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iNaturalist as a Tool to Improve Agroecological Biodiversity Knowledge: An Ecuadorian Case Study Cover

iNaturalist as a Tool to Improve Agroecological Biodiversity Knowledge: An Ecuadorian Case Study

Open Access
|Jul 2026

Full Article

Introduction

Defined as public participation in scientific research that involves non-professional individuals in scientific endeavors (Kobori et al. 2018), citizen science has the potential to promote social empowerment, scientific literacy, the democratization of science, collaborative systems, and global citizenship (Finquelievich and Fischnaller 2014; Fritz et al. 2019; Wu and Hsu 2024). It can also contribute to the development of public policy and environmental governance (Kobori et al. 2016; Schade et al. 2021). As an exercise in democratizing knowledge production, citizen science has expanded successfully in recent decades, primarily in countries of the Global North, while practice and benefits in the Global South are only beginning to emerge (D’Onofrio, Arza, and Actis 2024).

Citizen science and agroecology share an approach centered on active public participation. Agroecology promotes the creation of sustainable food systems by engaging both producers and consumers (Hanappe et al. 2016). Similarly, citizen science enables people to contribute to the planning, monitoring, and evaluation of agroecosystems. However, its application within agricultural research remains relatively underexplored (van de Gevel, van Etten and Deterding 2020; Ebitu et al. 2021; Ryan et al. 2018).

Given that agriculture is a major driver of global biodiversity loss, addressing information gaps on biodiversity in cultivated landscapes is critical for improving our understanding of these impacts and for guiding conservation and restoration priorities (Remelgado, Levers, and Cord 2025). Integrating agroecology with citizen science can help address challenges related to fertilization, pest and pollinator management, land use, irrigation, and crop yields (Mourad et al. 2020). In addition, citizen science can drive shifts in practices and knowledge associated with agroecology and biodiversity conservation (Gerits et al. 2024), and thereby advance agricultural practices that support biodiversity conservation (HLPE 2019).

Nevertheless, several barriers limit stronger connections between agroecology and citizen science. A major challenge is the limited participation of farmers in citizen science projects (Mourad et al. 2020).

Numerous farmer-oriented applications exist (e.g., Plantix, Bioleaf, Adama Bullseye, Pmapp; Mendes et al. 2020), that focus on crop protection and diagnostics, nutrition and fertilization, irrigation, plant development, harvesting, general farm management, or field information systems. However, very few integrate environmental monitoring or biodiversity assessment components (Ruck et al. 2024). In contrast, one of the most widely used and successful citizen science platforms for biodiversity monitoring worldwide is iNaturalist and its associated application, Seek (Wittmann, Girman and Crocker 2019). In Latin America, 9 of the 17 countries operate their own national iNaturalist nodes to promote citizen science activities (iNaturalist 2025). These nodes play an important role in establishing the platform’s legitimacy and promoting its local adoption (Grattarola et al. 2024; Riquelme 2024).

Key features of iNaturalist—such as ease of use, open access, versatility, and automation—have facilitated the rapid development of exchange networks among users (López-Guillén et al. 2024). An additional benefit is the ability to identify pollinators without lethal sampling methods, thereby avoiding ethical concerns linked to specimen collection (Turley et al. 2024). Although iNaturalist activities cannot replace the expertise of professional specialists such as botanists, they remain an important data source when researchers carefully evaluate the contributed records (López-Guillén et al. 2024). Interactions among and between youth participants and professional taxonomists affiliated with museums and herbaria can further strengthen the use of the platform (Echeverria et al. 2021). Despite the large number of projects hosted on iNaturalist, relatively few scientific publications actively use the available data. Martínez-Sagarra et al. (2022) reported that 86% of iNaturalist projects in Spain serve exclusively educational or recreational purposes, while only two percent focus on scientific research. (In contrast, the data from iNaturalist on GBIF are used more than any other data provider for scientific publications). In 2023, the lead author of this article conducted an exploratory search within the global iNaturalist Projects section using the prefixes “agri” and “agro,” identifying 291 projects. After applying additional filters, including a minimum number of participants, location within agricultural areas, and a threshold of at least 10 observations per project, only 110 projects (38%) worldwide were found to directly link biodiversity observations to agriculture, agroecology, or agricultural environments.

In Ecuador, a megadiverse country, most iNaturalist initiatives have historically concentrated on documenting wild biodiversity. Starting with only four records in 2008, iNaturalist now reports more than 2.3 million observations from Ecuador, with exponential growth in recent years (iNaturalist 2025). The Ecuadorian national iNaturalist node (iNaturalistEC) is coordinated by the National Biodiversity Institute (INABIO), which has promoted the platform since 2018 (INABIO 2019). Most data contributions have been collected through “bioblitzes,” intensive citizen science events promoted by INABIO and other initiatives to enrich global biodiversity databases (Meeus et al. 2023).

Here, we present Agri Andes Ecuador, an agricultural biodiversity monitoring project initiated in July 2019 that actively engages students, farmers, and the general public in iNaturalist-based data collection. In Ecuador, only a small number of studies have emphasized community-based monitoring approaches involving both citizens and scientists (Medrano-Vizcaíno et al. 2023). Artificial intelligence platforms such as eBird, ePlants, and Ictio have expanded opportunities for environmental monitoring and for documenting environmental crimes (Jones et al. 2022; Páez-Vacas et al. 2023; Ulloa 2023). For our study, it is therefore significant that iNaturalist does not rely exclusively on artificial intelligence for species identification, and instead actively promotes collaboration between participants and experts (Meeus et al. 2023).

Our study focuses on rural regions of the Ecuadorian Andes, typically characterized by crop rotation systems involving potatoes, corn, quinoa, barley, lupins, flowers, and diverse vegetables, alongside livestock grazing and agroforestry practices (Struelens, Mina, and Dangles 2024). Our current approach aims to establish a biodiversity baseline in agroecosystems located 2,000 m above sea level, enabling the investigation of ecological patterns and processes as long-term data accumulate. Beyond its ecological objectives, this study advances citizen science in agroecology by demonstrating that participatory platforms can generate robust data in understudied agricultural landscapes. By engaging students, farmers, and expert identifiers, it highlights the capacity of citizen science to bridge information gaps, enhance taxonomic resolution, and inform decision-making. This aligns with emerging frameworks positioning citizen science as a tool for agroecological assessment and transformation (Mupangwa et al. 2025), particularly through context-specific knowledge co-production. Our findings provide empirical evidence that citizen science is not only a viable research approach but also a mechanism to foster learning, strengthen participation, and support transitions toward more sustainable agricultural systems.

The objectives of this study were to demonstrate the value of citizen science using the iNaturalist platform to document biodiversity in the agricultural landscape by: (1) examining iNaturalist projects in Ecuador and exploring biases in studies of agricultural diversity (2) reporting the diversity of wild plants, insects, spiders and birds within agricultural systems, (3) evaluating the improvement in the identification of a complex taxonomic class such as insects, and (4) identifying plant-insect ecological relationships (especially with respect to insects that are capable of pollination and plants that can provide these insects with the resources they need) from observations generated in the project from July 2019 to December 2023. Our ultimate goal is to develop citizen science-supported tools that generate useful data to inform decisions in support of the agroecological transition of food systems, to conserve non-cultivated biodiversity in crop systems and the ecosystem services they provide.

Methods

The Agri Andes Ecuador project

Agri Andes Ecuador was established in 2019 as part of the Agroecological Pest Management (AMIGO) project, funded by the McKnight Foundation and implemented in collaboration with local farmers and universities in Ecuador (Agri Andes Ecuador 2019). The initiative was conceived by the lead authors of this article, who are affiliated with the Pontifical Catholic University of Ecuador.

Between July 2019 and December 2023, the authors used iNaturalist to document birds, spiders, insects, and plants across predominantly agricultural landscapes in the central–northern Andes of Ecuador, at elevations above 2,000 m. The goal was to discover, learn about, and share information on these organisms and their interactions. The study area included the provinces of Carchi, Imbabura, Pichincha, Cotopaxi, Tungurahua, Bolívar, Chimborazo, Cañar, Azuay, and Loja, excluding national parks, reserves, moorland grasslands, and volcanic areas (Figure 1a). This region is characterized primarily by a mosaic of smallholder agricultural farms and expanding commercial floriculture, interspersed with remnants of Andean shrubland and moorland, as well as growing suburban and urban areas (Curatola Fernández et al. 2015; Guarderas, Smith, and Dufrene 2022) (Figure 1b).

Figure 1

(a) Spatial distribution of Agri Andes Ecuador records. Grid cells are 5.7 km²; green indicates areas above 2000 m with no observations. (b) Typical agricultural landscape in the Ecuadorian Andes.

Community building and project training strategy

The entomological literacy component aimed to enhance farmers’ knowledge using iNaturalist. To sustain interest and encourage continued data collection, we organized bioblitzes, which are events where people collect biodiversity data in a specific place and time, involving school and university students, farmers, and the general public.

We conducted bioblitzes in May 2022 and 2023 as part of World Bee Day. Our partnership with AMIGO was instrumental in recruiting students as new naturalists. With our partner universities, we coordinated schedules and class times that incorporated bioblitzes as curricular activities. We replicated this scheme with schools (with students between 13 and 17 years old) via institutional agreements and collaborative networks. To work with farmers, we formed teams of university students who had been trained to use the application. As most of the participating farmers were over 50 years old, we encouraged their young family members to accompany them to workshops and bioblitzes to help them adopt iNaturalist. Registration was via a Survey123 link (see Supplemental Table 1).

The content of the training sessions was based on the proposal by Natural History Museum (2019), which focused on explaining how the application works, how to load observations (pictures), and common errors in using the tool. The training was supplemented by the dissemination of other basic tips on how to use iNaturalist, inspired by the video tutorials on the app. This was done through workshops (especially for farmers), competitions, social networks (TikTok, Facebook), and videos, publications, and journal entries in iNaturalist (for students). iNaturalist journals entries can be used, for instance, to report on specific trips or observations, organize events, and record general notes. The Agri Andes Ecuador project used these diary entries to encourage participation, particularly among students, by providing information mainly about insects and plants (see Agri Andes Ecuador journal) (Agri Andes Ecuador 2019). Finally, the practical component of the training was developed through bioblitz, where people contributed with their observations (BioBlitz Guide 2024). This process aimed to integrate all of iNaturalist’s features to support the training process.

Data collection and analysis

Focus of the iNaturalist projects in Ecuador

To identify iNaturalist projects in Ecuador that focus on agricultural biodiversity, we searched the Projects tab using the keyword “Ecuador.” This search was conducted in September 2023 within the iNaturalist Ecuador network and identified 408 projects. Of these, 379 were analyzed after excluding those with fewer than three observations (see meta-analysis by Martínez-Sagarra, Castilla, and Pando [2022] on why some initiated projects may be abandoned). The following aspects of the analyzed projects were reviewed: creation date, topic, taxonomic group of interest, geographical area, number of observers, observations, identifiers and members. An alluvial chart was created to show the geographical areas of interest of the projects and their relationship with the relevant taxonomic groups. The results showed that, except for the Agri Andes Ecuador project developed by the authors, there were no similar iNaturalist initiatives in the country at the time of the search.

Focus on and analysis of data from the Agri Andes Ecuador project

To analyze the temporal evolution of the Agri Andes Ecuador project, we downloaded from iNaturalist the 32,457 records collected from July 2019 to December 2023 (53 months). We also downloaded the variables provided by the application: latitude, longitude, date and time of observation, concordant and discordant identifications, taxon identification number and different taxonomic categories, and numbers of observers and identifiers. To calculate the project’s growth, we used data on the number of users and observations. More specifically, we related the numbers of observations, observers, and identifiers to the training events held from the start of the project until December 2023. The data were organized chronologically using monthly statistics; the dates of training events (classes and bioblitzes) were recorded, and the average number of observations per month was calculated. In some cases, the “comment” feature (activated by typing “@” followed by the username) was used to help identify the identifiers. The person mentioned would then receive a notification containing a direct link to the comment.

A total of 1,639 people were trained in the use of iNaturalist, of which 460 joined the Agri Andes Ecuador project as observers. Training activities were adapted to fit the participating schools’ and universities’ calendars, which is why the analyses focused on certain months of the year when activity increased (in terms of both users and observations). Based on the iNaturalist database up to December 2023, the 20 experts who contributed the most identifications to the Agri Andes Ecuador project were selected from all the identifiers. We then reviewed these experts’ iNaturalist profiles to determine their country of origin and their role within the platform.

Quality framework and community verification

To evaluate improvements in taxonomic identification generated through citizen science, we filtered the iNaturalist database by biological group (plants, insects, spiders, birds), and then by order and family. Previous studies show that citizen science data can reach comparable or complementary quality to traditional sources such as herbarium records (White et al. 2023; Echeverria et al. 2021).

For insects, identification improvement was quantified by comparing the taxonomic rank of the initial observation with the final community consensus. Ranks were assigned ordinal values, with the initial identification set as level 1, and the highest resolution achieved as the final level. Improvement was calculated as the difference between these levels. Observations with fewer than three agreeing identifiers were excluded to ensure reliability.

Data quality followed iNaturalist standards, including date, georeferencing, multimedia evidence, and classification as wild or cultivated. Observations were categorized through the platform’s Data Quality Assessment (DQA) framework, where “research grade” is achieved when ≥2/3 of identifiers agree at species level or below. This community-based validation process reflects a core principle of citizen science: the co-production of reliable biodiversity data through distributed expertise.

Plant–insect (pollinator) interactions from iNaturalist imagery

Finally, to identify plant-insect relationships, especially in the case of pollinating insects, observations from the Cotopaxi project were analyzed. Cotopaxi is the province with the most records (1,530 observations, accounting for 4.7% of the insect data in Agri Andes Ecuador). A total of 950 photographs were selected in which both the flower and the insect could be clearly distinguished. Duplicate photos (of the same insect and plant) and low-quality images (blurry images) were eliminated, resulting in 720 images similar to those used by Pernat et al. (2024). Insects that could not be identified as pollinators in the literature or on iNaturalist were discarded, leaving 494 photographs. The main floral resource of each botanical family was determined using the Missouri Botanical Garden database (tropicos.org). Plants were classified as providers of nectar, pollen, or both.

Metrics, statistical procedures, and visualization tools

Descriptive statistics were used to calculate the percentage of the geographical area of interest covered by each taxonomic group. Project growth was determined by calculating the correlation between the number of observers and the number of observations, as well as between the number of observations and the number of identifiers. The number of observations and observers one month before each training activity (classes and bioblitzes) was recorded. To determine the absolute and relative growth values, the number of observations and observers one month after the training event was subtracted from the number one month before. The averages between training events were then compared to obtain an average growth rate. Excel professional plus 2021, R version 4.2.2 and Raw Graph (RAWGraphs 2013), and Scalable Vector Graphics (SVG) Editor Inskcape 1.0.2-2 (e86c870879, 2021-01-15) were used for data analysis and design.

Results

iNaturalist projects in Ecuador

The analysis showed that almost all of the analyzed projects had a generalist approach in terms of the diversity of species they intended to record. Of the 379 projects, 51% collected information at the country level and did not define a specific geographic area. The remaining projects focused on specific areas such as paramos (high altitude grasslands), protected areas, national parks, reserves, etc. Of the 379 projects, 59% were focused on flora and fauna in general, but only one (Agri Andes Ecuador) focused on agricultural landscapes with farmland biodiversity (Figure 2).

Figure 2

Alluvial chart of iNaturalist projects filtered with the keyword “Ecuador” with their main focuses according to geographic area and taxonomic groups. Source: iNaturalist 2023.

Dynamics of the Agri Andes Ecuador project

Agri Andes Ecuador has created a community of students, researchers and farmers who have contributed their records to the continued growth of this local initiative (see Supplemental Table 2). The community was 43% men and 57% women; and 93% of participants were high school/university students, while 7% were teachers, farmers, or professionals from other fields. The growth of the project is illustrated by the strong correlation between the number of observers and the number of observations (r = 0.97; p value = 0 < 0.001) in Figure 3a. This trend is further supported by Figure 3b, which shows a correlation between the number of observations and the number of identifiers (r = 0.98; p value = 0 < 0.001).

Figure 3

Temporal evolution of observers over 53 months of the Agri Andes project. (a) Observers and observations over time (VC, virtual classes; C, face-to-face classes). (b) Relationship between observations and identifiers (see Supplemental Table 1). (iNaturalist, accessed January 1, 2024).

Between July 2020 and November 2023, 27 training sessions were conducted, including virtual and in-person classes, as well as bioblitz workshops and competitions. Thanks to these activities (especially the bioblitzes), some trained students mobilized and recorded observations across several farmers’ fields. A total of 99 hours were invested in these activities. Between April and December 2021, training activities consisted mainly of classes, most of which were virtual because of the pandemic. Following these activities, observation numbers increased by between 10.5% and 16.6% (on average, 13.5%). An average of 2,000 observations per month was recorded in the four bioblitzes carried out (December 2020, May 2022, November 2022, and May 2023), ranging from 918 to 3,082 observations per month.

Interest in iNaturalist motivated faculty at participating universities to incorporate workshops, thesis projects, and teaching activities based on the application. The average number of records before the interventions was 318 per month. After the bioblitz and the classes, this figure increased to 745 per month. Overall, bioblitzes increased the slope of the number of observations over time by 200 to 459% compared with pre-bioblitz trends (Supplemental Table 3). Between the third and fourth years of the project (June 2022 to June 2023), the number of observers increased by 53.4%.

Between July 2019 and December 2023, Agri Andes Ecuador recorded 32,457 observations with 2,630 species, of which 51.5% were plants, 39.3% insects, 5.6% birds, 2.6% arachnids, and 0.9% other animals. 22.5% of the observations were identified to “research grade” level, while the rest of the records are still in taxonomic categories such as genus, family, and observations marked as “needs identification”.

The implementation of the Agri Andes Ecuador project allowed interaction with more than 1,900 identifiers (expert iNaturalist users mainly categorized as curators) and Agri Andes Ecuador project members (mainly ecuadorian researchers and university students) (Figure 3b). Of the top 20 identifiers who contributed the most to Agri Andes Ecuador, eight (40%) are Ecuadorian identifiers and naturalists, many of them with a regular identification activity within iNaturalist. Seven (35%) are curators in the iNaturalist platform, from three continents and nine countries (Germany, Brazil, Canada, Denmark, Ecuador, USA, Spain, Korea, and Mexico).

iNaturalist in the identification of diversity associated with agricultural fields

Plants represented the largest group recorded through citizen science, with 16,715 observations and 1,163 identified species, 99% of which were non-cultivated and associated with agricultural landscapes. Insects were the second most abundant group (12,762 records), mostly identified at the genus level, reflecting typical taxonomic challenges in citizen science datasets. Arthropod identifications were predominantly resolved at the genus level, with Bombus as the most frequent genus and Apis mellifera as the most recorded species. Birds (1,846 records) and spiders (860 records) were less represented. These patterns highlight both the potential and limitations of participatory platforms in generating biodiversity data across taxa (Figure 4).

Figure 4

Diversity of insects, plants, birds, and spiders reported and identified in the Agri Andes project (2019–2023). The three most recorded species are detailed in the upper right of each box.

iNaturalist as a tool to improve taxonomic identification in insects

Among insects recorded through citizen science, Diptera was the most represented order (4,686 records; 34%), followed by Hymenoptera (21%) and Coleoptera (17%). When considering observations with at least three agreeing identifiers, Hymenoptera showed the highest taxonomic resolution, with 550 records identified at species level, followed by Diptera (349) and Coleoptera (277) (Figure 5a).

Figure 5

Relationship between initial–final identification levels and taxonomic improvement across insect families in four orders. For Hemiptera, Diptera, and Coleoptera: 4 = class, 8 = infraorder, 12 = tribe; for Hymenoptera: 4 = class, 8 = infraorder, 12 = subfamily.

Taxonomic improvement varied among orders, reflecting differences in detectability and expertise availability. All groups showed progress from initial to final identifications, demonstrating the effectiveness of community-based validation (see Supplemental Figure 1). Maximum identification levels (MIL) differed across orders, although some records remained unidentified even at the family level, highlighting persistent knowledge gaps (see Supplemental Figure 2).

More than 50% of records in Hymenoptera, Diptera, and Coleoptera reached higher taxonomic resolution (tribe/genus level) (Figure 5a,b,c). A. mellifera accounted for 40% of species-level identifications within Hymenoptera, indicating a bias toward conspicuous species. In contrast, Hemiptera showed lower initial and final identification levels. (Figure 5d). These results illustrate both the strengths and limitations of citizen science in improving taxonomic knowledge through distributed expertise.

Ecological relationships between insects’ pollinators and plants

From 494 citizen science photographic records, 21 insect species across 4 orders were identified interacting with 27 plant families. Hymenoptera dominated (71%), with A. mellifera, Bombus robustus, and Bombus funebris as the most frequent species, reflecting observer bias toward conspicuous pollinators. Diptera with species such as Eristalis tenax and Eristalis bogotensis, accounted for 13% of photographic records analyzed. These insects were associated with 24 plant families (89%), mainly Fabaceae, Asteraceae, Brassicaceae, and Malvaceae. Fabaceae was the most represented plant family (39% of records) (Figure 6). These findings demonstrate the capacity of citizen science imagery to document plant–insect interactions, while also highlighting taxonomic and detection biases inherent to participatory data collection.

Figure 6

Alluvial chart of plant–insect interactions from 494 Agri Andes records. Insects are identified to species and plants to family. Main floral resources per family were obtained from information linked to iNaturalist.

Discussion

iNaturalist projects in Ecuador have addressed a variety of objectives, often at the country level. In cases where geographical scope was indicated, they have primarily focused on reporting biodiversity in protected areas, national parks, urban environments, or other non-agricultural areas. Only one study (our Agri Andes Ecuador project) was conducted within agricultural systems. This highlights a critical gap, but also a conceptual opportunity to position citizen science within agroecology, a field that explicitly integrates biodiversity conservation and crop habitat management (HLPE 2019). Agricultural landscapes remain underrepresented in biodiversity monitoring despite being key sites of ecological interaction and transformation (Remelgado, Levers, and Cord 2025). From a citizen science perspective, this underrepresentation reflects a broader tendency to prioritize “charismatic” or protected ecosystems, rather than productive landscapes where biodiversity is often more contested and less visible.

In this context, our project contributes to an emerging body of work that situates citizen science not only as a data collection tool, but as a knowledge co-production process embedded in socioecological systems. Martínez-Sagarra et al. (2022) have shown that iNaturalist projects in Spain led by local associations, involving researchers in project design, identification support, and data analysis, attracted more participants when the purpose and scientific value were clearly articulated. In Agri Andes Ecuador, partner universities incorporated citizen science tools into formal training programs and degree projects, which extend beyond the interactivity described by Echeverría et al. (2021). This integration suggests a shift from contributory citizen science models toward more collaborative or co-creative approaches, where participants are not only observers but also learners and interpreters of ecological processes.

This distinction is important from a theoretical standpoint. Citizen science has often been categorized along a spectrum, from contributory (data collection) to collaborative and co-created models (Bonney et al. 2009). Our project aligns more closely with the latter, as its goal is not only to report observations but to generate knowledge relevant for conservation and agricultural decision-making in underrepresented systems (Remelgado, Levers, and Cord 2025). In this sense, citizen science becomes a mechanism for linking ecological monitoring with evidence-based management and policy processes, particularly in contexts where formal scientific data are scarce.

At the same time, the project demonstrates that the quality and impact of citizen science depend heavily on the strength of interaction networks between scientists and participants. As highlighted by Henning et al. (2023), community networks can lead to significant scientific discoveries, such as the rediscovery of species previously thought extinct. In our case, the recording of (Pteroplatus luculentus), an insect with no recent reports of living specimens, illustrates how agricultural landscapes managed without pesticides can serve as reservoirs of overlooked biodiversity. This finding reinforces the idea that citizen science can reveal “hidden” ecological dynamics, particularly when it is embedded in territories undergoing alternative management practices.

Bioblitzes were identified as one of the most effective strategies for expanding participation (see also Martinez-Sagarra et al. 2022), increasing observations, and raising awareness. Their effectiveness aligns with previous studies emphasizing the role of gamification and collective events in motivating participation (Bowser et al. 2013; Meeus et al. 2023; Potsikas et al. 2023). However, our experience also highlights a limitation often overlooked in citizen science literature: Participation does not automatically translate into sustained engagement or data quality. Variations in duration, geographic scope, and institutional involvement may dilute sampling effort, particularly in projects that rely on heterogeneous participant groups such as students, schools, and universities.

This points to a key tension in citizen science: the balance between scale and depth. While large-scale participation increases data volume, it may also reduce consistency and engagement. Dimson and Gillespie (2023) suggest that projects with lower intrinsic appeal, such as those focused on agricultural systems, require additional support, feedback, and institutional mediation. Our findings support this view, as approximately three-quarters of participants did not remain actively engaged. This suggests that citizen science in agricultural contexts may require more intensive facilitation and feedback loops, particularly when working with communities that are not traditionally engaged in biodiversity monitoring.

Technological barriers also played a significant role. While smartphones facilitated participation among younger users (see Stevenson, Merrill, and Burn [2021] for a project with students at the University of Massachusetts, Boston), they limited engagement among farmers, particularly those with low connectivity or limited device capacity. This digital divide is consistent with findings from other contexts (Dehnen-Schmutz et al. 2016), and highlights the importance of adapting citizen science tools to local conditions. The positive reception of the Seek application suggests that offline-capable tools with intuitive interfaces can reduce barriers to participation (Campbell et al. 2023). However, the effectiveness of such tools depends on the availability of local biodiversity data, pointing to a recursive challenge: citizen science depends on data availability, but also contributes to it.

Data quality remains a central concern in citizen science. Our results confirm previous findings that identification accuracy can be variable, particularly in taxonomically complex groups such as insects (López-Guillén et al. 2024; Gardiner and Roy 2022). While plants were easier to record and often overrepresented, insects posed greater challenges due to their size, diversity, and the limited taxonomic expertise among participants. Nevertheless, methodological adaptations, such as the use of magnifying lenses and video recordings linked to youtube (Mina 2023), improved data quality and facilitated expert validation. These practices illustrate how citizen science can evolve through iterative methodological innovation, rather than relying solely on standardized protocols.

Importantly, citizen science platforms such as iNaturalist also provide opportunities to integrate and value local and experiential knowledge. In our project, the inclusion of local names and uses for plants and insects enriched the dataset and expanded its interpretative value (e.g., moscabeja, pakunka, and piliquitze; Cárdenas et al. 2025). This aligns with broader discussions on the role of citizen science in recognizing diverse knowledge systems and challenging the dominance of purely scientific classifications. From this perspective, citizen science is not only about data collection but also about epistemic inclusion, allowing different ways of knowing to coexist and inform ecological understanding.

The focus on pollinators revealed patterns consistent with global observations, including biases toward larger and more visible species (Turley et al. 2024). While such biases are often seen as limitations, they also reflect the ways in which perception, visibility, and cultural familiarity shape participation in citizen science. Rather than attempting to eliminate these biases entirely, it may be more productive to recognize them as part of the situated nature of observation, and to design complementary strategies that capture less visible taxa.

Despite these challenges, our findings demonstrate that monitoring insect–plant interactions does not require highly specialized expertise or equipment (Lewinsohn et al. 2022). Through guided observation and training, participants were able to document ecological interactions and identify generalist pollinators across multiple plant families. This suggests that citizen science can play a key role in democratizing ecological knowledge, making it accessible and actionable for non-specialists. In agricultural contexts, this has important implications for teaching–learning processes, as it enables farmers to reinterpret ecological interactions and potentially adjust management practices (Puig 2021; Curilén and Luciano 2023).

From a broader perspective, the Agri Andes Ecuador project illustrates how citizen science can contribute to transformative processes in socioecological systems. Rather than simply generating data, the project facilitated the creation of a community of practice, supported by training activities and institutional partnerships. However, the limited participation of farmers indicates that further work is needed to strengthen engagement and ensure that citizen science initiatives are inclusive and context-sensitive.

Overall, integrating citizen science into agricultural systems requires moving beyond a purely technological or data-driven approach. It involves recognizing citizen science as a social, epistemic, and ecological process, where participation, learning, and knowledge production are intertwined. In this sense, the potential of citizen science in agroecology lies not only in its ability to monitor biodiversity, but also in its capacity to reshape how people perceive, value, and manage ecological interactions within agricultural landscapes.

Despite active agroecological transitions, ecological data remain scarce in Ecuadorian agroecosystems and elsewhere around the world, where citizen science projects are crucial to documenting non-crop biodiversity. Engaging farmers and communities can strengthen monitoring capacities, democratize knowledge, and inform policies that link food sovereignty, sustainability, and biodiversity conservation to the country’s broader social and economic transformations (Saenz-Lituma 2025).

Conclusions

Considering the impacts of agriculture on biodiversity, citizen science applications such as iNaturalist hold considerable potential for expanding ecological monitoring within cultivated landscapes. Within the Agri Andes Ecuador project, the development of an active community of naturalists was supported through training activities and public events, even under the constraints of the COVID-19 pandemic, which likely limited participation and slowed project implementation. Beyond generating biodiversity records, our findings indicate that citizen science functioned as a process of knowledge co-production, enabling participants to observe, interpret, and engage with ecological interactions, particularly plant–insect relationships within agricultural contexts. This suggests that citizen science can contribute not only to data generation but also to shaping how ecological processes are understood by different actors.

However, participation was uneven, with limited engagement from farmers, highlighting the need for more context-sensitive approaches that address barriers such as connectivity, digital literacy, entomoliteracy, and time availability. Tools such as the Seek application showed potential to lower these barriers by enabling participation among users with limited experience using mobile technologies. The project’s key strengths include the integration of naturalist training into university curricula, and the presence of a national iNaturalist node, both of which supported sustained engagement and a sense of shared ownership across geographically distributed participants. Bioblitz events were effective in increasing observations and fostering interaction, although more standardized protocols may improve data consistency and long-term engagement. Overall, this study highlights the potential of citizen science to link biodiversity monitoring, social learning, and environmental education, while also underscoring the importance of designing inclusive and context-adapted approaches for agricultural systems.

Supplementary Files

The supplementary files for this article can be found as follows:

Supplemental Table 1

Total number of class hours and other activities promoting the use of iNaturalist in schools and universities. DOI: https://doi.org/10.5334/cstp.819.s1

Supplemental Table 2

Links and descriptions of websites related to the Agri Andes Ecuador Project and iNaturalist. DOI: https://doi.org/10.5334/cstp.819.s2

Supplemental Table 3

Effect of bioblitz events on the growth rate of observations (200–459% increase compared with pre-bioblitz trends). DOI: https://doi.org/10.5334/cstp.819.s3

Supplemental Figure 1

Relationship between initial–final identification levels and taxonomic improvement across insect families in four orders. For Hemiptera, Diptera, Coleoptera: 4 = class, 8 = infraorder, 12 = tribe; for Hymenoptera: 4 = class, 8 = infraorder, 12 = subfamily. DOI: https://doi.org/10.5334/cstp.819.s4

Supplemental Figure 2

The taxonomic levels were counted in the order of the Hymenoptera, up to the maximum level of identification. Apis mellifera was used as an example. DOI: https://doi.org/10.5334/cstp.819.s5

Data Accessibility Statement

The data are summarized in Agri Andes Ecuador. The analyzed data is available directly from the Agri Andes Ecuador project website.

Ethics and Consent

Our team confirms that training included a presentation of the iNaturalist platform, where participants agree to terms of use and data-sharing policies upon registration, constituting informed consent. Only publicly available data were used, and no personal information was accessed or stored. Participation of schoolchildren and farmers was voluntary. No data or information that could personally identify participants were collected.

Acknowledgements

The authors were supported by the Mcknight Foundation, which funded the project. Scientific support was provided by researchers from the French Institute for Development (IRD). The authors would like to thank the partner universities of the Agri Andes Ecuador project, as well as the farmers and students who participated in the workshops and bioblitz.

Author Contributions

All authors conceptualized the idea and defined the questions and methodological approach. Diego Mina carried out the analyses, assisted by Olivier Dangles and Rommel Montufar, and led the writing. Mayra Coro actively contributed to the workshops/bioblitz and data collection, especially data on plant-insect ecological relationships. All authors contributed to the writing, participated in the discussion and agreed on the final version of the manuscript.

DOI: https://doi.org/10.5334/cstp.819 | Journal eISSN: 2057-4991
Language: English
Page range: 17 - 17
Submitted on: Nov 26, 2024
Accepted on: Jun 16, 2026
Published on: Jul 23, 2026
Published by: Ubiquity Press
In partnership with: Paradigm Publishing Services

© 2026 Diego Mina, Rommel Montúfar, Mayra Coro, Olivier Dangles, published by Ubiquity Press
This work is licensed under the Creative Commons Attribution 4.0 License.