Methods
for data quality control.
CNC was initially planned in 2016 as a friendly competition between San Francisco and
Los Angeles, but has grown swiftly, with over 400 cities in over 40 countries competing
annually (Palma et al., 2024). The event gives communities a framework to record local
biodiversity and invites the public to get involved in conservation initiatives.
Why is it an IT-based BioBlitz? Because the CNC enables participants to upload
observations to citizen science observatories such as iNaturalist, MINKA or any other. A
global community of specialists and enthusiasts validate the observations. In particular,
the CNC has been useful for local governments as it provides an affordable method to
assess urban biodiversity, guide land management decisions, and promote
environmental stewardship at the community level (Palma et al., 2024).
CNC has also been educationally impactful, as participants have been able to have
hands-on learning experiences to help them understand local ecosystems. Comparative
research in many countries has demonstrated that CNC enhances the sense of
connectedness with nature, particularly in urban people, where direct contact with
biodiversity is often limited (Sakurai et al., 2022) . Participants from different cultures
have become more conscious of environmental issues and more motivated to take part
in conservation efforts after their engagement in CNC (Sakurai et al., 2022) . CNC
engagement remained resilient even during the COVID-19 epidemic and community
science approaches were adapted efficiently (Kishimoto and Kobori, 2021)
.
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Challenges and opportunities for marine citizen science
Marine citizen science (MCS) is gaining prominence in marine and coastal management
(Cigliano et al., 2015) , spatial ecology and conservation (Bosso et al., 2024) .
Participatory marine monitoring systems enable volunteers, from amateur naturalists to
trained divers, to report data and expand their scientific knowledge through biodiversity
monitoring, marine debris tracking, and environmental parameter collection (Busch et
al., 2016; Ceccaroni et al., 2020; Kelly et al., 2020; Garcia-Soto et al., 2021; Soacha
Godoy et al., 2022) . These participatory activities enable data gathering in previously
understudied marine areas and enhanced public involvement in marine conservation
issues (Thiel et al., 2014; Dean et al., 2018).
Marine citizen science initiatives have shown significant policy significance and
research potential. For example, citizen-produced data from the UK’s Seasearch project
helped to designate 38 marine conservation zones (Earp and Liconti, 2020) . Similarly,
the Marine Biodiversity and Climate Change project (MarClim) has produced data that is
important evidence of changes in species distributions owing to climate change, and
offers practical guidance for adaptive marine management and policy makers (Soacha
Godoy et al., 2022) . These examples highlight the promise of MCS to impact marine
governance and to empower coastal populations to participate in ocean stewardship at
the same time.
MCS is under-represented in the literature compared to terrestrial projects (Roy et al.,
2012; Sandahl and Tøttrup, 2020; Garcia-Soto et al., 2021; Wehn et al., 2025). But the
quick growth of this field highlights its increasing importance to the academic and the
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general public. Volunteer contributions provide rich coverage of maritime ecosystems,
which may be difficult and/or costly to access using traditional scientific methods and
represent a major opportunity to complement professional research efforts (Kelly et al.,
2020). In addition, MCS facilitates the co-creation of ecological knowledge, aligning with
the agendas of inclusive and transformative research (Fraisl et al., 2020; Soacha Godoy
et al., 2022).
However, MCS has its own unique obstacles, largely due to the intrinsic complexity and
logistics of marine environments compared with terrestrial ones. Furthermore,
participation is limited by logistical issues, such as the requirement for certain
equipment (e.g. fins, diving masks, wetsuits or underwater cameras) or safety issues
(Martin et al., 2016) . This, together with the fact that MCS sometimes needs technical
skills such as swimming or diving, as well as access to intertidal and underwater
environments, can influence the motivation and long-term engagement of participants
(Martin et al., 2016; Liñán et al., 2022) . Similarly, social or geographical constraints
might influence the inclusiveness and representativeness of participation, which
requires enhancing community outreach and support mechanisms (Mazumdar et al.,
2018).
The nature of marine species and their habitats makes it more challenging to engage
the public in marine biodiversity monitoring. Non-specialists generally don’t know many
taxonomic groups of marine organisms. Even if they are phylogenetically distant, MCS
volunteers may have difficulty in distinguishing between coralline algae, bryozoans and
sponges (Cigliano et al., 2015; Terenzini, Safaya and Falkenberg, 2023) . In terrestrial
settings, on the other hand, unskilled and non-expert participants may discriminate
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between obvious classifications such as birds and reptiles. This information gap and the
limited access to underwater environments limit the opportunities for broad participation
in MCS, unlike land-based efforts.
Unlike the terrestrial initiatives, where the participants can typically post their
observations to a citizen science platform digitally on site, the underwater data
collection usually requires the participants to get out of the water to re-establish the
connectivity before uploading their findings. This additional process prevents immediacy
and can decrease motivation, resulting in data loss (Terenzini, Safaya and Falkenberg,
2023). Additionally, maritime habitats lack obvious terrestrial markers, and the absence
of distinct site boundaries can impede participants from developing a sense of
ownership and attachment to a certain spot, which may result in reduced involvement
(Cigliano et al., 2015).
The unpredictability of weather and sea conditions adds an additional dimension of risk
to MCS events. Activities may be cancelled and data continuity and engagement
affected by adverse sea conditions, such as strong currents or poor underwater visibility.
MCS also faces the challenge of maintaining the quality and consistency of data
gathered by volunteers. Inconsistencies in methods of observation, data input
procedures and species identification accuracy might undermine the reliability of results,
especially when protocols are not standardised (Ceccaroni et al., 2020; Kelly et al.,
2020). Standardised procedures and accurate data validation mechanisms, which are
missing in many present programs, are essential for the proper incorporation of MCS
into national or international biodiversity databases.
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MCS involves logistical and safety challenges that aren’t as visible in terrestrial citizen
science. Scuba diving, snorkelling, boat-based activities and specialised instruments
increase operational costs and risks, requiring strict safety regulations and insurance
considerations (Cigliano et al., 2015) . These factors tend to concentrate participation
among skilled ocean users such as divers, recreational boaters or marine biologists and
may reduce participation from wider audiences (e.g. tourists).
MCS integration into legislative and regulatory frameworks is still at its infancy.
Successful case studies have demonstrated the impact of volunteer data on marine
management. However, many citizen science datasets remain underutilised, due to
concerns about their quality or their incompatibility with formal monitoring programs
(Fraisl et al., 2020; Gumiero et al., 2025) . This needs building partnerships between
scientists, citizen science networks, local authorities and policymakers to ensure that
participatory data are validated and contextualised within decision-making processes.
To address these MSC problems for both volunteers and organisers, a variety of
techniques is required. Effective outreach and communication strategies are especially
important to boost volunteer motivation and engagement. Transparency about the
participation process, the participants’ role, and the concrete impacts of their
contributions influences the feeling of purpose and ownership of the participants (Liñán
et al., 2022) . Ongoing communication through social media, community events, and
dedicated engagement teams stresses the value of volunteer involvement and
promotes sustained engagement and a sense of community among volunteers (Cigliano
et al., 2015; Mazumdar et al., 2018).
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The BioMARathon Model: Adapting BioBlitzes to Marine
Citizen Science
To address some of the specific constraints of MSC, the BioMARathon model adapts
the short, intensive logic of the BioBlitz to a longer, seasonal and distributed format.
While “Blitz” evokes a sudden collective effort to reach a specific goal, the term
“BioMARathon” combines the idea of a longer-lasting process with “MAR”, meaning sea
in Catalan, to emphasise the marine focus of the initiative.
The BioMARathon is an international citizen science event designed to document
marine and coastal biodiversity through local, regional or national editions organised
within a shared framework. Participants upload biodiversity observations to a citizen
science platform, while local organisations, scientific institutions and public authorities
support mobilisation, validation, curation, learning and dissemination. Its purpose is not
only to record species, but also to create the conditions to foster recurrent participation,
marine biodiversity learning and the production of biodiversity data that can support
research, awareness-raising and conservation.
But the BioMARathon goes beyond an extended BioBlitz; it is a new class of citizen
science event resting on four interrelated design principles (Figure 1). First, participation
was extended across a season rather than concentrated into a single short event.
Second, activity was distributed across multiple local opportunities for involvement
rather than being tied to a single site and date. Third, the initiative relied on a visible
network of local mobilising partners rather than on centralised recruitment alone. Fourth,
participation was supported by relatively rapid scientific feedback and validation, helping
volunteers see that their contributions were part of a meaningful collective process.
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The first design choice mattered because marine participation is highly sensitive to
environmental conditions. By spreading the initiative across months instead of days,
BioMARathon reduced its dependence on a single weather window and increased the
chances that different kinds of participants could join at least some of the activities. This
extension also aligned the event more closely with ecological seasonality: a longer
campaign provides an opportunity to register a wider range of marine organisms
observations and seasonal variation over a brief snapshot could reasonably provide.
The second and third design choices mattered for engagement. A short event can be
intense and motivating, but it also produces a very narrow window for participation.
BioMARathons instead created multiple points of entry through guided outings, local
communication, and repeated opportunities to contribute. This is especially important for
marine contexts, where many potential participants depend on trusted intermediaries
such as diving centres, federations, or coastal organisations in order to access the sea
safely and meaningfully. The mobilising community, therefore, did more than advertise
the initiative; it acted as a bridge between scientific aims and real participation
conditions.
Rapid feedback also plays a central role. The original project design identified fast
validation or identification responses as one of the key factors supporting volunteer
engagement (Liñán et al., 2022). That is relevant in marine citizen science because the
field setting itself often prevents immediate upload and recognition. If participants only
receive delayed or opaque responses, the perceived value of their contribution can
weaken. The extended seasonal design of BioMARathons gave experts more room to
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validate observations continuously, making feedback part of the engagement logic
rather than an afterthought.
Figure 1: Comparison between BioBlitz and BioMARathons
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Also, a longer data collection time increases the likelihood of recording a wider range of
species, including non-indigenous species, protected species, and rare occurrences
that may not be observed in a brief monitoring period. As a result, the findings
communicated to participants are more comprehensive and scientifically valuable,
offering richer insights into marine biodiversity. This increases both the robustness of
the data and the participant experience, as the more extensive and impressive results
are a powerful motivator for continued engagement.
The Janus Engagement Framework
To implement the BioMARathon, we use the Janus Engagement Framework (Figure 2),
originally developed to address long-term public engagement challenges in citizen
science projects (Liñán et al., 2022). In the BioMARathon model, the value of Janus lies
in its capacity to organise engagement as a distributed process involving different
communities, responsibilities and forms of motivation. This is especially relevant in
MCS, where barriers to participation are not only motivational but also logistical,
technical, social and environmental.
MCS initiatives must address several simultaneous challenges: access to the sea,
weather and safety constraints, the need for specific equipment or skills, difficulties in
identifying marine species, delayed data upload after underwater activities, and the
need for trusted validation mechanisms. It is difficult for a single stakeholder to tackle all
these issues. For this reason, BioMARathons built this engagement strategy on the
Janus Framework, being designed as a multi-stakeholder engagement system in which
different communities perform complementary roles. The Janus Framework helps to
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identify who can trigger participation, who can reduce barriers, who can provide learning
and scientific credibility, and who can offer recognition or rewards that make sustained
participation meaningful.
Figure 2: Simplified representation of the Janus Engagement Framework applied to the
BioMARathon model. This figure illustrates the Janus Engagement Framework as the
integration of the Hook Model and the Fogg Model. The Hook cycle links trigger, action, reward,
and investment, while the Fogg Model highlights motivation and ability as conditions shaping
participation. In the BioMARathon context, investment is central because it links initial
engagement to future re-engagement, supporting continuity and retention across successive
cycles of participation.
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The framework applies the Quintuple Helix of Innovation (Carayannis, Barth and
Campbell, 2012) to identify these roles and define four community types:
The Participatory Community includes the volunteer participants who contribute to the
initiative as observers, identifiers, validators or local ambassadors. In BioMARathons,
this community is diverse: it may include underwater photographers, divers, snorkellers,
coastal naturalists, families, students and people interested in marine biodiversity. Their
contribution is not limited to uploading observations; they also help to expand collective
knowledge by learning to recognise species, improving data quality over time, sharing
the initiative through their networks, and returning in subsequent editions. For this
community, engagement is supported through clear participation instructions, accessible
activities, visible results, species identification support, friendly competition, public
recognition and the possibility of seeing their observations become part of a wider
scientific and conservation effort.
The Academic Community includes universities, research centres and scientific
experts responsible for the scientific framing of the initiative. In BioMARathons, this
community provides methodological guidance, taxonomic expertise, data validation and
curation, training and feedback. Academic actors, therefore, act both as scientific
guarantors and as engagement enablers: they transform volunteer observations into
validated biodiversity data, provide workshops and identification support, and create
feedback loops that show participants that their contributions have scientific value.
Rapid validation or identification responses, ideally within a short period after the
observation is uploaded, are an important engagement mechanism because they
convert participation into learning and recognition (Liñán et al., 2022).
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The Mobilising Community includes the organisations that are in direct contact with
potential participants and can activate participation locally. In BioMARathons, this
community may include underwater activities federations, diving centres and clubs,
snorkelling companies, environmental NGOs, local associations, schools, museums or
coastal outreach organisations. Their role is central because many potential participants
cannot access marine environments safely or confidently without trusted intermediaries.
Mobilising actors organise guided activities, communicate the initiative to their own
communities, help participants use the digital platform, provide local knowledge and
reduce practical barriers such as access, equipment, safety and confidence. They also
benefit from the initiative by offering their members or clients opportunities to
collaborate with science, receive training from experts and participate in a collective
environmental action.
The Facilitating Community includes public authorities, protected area managers,
municipalities and other institutions responsible for the governance or stewardship of
the study area. Their role is to create enabling conditions for participation and to
connect the initiative with local environmental management, education or conservation
agendas. In BioMARathons, facilitating actors can support permits, dissemination,
access to public spaces, local legitimacy, institutional visibility and the potential use of
citizen-generated data in decision-making. Their involvement can also reinforce the
perceived relevance of the initiative, helping volunteers understand that their
observations are not isolated records but part of a broader effort to improve knowledge
and stewardship of marine and coastal ecosystems.
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Figure 3 shows how this multi-stakeholder approach structured the BioMARathon as a
dynamic Community of Practice (CoP), in which each stakeholder group played a
distinct and necessary role; Figure 3 also complements this by illustrating concrete
examples of the engagement actions through which these roles were operationalised in
practice.
Figure 3. Examples of actions through which the Janus Engagement Framework was
implemented in the BioMARathon and the MINKA observatory. This annotated figure presents
concrete examples of actions associated with different elements of the Janus Engagement
Framework in the BioMARathon, including notifications, comments and validations in MINKA,
social media, newsletters, organised activities, log-in and observation upload, attribution and
acknowledgement, mentorship, training, collaborative identification sessions, simple
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participation protocols, shared goals, and trust in scientists. The symbols indicate the
stakeholder groups mainly involved in each action: academia, citizens, and enablers, where
enablers correspond to the mobilising and facilitating communities in the Janus framework. The
figure illustrates how engagement was operationalised through multiple coordinated actions
across both the participatory process and the supporting observatory infrastructure.
MINKA: a citizen science observatory for BioMARathons
MINKA (EMBIMOS research group, 2021) is the participatory infrastructure used to
implement the BioMARathon concept. It was originally based on the iNaturalist code,
which has become a reference for IT-based biodiversity recording and BioBlitz-style
participation. However, in the BioMARathon model, MINKA is not only a data repository
or an observation upload tool, but one of the infrastructures that makes the Janus
Engagement Framework operational.
MINKA supports BioMARathons by enabling the different Janus communities to perform
their roles within a shared digital environment. For the participatory community, the
platform provides a visible space where volunteers can upload observations, receive
identifications, follow the progress of the campaign and see their contributions as part of
a collective biodiversity effort. For the academic community, MINKA provides tools to
explore, filter, identify and validate observations, making it possible to transform
volunteer contributions into more reliable biodiversity data. For the mobilising
community, it offers a common platform with specific projects for their guided activities,
training sessions and local campaigns. For the facilitating community, it provides a
public and traceable record of biodiversity observations that can support
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awareness-raising, environmental education and, where appropriate, local management
discussions. In this sense, MINKA complements the Janus Engagement Framework by
providing the technical layer required for engagement actions to become visible,
coordinated and sustained.
Figure 4. Example of an adaptation for managing marine observations in MINKA. (a) Initial filter
panel for searching observations in iNaturalist, which is more focused on terrestrial taxons. (b)
MINKA filter panel with specific filters for marine taxons (icons highlighted in dotted blue).
MINKA has also been adapted to better support marine biodiversity monitoring during
BioMARathons (Figure 4). As an example, its graphical tools and filter panels allow
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observations to be selected according to predefined criteria. MINKA has incorporated
dedicated filter options for marine taxonomic groups, facilitating the work of marine
specialists who need to explore, select and validate different taxa during BioMARathons
according to their expertise. This is particularly important in MCS because expert
validation is both a data quality mechanism and an engagement mechanism: it
improves the reliability of observations while also providing participants with feedback
that reinforces learning and motivation.
BioMARató Catalunya: the Founding Case of the
BioMARathon Model
The BioMARathon model is conceived as an umbrella format that can be implemented
through different local, regional or national editions. In this sense, it follows a logic
similar to other large-scale citizen science events such as the City Nature Challenge: a
shared participatory structure, common digital infrastructure and comparable
engagement principles are adapted to different territories through local organising
communities. The first BioMARathon was launched in Catalonia in 2021 under the
name BioMARató Catalunya. The model was later replicated in northern Portugal in
2024 as BioMARatona Norte and expanded into the whole Portuguese continental coast
in the 2025 edition. Further expansion has been discussed in other regions.
BioMARató Catalunya is the founding implementation of this model. The first edition
took place between spring and summer 2021 and involved the provinces of Barcelona,
Girona and Tarragona (Catalonia, Spain) through snorkelling, scuba diving and coastal
observation guided activities and also spontaneous participation not linked to any
activity. Its objective is to photograph as many living organisms as possible along the
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Catalan coast, including birds, coastal plants and underwater species, and to upload
these observations to the citizen science observatory MINKA. The initiative is promoted
by the Institute of Marine Sciences (ICM-CSIC).
Since then, BioMARató Catalunya has shown continuous growth in participation,
observations and taxonomic coverage. In 2021, 117 people participated and collected
more than 10,000 observations of 1,061 species. In 2022, the Catalan edition involved
127 participants and generated more than 21,700 observations of 1,300 species. In
2023, BioMARató Catalunya exceeded 60,000 observations, tripling the previous year’s
total, with contributions from more than 300 volunteers and 1,440 species recorded
during that edition. In 2024, the initiative reached more than 91,000 research-grade
observations and over 1,720 species, with the participation of 481 people. In 2025, the
fifth edition further expanded the model: more than 520 people contributed over 94,000
observations to MINKA, and 2,040 species were identified. With these contributions,
BioMARató Catalunya accumulated more than 380,000 observations and 2,870
documented species.
These results show that BioMARató Catalunya is not only an engagement event, but
also a mechanism for producing relevant biodiversity knowledge. Several findings are
particularly significant. The 2021 edition detected 24 non-indigenous species (NIS)
along the Catalan coastline and recorded two first records in Catalonia. The 2022
edition registered four first records for the Catalan coast and also documented mortality
events in red coral and gorgonian populations, consistent with concerns about the
ecological effects of high temperatures and marine heatwaves. During the 2023 edition,
participants detected 34 NIS and 40 protected or threatened species. The three editions
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together had censused around 1,900 marine species. The 2025 edition achieved the
first complete spatial coverage of the Catalan coastline, in 10x10 km² grid cells
resolution.
Figure 5: Evolution of the number of observations per month from January 2020 to January
2026 performed in the local BioMARathons (Catalonia coasts). The shaded vertical bands
indicate the annual BioMARató periods, running approximately from the first Saturday of May
until mid October. The figure shows the strong seasonal pattern of marine participation, with
observation peaks during the BioMARató months and lower activity during winter. Rather than
representing a single isolated annual event, the pattern suggests a cyclical but cumulative
model of participation, in which each edition contributes to reactivating and consolidating the
community of observers.
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The four Janus communities contributed to BioMARató Catalunya's success. The
participatory community includes volunteers contributing observations and
identifications. The academic community is centred on the Institute of Marine Science
(ICM-CSIC), which supports scientific framing, species validation and data curation, and
the broader design of the initiative. The mobilising community includes the Catalan
Federation of Underwater Activities (FECDAS) and a set of small coastal companies
and organisations promoting volunteer participation locally through guided outings,
communication, and logistical support. The facilitating community included
municipalities and public authorities with responsibilities connected to coastal territories
and environmental awareness, such as the Area Metropolitana de Barcelona (AMB).
Figure 5 shows a clear seasonal rhythm. Observations increase during the BioMARató
period, when sea conditions are usually more favourable, organised activities are
concentrated, and communication efforts are stronger. These changes occur during
winter, when sea temperature decreases, weather conditions are less favourable, and
overall outdoor activity makes the marine environment less accessible. This seasonal
decline should not be interpreted as a failure of engagement. In marine citizen science,
a reduction in activity during less favourable months is expected.
The key interpretive question is whether participation disappears after each edition or
whether part of the community remains available to be reactivated. Figure 5 shows that
after each BioMARató edition, activity does not simply return to the initial baseline
observed before the initiative was consolidated. Instead, the figure suggests a
cumulative pattern in which annual peaks are followed by lower but persistent activity,
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suggesting a retention rate of participants, and subsequent editions reactivate
participation from a progressively stronger base.
This interpretation is important because the success of a recurring MCS initiative cannot
be assessed only by the intensity of its annual peak. A short-term increase in
observations during a campaign may indicate successful mobilisation, but it does not
necessarily demonstrate sustained engagement. For BioMARató Catalunya, the
relevant pattern is the combination of recurrence and accumulation: each edition acts as
a new trigger for participation, while the persistence of activity between editions
suggests that the initiative has gradually built a more stable community of marine
observers.
This pattern also connects with the Janus Engagement Framework. Janus and its
implementation combine short-term engagement mechanisms,such as campaign
launches, guided activities, friendly competition, communication and public recognition,
with longer-term mechanisms, including expert validation, learning, repeated
participation, community identity and the integration of observations into a shared
biodiversity dataset. In Janus terms, the annual event works as a recurring trigger, but
retention depends on whether participants continue to perceive value after the
immediate event has passed. Data suggests that BioMARató not only generate
temporary mobilisation; it also creates conditions for reactivation, learning and
continuity.
The 2025 edition is particularly relevant for interpreting this resilience. During July 2025,
poor weather and bad sea conditions along the Catalan coast led to the cancellation of
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several BioMARató activities for safety reasons. In a short BioBlitz-style event, similar
conditions could have seriously compromised the entire data collection window. In
contrast, the extended BioMARathon format reduced dependence on a single
favourable date or weekend. Although weather-related cancellations affected activity
during part of the season, the overall pattern still shows continuity and reactivation. This
supports one of the central arguments of the BioMARathon model: in marine
environments, where participation is strongly conditioned by safety, access and
environmental variability, engagement must be designed with enough temporal and
organisational flexibility to absorb disruption.
Lessons for Citizen Science Practice
BioMARató Catalunya suggests several lessons for designing citizen science initiatives
in marine and other logistically demanding environments.
First, extending the duration of an event can be an engagement strategy, not only a
sampling strategy. In marine contexts, participation is shaped by sea state, weather,
accessibility, safety and seasonality. A longer event window reduces dependence on a
single date and allows activities to be rescheduled when conditions are not safe or
favourable.
Second, distributed local mobilisation is essential. BioMARató Catalunya shows that
marine citizen science cannot rely only on centralised communication by a scientific
institution. Mobilising organisations such as diving centres, federations, environmental
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NGOs and local associations act as trusted intermediaries. They provide access to
participants, local knowledge, logistical support, safety conditions and social legitimacy.
Third, feedback and validation should be treated as engagement mechanisms. Expert
validation is often discussed in relation to data quality, but in the BioMARathon model, it
also supports learning, recognition and motivation. This is especially relevant in marine
biodiversity, where many taxa are difficult for non-specialists to identify.
Fourth, digital infrastructure must support communities, not only data collection. MINKA
enables volunteers, experts, mobilising organisations and facilitating institutions to act
within a shared environment. It therefore functions as part of the engagement
architecture, connecting observations, validation, learning and public visibility.
Finally, recurring citizen science events should consider retention and reactivation as
key indicators of success. In seasonal marine contexts, sustained engagement does not
necessarily mean constant participation throughout the year. It may appear as cyclical
engagement: participants reduce activity when conditions are unfavourable but return
during subsequent editions.
Constraints and Limitations
The Catalan coast case study describes the development and implementation of the
BioMARathon model rather than presenting a formal evaluation of its causal effects.
The annual figures on participants, observations and species are descriptive indicators
of growth and consolidation, but they should not be interpreted as experimental
evidence.
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The interpretation of retention is also based on community-level observation patterns
rather than on a formal user-level retention analysis. Monthly observation data suggest
reactivation and cumulative participation across editions, but future work should analyse
individual participant trajectories to distinguish new participants, returning participants,
occasional contributors and highly active long-term contributors.
The BioMARató Catalunya case is also shaped by specific territorial and institutional
conditions, including the role of ICM-CSIC, the availability of MINKA, collaboration with
diving and environmental organisations, and the characteristics of the Catalan coast.
These conditions may not be directly replicable in all coastal regions. The BioMARathon
should therefore be understood as an adaptable model rather than a fixed protocol.
Finally, the model requires sustained coordination. Extending an event over several
months reduces dependence on a single weather window, but it also requires
continuous communication, partner coordination, data validation and curation and
platform maintenance.
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Author contributions
SL, Conceptualisation, Writing–original draft. BC, Data curation, Writing–review and
editing. AA, Data analysis. XS, Data curation. MT, Writing–review and editing, CR,
Writing–review and editing, JP: Conceptualisation, Writing–original draft, Funding
acquisition.
Funding
The EMBIMOS research group was funded by the European Commission through the
PHAROS project, funded by the European Union’s Horizon Europe programme under
Grant Agreement No. 101157936, the ANERIS project under Grant Agreement No.
101094924, and the CS-MACH1 project under Grant Agreement No. 101214613. The
ICM-CSIC authors acknowledge the institutional support of the ‘Severo Ochoa Centre of
Excellence’ accreditation (CEX2019-000928-S and CEX2024-001494-S funded by AEI
(which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
The copyright holder for this preprintthis version posted May 15, 2026. ; https://doi.org/10.64898/2026.05.13.724939doi: bioRxiv preprint
10.13039/501100011033). The opinions expressed herein are those of the authors and
do not necessarily reflect those of the projects, the European Union or the European
Commission.
Acknowledgments
We thank all volunteer participants who contributed to BioMARató Catalunya as
observers, identifiers, validators or local ambassadors (see the full list here:
https://zenodo.org/records/17602383). A single participant may contribute to more than
one of these roles, and this multiplicity of contributions is central to the
community-based nature of the initiative. We also thank the mobilising organisations
that supported participant engagement and data acquisition, including the Federació
Catalana d’Activitats Subaquàtiques (FECDAS), Plàncton Diving, Oceánicos, Anèl·lides
and Xatrac, as well as the local institutions and organisations that helped facilitate
activities along the Catalan coast.
Competing Interests
The author(s) have no competing interests to declare.
(which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
The copyright holder for this preprintthis version posted May 15, 2026. ; https://doi.org/10.64898/2026.05.13.724939doi: bioRxiv preprint