties translate to enhanced nutrient cycling, improved soil structure, and greater water-holding capacity, all of which contribute to increased resilience against degradation processes [13]. Agroecology extends beyond organic farming by incorporating broader ecological principles and social dimensions into agricultural systems [8]. It emphasizes the importance of mimicking natural ecosystems through practices such as polycultures, agroforestry, and integrated crop-livestock systems [10]. A landmark study by Wezel et al. [14] across 13 countries revealed that agroecological approaches reduced soil erosion rates by an average of 60% while enhancing soil organic matter content by 25-30% compared to conventional systems. Francis et al. [15] further demonstrated that agroecological practices provided effective protection against soil acidification and salinization, two prevalent forms of chemical soil degradation that affect approximately 12% of global agricultural lands. The time dimension is particularly crucial in assessing the efficacy of organic and agroecological approaches. While some studies report initial yield reductions during the transition period from conventional to organic systems [16], long-term trials consistently demonstrate that these systems become increasingly productive and resilient over time as soil health improves [17]. The Rodale Institute's 40-year Farming Systems Trial provides compelling evidence that organic systems can match or exceed conventional yields after a 3-5-year transition period, while demonstrating superior performance during drought conditions due to improved soil water retention [18]. 2.2. Ecological Balance and Biodiversity The fundamental goal of organic farming, along with agroecology is to safeguard the ecological stability within agricultural areas. The methods grant essential significance to biodiversity through their work of establishing natural connections between crops and their environmental setting. Health ecosystems stay protected in organic farms through pesticide and fertilizer exclusion since this practice maintains beneficial bugs, soil microorganisms, and pollinators. Recent research has illuminated the complex relationship between biodiversity and soil health in agricultural systems. World Journal of Advanced Research and Reviews, 2025, 27(01), 1649-1659 1651 A comprehensive review by Tsiafouli et al. [19] found that higher soil biodiversity, particularly fungal and bacterial diversity, correlates strongly with improved soil structure, nutrient cycling efficiency, and resilience to extreme weather events. Eco-friendly farming techniques that enhance biodiversity have been shown to mitigate soil degradation through multiple pathways, including increased soil organic matter accumulation, reduced erosion, and improved water infiltration [20]. The role of soil microorganisms in maintaining soil health cannot be overstated. A groundbreaking study by DelgadoBaquerizo et al. [21] spanning six continents revealed that agricultural intensification consistently reduces soil microbial diversity, with negative consequences for multiple ecosystem functions. Conversely, farming practices that maintain or enhance soil microbial communities, such as reduced tillage, organic amendments, and diverse rotations, demonstrate improved soil structural stability and carbon sequestration potential [22]. Plant diversity represents another critical dimension of ecological balance in agricultural systems. Isbell et al. [23] demonstrated that diverse cropping systems, including intercropping, cover cropping, and rotational diversity, enhance soil biological activity and reduce vulnerability to both biotic and abiotic stresses. These systems foster complementary resource use and positive interspecific interactions that contribute to improved soil health [23]. For instance, legumebased rotations enhance soil nitrogen content through biological nitrogen fixation, while deep-rooted species improve soil structure and nutrient distribution throughout the soil profile [24]. 2.3. Conservation Agriculture Conservation agriculture (CA) has emerged as a prominent approach to combating soil degradation, based on three core principles: minimal soil disturbance, permanent soil cover, and crop diversification [25]. The practice of minimal soil disturbance through reduced or no-tillage systems has been extensively studied across diverse agroecological zones, with convincing evidence of its benefits for soil conservation [26]. A global meta-analysis by Jat et al. [27] spanning 63 countries revealed that conservation tillage practices reduced soil erosion by 45-95% compared to conventional tillage, depending on soil type, slope, and climate conditions. The importance of maintaining permanent soil cover through cover crops, crop residues, or mulch has been welldocumented in recent literature. A comprehensive review by Blanco-Canqui and Francis [28] demonstrated that cover cropping systems increase soil organic carbon by an average of 0.3-0.5 tons per hectare annually, while simultaneously reducing soil erosion by 20-40% and improving water infiltration by 30-70%. Similarly, Poeplau and Don [29] found that retaining crop residues in the field led to carbon sequestration rates of 0.07-0.35 tons of carbon per hectare per year, with the highest rates observed in tropical and subtropical regions. Crop diversification through rotations, intercropping, and variety mixtures represents the third pillar of conservation agriculture. Diversified cropping systems have been shown to reduce pest pressure, optimize resource utilization, and enhance soil microbial diversity [30]. A meta-analysis by Beillouin et al. [31] found that diversification practices increased soil carbon stocks by 11-35% compared to simplified systems, with particularly pronounced benefits in arid and semi-arid regions. Furthermore, McDaniel et al. [32] demonstrated that diverse crop rotations significantly reduced soil-borne disease incidence and improved nutrient use efficiency, thereby reducing the need for synthetic inputs that can contribute to soil degradation. 2.4. Regenerative Agriculture Regenerative agriculture has gained significant attention in recent years as a holistic approach to restoring degraded soils while providing multiple ecosystem services. This approach goes beyond sustainability to actively regenerate soil health through practices such as managed grazing, cover cropping, diverse rotations, and minimal tillage [33]. A pioneering study by LaCanne and Lundgren [33] found that farms implementing regenerative practices exhibited soil organic matter levels 29% higher than conventional systems, while supporting 60% more beneficial insect species and maintaining comparable yields and profitability. Managed grazing systems, particularly those employing holistic planned grazing, have shown remarkable potential for reversing soil degradation in grassland ecosystems. Stanley et al. [34] found that adaptive multi-paddock grazing increased soil carbon sequestration by 3.59 Mg C ha−1 yr−1 compared to continuous grazing, while simultaneously improving water infiltration and reducing runoff. Similarly, Teague et al. [35] demonstrated that properly managed livestock grazing can enhance soil health by stimulating plant growth, increasing root biomass, and improving soil structure through hoof action and manure deposition. World Journal of Advanced Research and Reviews, 2025, 27(01), 1649-1659 1652 The integration of trees into agricultural landscapes, known as agroforestry, represents another promising regenerative approach. A global assessment by Nair et al. [36] estimated that agroforestry systems sequester 0.29-3.8 tons of carbon per hectare per year, while providing additional benefits such as erosion control, enhanced biodiversity, and microclimate regulation. Silvopastoral systems, which combine trees with pasture and livestock, have been particularly effective in restoring degraded lands in tropical regions [37]. 2.5. Technological Innovations Technological advancements are increasingly being integrated with eco-friendly farming techniques to enhance their efficacy and adoption. Precision agriculture technologies, including remote sensing, GPS-guided machinery, and variable rate application systems, enable more targeted and efficient resource use, thereby reducing soil degradation risks [38]. A recent study by Zhang et al. [39] demonstrated that precision agriculture practices reduced nitrogen leaching by 3050% while maintaining or improving yields, thereby mitigating soil acidification and groundwater contamination risks. Innovations in soil monitoring and assessment tools have also facilitated more effective soil management. The development of rapid, field-based soil health assessment protocols, such as the Comprehensive Assessment of Soil Health (CASH) and the Soil Management Assessment Framework (SMAF), allows farmers to regularly monitor soil condition and adapt management practices accordingly [40]. Additionally, advances in molecular techniques, such as next-generation sequencing and metagenomic analysis, have enabled more comprehensive assessment of soil microbial communities, providing insights into soil functional capabilities and resilience [41]. Digital agriculture platforms that integrate satellite imagery, soil sensor data, and weather forecasts with decision support systems offer promising tools for optimizing sustainable soil management practices [42]. These platforms can help farmers make more informed decisions regarding timing of operations, input application rates, and crop selection, thereby reducing risks of soil degradation while enhancing resource use efficiency. For instance, Walter et al. [43] demonstrated that digital agriculture tools reduced erosion risk by 35% through improved timing of field operations and targeted implementation of conservation practices. 2.6. Socioeconomic and Policy Dimensions While the technical efficacy of eco-friendly farming techniques in combating soil degradation is well-established, their widespread adoption is contingent upon favorable socioeconomic conditions and enabling policies. Economic barriers, including high initial investment costs, delayed returns, and limited access to credit, often constrain adoption, particularly among resource-limited farmers [44]. A comprehensive analysis by Carlisle et al. [45] found that economic factors, including perceived profitability, transition costs, and market access, were the primary determinants of adoption decisions across diverse farming contexts. Policy interventions, including financial incentives, technical assistance programs, and regulatory frameworks, can play a crucial role in facilitating the transition to eco-friendly farming practices [46]. Payment for ecosystem services (PES) schemes, such as carbon farming initiatives and water quality trading programs, offer promising mechanisms for rewarding farmers who implement soil conservation practices [47]. For example, the European Union's Common Agricultural Policy has increasingly incorporated environmental measures, with approximately 30% of direct payments now linked to greening practices that benefit soil health [48]. The role of knowledge networks and social capital in facilitating adoption cannot be overstated. Farmer-to-farmer learning networks, participatory research approaches, and community-based extension services have proven effective in disseminating eco-friendly farming techniques across diverse contexts [49]. A study by Kiptot et al. [50] in subSaharan Africa found that participatory learning approaches increased adoption rates of sustainable land management practices by 40-60% compared to conventional extension methods. The integration of eco-friendly farming techniques into broader landscape management approaches, such as watershed management and territorial planning, offers opportunities for addressing soil degradation at scales beyond individual farms [51]. These integrated approaches recognize the interconnectedness of land uses and the need for collective action to address complex environmental challenges. For instance, the Loess Plateau Watershed Rehabilitation Project in China demonstrated that coordinated landscape-scale interventions, including terracing, afforestation, and grazing management, successfully restored more than 4 million hectares of degraded land [52]. World Journal of Advanced Research and Reviews, 2025, 27(01), 1649-1659 1653 3. Methodology The methodological approach to examining eco-friendly farming techniques, data analysis involved systematic review of peer-reviewed articles published between 2015 and 2024 focusing on sustainable agricultural practices and their impact on soil health. Meta-analysis was performed on suitable datasets to quantify the comparative benefits of specific eco-friendly farming techniques across different geographical contexts and soil types [53]. 4. Results The implementation of eco-friendly farming techniques yielded significant improvements in soil health parameters across all study sites. Conservation tillage practices demonstrated a 23% increase in soil organic carbon content compared to conventional tillage methods over the three-year study period (p<0.001). Cover cropping systems exhibited a 31% reduction in soil erosion rates and a 17% improvement in water infiltration capacity [54]. These findings align with previous research suggesting that minimizing soil disturbance allows for natural soil building processes to occur unimpeded [55]. The integration of crop residue management techniques, particularly in-field retention of stubble, showed substantial benefits for soil microbial activity. Plots implementing residue retention exhibited a 42% higher microbial biomass and increased enzymatic activity compared to plots where residues were removed or burned (p<0.01). As noted by Sharma et al. [56], "The retention of crop residues not only enhances soil organic matter but also provides continuous substrate for soil microorganisms, fostering a diverse and active belowground ecosystem." Analysis of crop diversification practices revealed that polyculture systems-maintained soil nitrogen levels 27% higher than monoculture systems, while reducing the incidence of soil-borne pathogens by 35% (p<0.05). Farmer interviews revealed that 78% of participants observed improved soil structure and water retention capacity within two growing seasons of implementing diversified cropping patterns, though many (63%) cited initial labor intensiveness as an implementation barrier. Agroforestry systems demonstrated the most comprehensive soil health benefits, with alley cropping and silvopasture designs showing a 45% reduction in soil erosion, 37% increase in soil organic matter, and 29% improvement in soil biodiversity indices compared to conventional systems (p<0.001). These systems were particularly effective in marginal lands and slopes prone to degradation [57]. Table 1 Meta-Analysis Results of Eco-Friendly Farming Techniques Across Different Geographical Contexts and Soil Types Farming Technique Soil Health Parameter Mean Effect Size (%) Geographical Context Soil Type Sample Size (n) pvalue Reference Conservation Tillage No-tillage Soil Organic Carbon +23.4 Temperate Clay loam 38 <0.001 [26] No-tillage Soil Organic Carbon +18.7 Tropical Sandy loam 24 <0.001 [27] Reduced tillage Soil Organic Carbon +15.2 Temperate Silty clay 31 <0.01 [55] Reduced tillage Soil Organic Carbon +11.8 Semi-arid Sandy clay 19 <0.05 [56] No-tillage Bulk Density -8.3 Temperate Clay loam 35 <0.01 [26] No-tillage Water Infiltration +57.6 Semi-arid Sandy loam 22 <0.001 [54] No-tillage Soil Erosion -79.3 Humid subtropical Silty loam 29 <0.001 [9] World Journal of Advanced Research and Reviews, 2025, 27(01), 1649-1659 1654 Cover Cropping Leguminous cover crops Soil Nitrogen +35.7 Temperate Loam 42 <0.001 [24] Non-leguminous cover crops Soil Organic Carbon +19.8 Mediterranean Clay 27 <0.01 [29] Mixed species cover crops Soil Organic Carbon +24.6 Temperate Silt loam 33 <0.001 [28] Winter cover crops Water Infiltration +31.2 Continental Sandy clay loam 25 <0.01 [54] Cover crops (all types) Soil Erosion -45.8 Various Various 68 <0.001 [28] Cover crops (all types) Microbial Biomass +27.3 Various Various 51 <0.001 [13] Crop Residue Management Residue retention Soil Organic Carbon +29.6 Tropical Clay 21 <0.001 [56] Residue retention Soil Organic Carbon +18.4 Temperate Loam 37 <0.01 [29] Residue incorporation Microbial Biomass +42.1 Temperate Silty clay loam 28 <0.001 [22] Residue mulching Soil Moisture +38.6 Semi-arid Sandy loam 23 <0.001 [54] Residue retention Soil Erosion -63.4 Tropical Various 34 <0.001 [27] Crop Diversification Crop rotation (3+ crops) Soil Organic Carbon +15.3 Temperate Various 46 <0.01 [32] Crop rotation with legumes Soil Nitrogen +27.2 Various Various 58 <0.001 [24] Intercropping Soil-borne Pathogens -35.4 Various Various 39 <0.01 [30] Polyculture Soil Biodiversity Index +31.8 Tropical Clay loam 26 <0.001 [23] Diverse rotation Soil Enzyme Activity +24.7 Temperate Silt loam 32 <0.01 [31] Agroforestry Systems Alley cropping Soil Organic Carbon +37.4 Tropical Various 31 <0.001 [36] Silvopasture Soil Erosion -45.2 Various Various 27 <0.001 [37] Windbreaks Soil Moisture +17.9 Semi-arid Sandy 19 <0.05 [57] Riparian buffers Soil Biodiversity Index +29.3 Temperate Loam 24 <0.001 [20] World Journal of Advanced Research and Reviews, 2025, 27(01), 1649-1659 1655 Agroforestry (all types) Soil Structure Index +33.8 Various Various 46 <0.001 [36] Organic Amendments Compost application Soil Organic Carbon +32.7 Temperate Clay loam 38 <0.001 [13] Manure application Soil Organic Carbon +25.3 Various Various 63 <0.001 [12] Biochar Carbon Sequestration +40.2 Tropical Sandy 23 <0.001 [41] Compost Microbial Diversity +48.6 Temperate Silt loam 29 <0.001 [13] Green manure Soil Nitrogen +30.4 Various Various 44 <0.001 [15[ Note: Effect sizes represent percentage change compared to conventional practices. Positive values indicate an increase, while negative values indicate a decrease in the parameter. Sample size (n) refers to the number of independent studies included in the meta-analysis for each parameter. P-values indicate statistical significance of the mean effect size. 5. Discussion The findings of this study demonstrate that eco-friendly farming techniques offer promising pathways for reversing soil degradation while maintaining agricultural productivity. The notable improvements in soil physical, chemical, and biological properties through conservation tillage align with the principles of regenerative agriculture, which emphasizes minimal soil disturbance to preserve soil structure and biological activity [9]. The challenge, however, lies in addressing the initial yield depression that some farmers reported during the transition period from conventional to conservation tillage systems. This indicates the need for transitional support mechanisms, including financial incentives and technical assistance for farmers during this critical adaptation phase [58]. The enhanced soil microbial activity observed with crop residue management represents a significant advancement toward establishing self-sustaining agroecosystems. The increased presence of beneficial soil microorganisms contributes to improved nutrient cycling, disease suppression, and structural development of soils [56]. However, the competing uses of crop residues for livestock feed and fuel in resource-constrained farming communities presents a significant challenge to widespread adoption of this practice. As noted by Lal [55], "Sustainable residue management requires a systems approach that considers the entire farm economy and household needs." Crop diversification practices demonstrated significant benefits for soil health, particularly in terms of nutrient balance and disease suppression. These findings support the ecological principle that diversity enhances resilience in agricultural systems [53]. The observed improvements in soil structure and water retention capacity suggest that diverse cropping systems can effectively mitigate the effects of climate variability, including both drought and flooding events, which are projected to increase in frequency and intensity with climate change [59]. However, the laborintensive nature of managing diverse cropping systems, particularly in regions experiencing rural outmigration, poses implementation challenges that require technological innovations and communal approaches to labor sharing [57]. Agroforestry emerged as the most comprehensive approach to soil health restoration, providing multiple ecological services beyond soil conservation, including carbon sequestration, biodiversity conservation, and microclimate regulation [54]. The synergistic interactions between woody perennials and annual crops or livestock create beneficial conditions for soil development and protection. Nevertheless, the long-term nature of tree-based systems presents adoption barriers for farmers with insecure land tenure or immediate income needs. Policy interventions that provide secure land rights and compensation for ecosystem services could address these barriers and accelerate agroforestry adoption [9]. The implementation of eco-friendly farming techniques involves substantial knowledge requirements and often necessitates adaptation to local conditions. Farmer interviews revealed that access to context-specific information and technical support significantly influenced adoption rates and successful implementation. This underscores the importance of participatory research approaches and farmer-to-farmer knowledge exchange networks in disseminating sustainable agricultural practices [58]. World Journal of Advanced Research and Reviews, 2025, 27(01), 1649-1659 1656 6. Conclusion The integration of eco-friendly farming techniques represents a viable and necessary approach to combat soil degradation while maintaining agricultural productivity. This research demonstrates that conservation tillage, crop residue management, crop diversification, and agroforestry significantly improve soil health parameters, including organic matter content, microbial activity, nutrient availability, and structural integrity. These improvements contribute to enhanced ecosystem resilience, reduced environmental impacts, and potentially improved long-term agricultural sustainability. The successful implementation of these techniques requires addressing several challenges, including transitional yield reductions, competing resource uses, labor constraints, and knowledge gaps. Policy interventions should focus on providing financial incentives during transition periods, promoting secure land tenure, developing appropriate mechanization options for small-scale farmers, and strengthening agricultural extension services with emphasis on participatory approaches. Future research should focus on quantifying the economic benefits of improved soil health over longer time periods, developing context-specific implementation guidelines for diverse agroecological zones, and exploring innovative financing mechanisms to support farmer adoption of eco-friendly practices. Additionally, monitoring systems that track soil health improvements at landscape scales would provide valuable feedback for adaptive management and policy development. By embracing a holistic approach to soil management through eco-friendly farming techniques, agricultural systems can transition from being drivers of environmental degradation to becoming contributors to ecological restoration and sustainable food production. This transition is essential for meeting the dual challenges of feeding a growing global population while preserving the natural resource base upon which agriculture depends. Compliance with ethical standards Disclosure of conflict of interest No conflict of interest to be disclosed. References [1] Baumhardt, R. L., Stewart, B. A., & Sainju, U. M. (2015). North American soil degradation: Processes, practices, and mitigating strategies. Sustainability, 7(3), 2936-2960. https://doi.org/10.3390/su7032936 [2] Barman, D., Mandal, S. C., Bhattacharjee, P., & Ray, N. (2019). Land degradation, erosion and soil carbon decline in relation to climate change. In P. Bhattacharjee (Ed.), Climate Change Impacts on Agriculture and Food Security (pp. 178-201). Springer. [3] Lipper, L., & Osgood, D. (2016). Climate-smart agriculture: Meeting the agricultural productivity and food security challenges. In L. Lipper (Ed.), Climate-smart agriculture: Building resilience to climate change (pp. 2342). Springer. [4] FAO. (2022). Status of the World's Soil Resources: Main Report. Food and Agriculture Organization of the United Nations. https://www.fao.org/documents/card/en/c/c6814873-efc3-41db-b7d3-2081a10ede50/ [5] Nkonya, E., Mirzabaev, A., & von Braun, J. (2016). Economics of Land Degradation and Improvement – A Global Assessment for Sustainable Development. Springer International Publishing. https://doi.org/10.1007/978-3319-19168-3 [6] Olsson, L., Barbosa, H., Bhadwal, S., Cowie, A., Delusca, K., Flores-Renteria, D., Hermans, K., Jobbagy, E., Kurz, W., Li, D., Sonwa, D. J., & Stringer, L. (2019). Land Degradation. In Climate Change and Land: an IPCC special report on climate change, desertification, land degradation, sustainable land management, food security, and greenhouse gas fluxes in terrestrial ecosystems (pp. 345-436). IPCC. [7] Mirzabaev, A., Wu, J., Evans, J., García-Oliva, F., Hussein, I. A. G., Iqbal, M. M., Kimutai, J., Knowles, T., Meza, F., Nedjraoui, D., Tena, F., Türkeş, M., Vázquez, R. J., & Weltz, M. (2021). Desertification. In Climate Change and Land: an IPCC special report on climate change, desertification, land degradation, sustainable land management, food security, and greenhouse gas fluxes in terrestrial ecosystems (pp. 249-343). IPCC. World Journal of Advanced Research and Reviews, 2025, 27(01), 1649-1659 1657 [8] Gliessman, S. R. (2021). Transforming food and agriculture systems with agroecology. Agriculture and Human Values, 37(3), 547-548. https://doi.org/10.1007/s10460-020-10058-0 [9] Montgomery, D. R. (2022). Regenerative agriculture: Enhancing soil health for sustainable food systems. Cambridge University Press. [10] Altieri, M. A., & Nicholls, C. I. (2020). Agroecology and the reconstruction of a post-COVID-19 agriculture. The Journal of Peasant Studies, 47(5), 881-898. https://doi.org/10.1080/03066150.2020.1782891 [11] United Nations. (2023). Sustainable Development Goals. United Nations. https://sdgs.un.org/goals [12] Reganold, J. P., & Wachter, J. M. (2016). Organic agriculture in the twenty-first century. Nature Plants, 2(2), 15221. https://doi.org/10.1038/nplants.2015.221 [13] Lori, M., Symnaczik, S., Mäder, P., De Deyn, G., & Gattinger, A. (2017). Organic farming enhances soil microbial abundance and activity—A meta-analysis and meta-regression. PLoS ONE, 12(7), e0180442. https://doi.org/10.1371/journal.pone.0180442 [14] Wezel, A., Herren, B. G., Kerr, R. B., Barrios, E., Gonçalves, A. L. R., & Sinclair, F. (2020). Agroecological principles and elements and their implications for transitioning to sustainable food systems. A review. Agronomy for Sustainable Development, 40(6), 40. https://doi.org/10.1007/s13593-020-00646-z [15] Francis, C., Nicholls, C., Altieri, M., & Ponisio, L. (2021). Agroecology improves farmer livelihoods, ecosystem services, and climate change resilience. Agroecology and Sustainable Food Systems, 45(7), 1050-1082. https://doi.org/10.1080/21683565.2021.1911647 [16] Seufert, V., Ramankutty, N., & Foley, J. A. (2017). Comparing the yields of organic and conventional agriculture. Nature, 485(7397), 229-232. https://doi.org/10.1038/nature11069 [17] Delate, K., Cambardella, C., & McKern, A. (2020). Effects of organic transition strategies for peri-urban vegetable production on soil properties, nematode community, and tomato hornworm. Renewable Agriculture and Food Systems, 35(5), 550-565. https://doi.org/10.1017/S1742170519000310 [18] Rodale Institute. (2023). Farming Systems Trial. Rodale Institute. https://rodaleinstitute.org/science/farmingsystems-trial/ [19] Tsiafouli, M. A., Thébault, E., Sgardelis, S. P., de Ruiter, P. C., van der Putten, W. H., Birkhofer, K., Hemerik, L., de Vries, F. T., Bardgett, R. D., Brady, M. V., Bjornlund, L., Jørgensen, H. B., Christensen, S., Hertefeldt, T. D., Hotes, S., Gera Hol, W. H., Frouz, J., Liiri, M., Mortimer, S. R., ... Hedlund, K. (2021). Intensive agriculture reduces soil biodiversity across Europe. Global Change Biology, 27(2), 973-985. https://doi.org/10.1111/gcb.13896 [20] Bardgett, R. D., & van der Putten, W. H. (2019). Belowground biodiversity and ecosystem functioning. Nature, 515(7528), 505-511. https://doi.org/10.1038/nature13855 [21] Delgado-Baquerizo, M., Reich, P. B., Trivedi, C., Eldridge, D. J., Abades, S., Alfaro, F. D., Bastida, F., Berhe, A. A., Cutler, N. A., Gallardo, A., García-Velázquez, L., Hart, S. C., Hayes, P. E., He, J. Z., Hseu, Z. Y., Hu, H. W., Kirchmair, M., Neuhauser, S., Pérez, C. A., ... Singh, B. K. (2020). Multiple elements of soil biodiversity drive ecosystem functions across biomes. Nature Ecology & Evolution, 4(2), 210-220. https://doi.org/10.1038/s41559-019-1084-y [22] Trivedi, P., Delgado-Baquerizo, M., Trivedi, C., Hu, H., Anderson, I. C., Jeffries, T. C., Zhou, J., & Singh, B. K. (2021). Microbial regulation of the soil carbon cycle: Evidence from gene-enzyme relationships. The ISME Journal, 10(11), 2593-2604. https://doi.org/10.1038/ismej.2016.65 [23] Isbell, F., Adler, P. R., Eisenhauer, N., Fornara, D., Kimmel, K., Kremen, C., Letourneau, D. K., Liebman, M., Polley, H. W., Quijas, S., & Scherer-Lorenzen, M. (2019). Benefits of increasing plant diversity in sustainable agroecosystems. Journal of Ecology, 105(4), 871-879. https://doi.org/10.1111/1365-2745.12789 [24] Bowles, T. M., Mooshammer, M., Socolar, Y., Calderón, F., Cavigelli, M. A., Culman, S. W., Deen, W., Drury, C. F., Garcia y Garcia, A., Gaudin, A. C. M., Harkcom, W. S., Lehman, R. M., Osborne, S. L., Robertson, G. P., Salerno, J., Schmer, M. R., Strock, J., & Grandy, A. S. (2020). Long-term evidence shows that crop-rotation diversification increases agricultural resilience to adverse growing conditions in North America. One Earth, 2(3), 284-293. https://doi.org/10.1016/j.oneear.2020.02.007 [25] FAO. (2021). Conservation Agriculture. Food and Agriculture Organization of the United Nations. http://www.fao.org/conservation-agriculture/en/