- 1Instituto de Estudios Ambientales (IDEA), Universidad Nacional de Colombia, Bogotá, Colombia
- 2Laboratorio de Evolución y Ecología Teórica, Instituto de Zoología y Ecología Tropical, Facultad de Ciencias, Universidad Central de Venezuela, Caracas, Venezuela
- 3Erasmus Mundus Joint Master Programme on Climate Change and Diversity: Sustainable Territorial Development (CCD-STeDe), Advanced Master in GIScience and Unmanned Systems for the Integrated Management of the Territory and Natural Resources, University of Padova, Padua, Italy
Editorial on the Research Topic
Agrobiodiversity, community participation and landscapes in agroecology
The current model of conventional agriculture on the planet, originated in the so-called “Green Revolution” (GR), has generated positive and negative effects during its more than 80 years of application, starting in the 1940s. Among the negative effects are the accelerated loss of biodiversity and agrobiodiversity.
Different alternative farming systems propose managing the agrobiodiversity of agroecosystems (farms) to face many of the problems generated on monoculture farms (e.g., soil and genetic erosion, emergence of genetic resistance in pests and weeds, as well as public health problems associated with the use of agrochemicals), which are characteristic of the current conventional model (Vandermeer and Perfecto, 2005; Pollan, 2007).
Many positive effects are attributed to diverse crop fields. To name just a few, at the ecosystem level, beneficial effects have been proven in the preservation of the habitat for beneficial insects (pollinators, natural enemies of pests), reduction in GHG emissions, protection of soil and water, zero poisoning of human beings and nonhumans, reduction of pollutants and hazardous waste, and climate stability (Altieri, 1996; Nicholls, 2002; Letourneau et al., 2011; Gliessman, 2014; Vandermeer and Perfecto, 2018).
Agrobiodiversity is the very foundation upon which agroecology is built. It provides the mechanisms that allow agroecosystems to be managed sustainably through a set of beneficial interactions between their elements (e.g., mutualisms that occur in pollination, mycorrhizae or in crop associations).
The elements that constitute an agroecosystem are directly related to its main agroecological structure (MAS), which refers to the way in which the different sectors, patches, live fences, and vegetation corridors are arranged (spatial configuration), mixed or not with crop areas, grasslands, or agroforestry systems inside the farms and in their close surroundings. An agroecosystem structure is historically constructed by farmers because of innumerable cultural variables (symbolic, economic, social, political, and technological), in conjunction with environmental processes and its evolution configures agroecosystem matrices in the landscape (León-Sicard et al., 2018; Quintero et al., 2022). In this context, the use of the MAS approach, paired with other agroecological tools, such as the farmer-to-farmer methodology and participatory action research, can be employed as inputs into the decision-making process necessary for sustainable landscape management and conservation of agrobiodiversity in rural environments (Holt-Gimenez, 2006; Guzmán et al., 2012).
Most of the world's industrial agricultural landscapes present matrices of farms with very poorly developed agroecological structures that respond to the simplification characteristic of conventional agriculture, which has eliminated forests, corridors, patches, and live fences to make way for extensive monocultures (Vandermeer and Perfecto, 2005; León-Sicard et al., 2018). This simplification has also been the product of pesticides used to eliminate biological competitors to the main crop and to eliminate agents considered pathogenic or harmful.
In contrast, ecological- or agroecological-based agriculture proposes to maintain and reinforce agrobiodiversity in all its manifestations, both on and off the farm, as a way of achieving greater resilience, equity, autonomy, stability, and productivity through the multiple interactions that it fosters. Agroecological landscapes, therefore, will have agroecosystem matrices with more developed structures and functions favorable to agrobiodiversity.
These interactions between the different elements of agrobiodiversity are not restricted to the biological realm but are rather intricately woven into the fabric of socio-ecological systems.
These latter systems, whose central protagonists are the farmers and their cultural actions, are clearly the beneficiaries of the interactions (services) but are also responsible, in multiple ways, for the maintenance of this biodiversity. It is important to highlight that the interactions that articulate these systems manifest themselves on different scales, and in this Research Topic, we will find works that clearly show this fact.
This Research Topic collected 13 articles involving 46 authors from 36 research institutions in 14 countries on four continents (Table 1). The case studies dealing with different levels of agrobiodiversity (from crop to landscape) are based in seven countries: China, Italy, Nigeria, Colombia, Venezuela, Chile, and Uruguay.
This Research Topic includes articles that address the effects of climate change on the soil fauna of agroecosystems (Gao et al.) and how the soil microbiome can be used to adapt crops to the new climate context (Pino and Griffon). Innovative management approaches link silvopasture systems with ecosystem restoration (Durana et al.). Other contributions investigate the needs of the end users of this biodiversity (Tchokponhoué et al.), the role of entrepreneurial identity in shaping attitudes toward sustainability (Rossi et al.), and studies that address people's ecological, esthetic, and medicinal knowledge about the plants in their crops and communities (Kolze et al.; Monagas and Trujillo). Other articles address, at a larger spatial scale, the criteria for establishing community gardens in urban environments (Codato et al.), the precautions that must be taken in terms of conservation before undertaking agricultural expansions (González-Orozco et al.), or the strategic role of managing the relations among agroecosystems and landscapes to build resilient nature matrixes (Puppo et al.; Rettore et al.) The work of Acevedo-Osorio et al. proposed an index of agroecological functionality at the landscape level in Colombia, and Rojas et al. measured the degree of connectivity of agroecosystems with the landscape, using the MAS method, in a Mediterranean environment in Chile.
In all of these works, it is clear that agrobiodiversity, through the multiple functions it fulfills, articulates, and keeps these socio-ecological systems viable. In this way, we can understand it as the glue, often invisible to our eyes, that holds these systems together and, in doing so, makes our own lives possible.
The growing competition of labels for innovative approaches to sustainable agriculture should be analyzed using the elements of agroecology (FAO, 2019), with special attention to agrobiodiversity and its plural connections with food culture and traditions, circular and solidarity economy, and responsible governance (Tittonell et al., 2022).
Agroecology, as a meeting point of plural paths between science, movements, practices, and symbolic tissues, indagates the participatory processes of the construction of agrobiodiversity, food sovereignty, and biocultural diversity (Pimbert, 2018) from a long-term perspective, weaving, often not explicitly, practices of circulation and the construction of complex nested agroecosystems and landscapes.
From an emancipatory perspective (Giraldo and Rosset, 2023), the reflections and practices deal with territorial and food policies that transform structures, do not reproduce exclusion, and cultivate autonomy based on the co-construction of knowledge at a higher level of integration among crops, animal and vegetal species, landscapes, and biomes. Agroecology has the task of revealing the ontology of agriculture itself, deepening the meanings of being, living, and remaining in the places of communities that build and transfer over time, co-evolving multiscalar matrices of nature (Giraldo, 2022).
At a cultural level, the effects of the diverse management of agroecosystems result in greater opportunities for rural employment, greater justice in the social relations of production, appreciation of indigenous, peasant, and Afro-American knowledge, fair trade, and greater opportunities for peace and reconciliation nationally and internationally, among other aspects.
Author contributions
TL-S: Conceptualization, Writing – original draft. DG: Conceptualization, Writing – original draft. MD: Conceptualization, Writing – original draft.
Funding
The author(s) declare that no financial support was received for the research, authorship, and/or publication of this article.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
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References
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Giraldo, O. F. (2022). Multitudes Agroecológicas. Mexico City: Universidad Nacional Autónoma de México.
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Keywords: farming, biodiversity, connectivity, rural community, agroecological structure
Citation: León-Sicard TE, Griffon D and De Marchi M (2024) Editorial: Agrobiodiversity, community participation and landscapes in agroecology. Front. Sustain. Food Syst. 8:1414397. doi: 10.3389/fsufs.2024.1414397
Received: 08 April 2024; Accepted: 24 July 2024;
Published: 14 August 2024.
Edited and reviewed by: Mariela Fuentes Ponce, Autonomous Metropolitan University Xochimilco Campus, Mexico
Copyright © 2024 León-Sicard, Griffon and De Marchi. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Tomás Enrique León-Sicard, teleons@unal.edu.co
†These authors have contributed equally to this work