1
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
Building local capacity for coral reef restoration:
insights from two Caribbean MPAs
Natalia Uribe-Castañeda1 2 3*; https://orcid.org/0000-0002-3797-5894
Martin Main4; https://orcid.org/0000-0002-6374-6294
1. School of Natural Resources and Environment, University of Florida, Gainesville, Florida, USA; natalia.uribe.cas-
taneda@gmail.com (*Correspondence)
2. Estuaries and Mangroves Ecology Research Group, Universidad del Valle, Cali, Colombia.
3. Knauss Fellow, National Oceanic and Atmospheric Administration, Office of Marine and Aviation Operations, Silver
Spring, Maryland, USA.
4. Department of Wildlife Ecology and Conservation, University of Florida, Gainesville, Florida, USA; mmain@ufl.edu.
Received 29-VIII-2025. Corrected 05-XII-2025. Accepted 23-III-2026.
ABSTRACT
Introduction: Coral reef restoration requires building local capacity and engaging stakeholders throughout plan-
ning and implementation to reduce conflicts and enhance ecological and socio-economic outcomes.
Objectives: To compare stakeholder perspectives on community engagement in coral reef restoration within the
Seaflower Biosphere Reserve (Colombia) and Laughing Bird Caye National Park (Belize), and to develop tailored
guidelines for effective engagement strategies.
Methods: We conducted a multiple-case study in the Seaflower Biosphere Reserve (Colombia) and Laughing
Bird Caye National Park (Belize), collecting eight months of field data through interviews, surveys, and SWOT
analyses, coding qualitative data and analyzing surveys with unpaired two-sample t-tests.
Results: The primary strategy for enhancing engagement in coral reef restoration was building local capac-
ity, complemented by strategic planning, budgeting, and educational initiatives for youth. Respondents from
Seaflower Biosphere expressed greater concern for coral declines, a stronger sense of reef identity, and felt person-
ally affected by the issues. In contrast, residents of Laughing Bird Caye focused more on economic opportunities,
community meetings, and passive educational approaches.
Conclusions: These guidelines provide a flexible framework for community engagement in coral reef restoration,
emphasizing the importance of understanding socio-cultural and economic contexts, identifying key stakehold-
ers, and fostering trusting, inclusive, and transparent relationships to empower communities and prioritize their
active participation in restoration efforts.
Keywords: participatory research methods; interviews; SWOT analysis; qualitative analysis; Seaflower Biosphere
Reserve; Laughing Bird Caye National Park.
RESUMEN
Desarrollo de la capacidad local para la restauración de arrecifes de coral:
perspectivas de dos AMPs del Caribe
Introducción: La restauración de arrecifes de coral requiere fortalecer la capacidad local e involucrar a actores
clave durante la planificación e implementación para reducir conflictos y potenciar los resultados ecológicos y
socioeconómicos.
https://doi.org/10.15517/chgx9f68
SUPPLEMENT
2Revista de Biología Tropical, ISSN: 2215-2075 Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
INTRODUCTION
The United Nations (UN) has placed a
significant emphasis on ‘rehabilitating our
environment’ by making it a central pillar of
the 2030 Agenda for Sustainable Development
(United Nations Environment Programme,
2021). To underscore the importance of this
mission, the UN designated 2021–2030 as the
UN Decade of Ecosystem Restoration. This
global initiative aims to reverse the trends of
ecosystem degradation, promote biodiversity
recovery, and ensure the sustainable provision
of ecosystem services, while also addressing the
pressing issue of climate change.
Within this broader framework, the United
Nations has recognized the urgent need to
address the challenges facing coral reefs (United
Nations Environment Assembly, 2019), which
are some of the most biologically diverse and
economically valuable ecosystems on our plan-
et (Souter et al., 2021). The decline of coral reefs
due to factors such as rising sea temperatures,
ocean acidification, pollution, and overfishing
has raised alarms in the scientific community
and among environmentalists worldwide (Sout-
er et al., 2021). The consequences of coral reef
degradation are far-reaching, affecting marine
biodiversity, food security, and livelihoods in
many coastal communities. Recognizing the
imperative need to restore and conserve these
vital ecosystems, the UN adopted Resolution
4/13 during the 4th UN Environment Assembly
in 2019 (United Nations Environment Assem-
bly, 2019). This resolution specifically addresses
the sustainable management of coral reefs and
highlights the role of restoration in achieving
biodiversity goals set forth by the UN Environ-
ment Assembly (United Nations Environment
Assembly, 2019).
The challenges that coral reefs face have
enhanced restoration efforts worldwide, moti-
vating practitioners and researchers to engage
actively in coral reef restoration. Coral reef
restoration is “an active intervention aimed to
assist the recovery of reef structure, function,
and key reef species in the face of rising climate
and anthropogenic pressures, promoting reef
resilience and the sustainable delivery of reef
ecosystem services” (Hein et al., 2021). Recent
decades have witnessed the development of
innovative approaches, such as coral propa-
gation and planting, which has transformed
restoration into a global initiative (Boström-
Einarsson et al., 2020; Suggett et al., 2023). The
global community has recognized the critical
Objetivos: Comparar perspectivas de los actores sobre participación comunitaria en la restauración de arrecifes
de coral en la Reserva de Biosfera Seaflower (Colombia) y el Parque Nacional Laughing Bird Caye (Belice), y
elaborar lineamientos adaptados para el desarrollo de estrategias de participación efectivas.
Métodos: Se realizó un estudio de caso múltiple en la Reserva de la Biosfera Seaflower (Colombia) y el Parque
Nacional Laughing Bird Caye (Belice), recopilando datos de campo durante ocho meses mediante entrevistas,
encuestas y análisis FODA, codificando los datos cualitativos y analizando las encuestas mediante pruebas t de
dos muestras independientes.
Resultados: La estrategia principal para fortalecer la participación en la restauración de arrecifes de coral fue
el desarrollo de capacidades locales, complementada con planificación estratégica, elaboración de presupuestos
e iniciativas educativas dirigidas a la juventud. Los encuestados de la Reserva de la Biosfera Seaflower expresa-
ron mayor preocupación por el deterioro de los corales, un sentido más fuerte de identidad con el arrecife y se
sintieron personalmente afectados por estos problemas. En contraste, los residentes de Laughing Bird Caye se
enfocaron más en oportunidades económicas, reuniones comunitarias y enfoques educativos pasivos.
Conclusiones: Estos lineamientos ofrecen un marco flexible para la participación comunitaria en la restauración
de arrecifes de coral, destacando la importancia de comprender los contextos socioeconómicos y culturales,
identificar actores clave y fomentar relaciones de confianza, inclusivas y transparentes, para empoderar a las
comunidades y priorizar su participación en los esfuerzos de restauración.
Palabras clave: métodos de investigación participativa; entrevistas; análisis FODA; análisis cualitativo; Reserva de
la Biosfera Seaflower; Parque Nacional Laughing Bird Caye.
3
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
importance of these efforts and has invested
significantly in reef restoration. In the last 10
to 15 years, restoration practitioners reported
that a total of USD 258 million has been spent
to support coral reef restoration initiatives in 56
countries (Hein & Staub, 2021).
In parallel to these global efforts, the UN
has recently introduced ‘The Standards of Prac-
tice to guide ecosystem restoration,’ a compre-
hensive framework that emphasizes the role
of community engagement as a central com-
ponent throughout all phases of ecosystem
restoration projects (Nelson et al., 2024). These
standards emphasize the role of local com-
munities, including the unique role that local
communities can contribute to ecosystem res-
toration (Nelson et al., 2024).
The significance of community engage-
ment in conservation efforts has been highlight-
ed by extensive scholarly research. Community
engagement fosters enhanced environmental
stewardship through collective action (Agrawal
& Gibson, 1999; Ostrom, 1990) and strengthens
the capacity to adapt to climate change (Ayers
& Forsyth, 2009). As Stern (2000) pointed out,
community engagement is recognized as a
key driver for promoting conservation action,
given that involving communities is crucial
for managing environmental issues. Monroe
(2003) emphasized the importance of engaging
communities in environmental conservation,
particularly in an era where resource scar-
city and environmental degradation necessitate
behavioral changes that favor conservation.
With policies related to community engage-
ment in natural resource management being
implemented in nearly every country world-
wide (Ojha et al., 2016), it is evident that com-
munity engagement has assumed a central role
in shaping conservation and environmental
management efforts.
Although the importance of engaging
communities as partners in environmental
conservation is widely recognized, it is equally
important to acknowledge that communities
differ and that these differences influence per-
spectives, needs, and motivations of communi-
ty members. The failure to develop engagement
strategies that address collective concerns and
priorities is not likely to generate the type of
community support needed for successful and
long-lasting partnerships. While prior stud-
ies have highlighted the role of community
engagement in marine conservation, compara-
tively few have applied a structured, compara-
tive, and stakeholder and community driven
approach to inform management and restora-
tion practices across distinct Marine Protected
Areas. In this context, this study provides a
novel and applied contribution by integrating
stakeholders and community perspectives from
two Caribbean MPAs to generate management-
relevant insights for coral reef restoration.
The objectives of this paper were to (1)
evaluate similarities and differences in perspec-
tives toward community engagement among
different stakeholder groups in coral reef resto-
ration programs in two Marine Protected Areas:
the Seaflower Biosphere Reserve in Colombia
and the Laughing Bird Caye National Park in
Belize and (2) to use the information obtained
to construct guidelines for developing success-
ful community engagement strategies that can
be tailored to meet the needs of different com-
munities and directly support adaptive man-
agement and restoration planning in MPAs.
MATERIALS AND METHODS
Theoretical framework: we used Carter
et al. (2022) ethical community engagement
framework to guide this research and develop
guidelines for engaging communities in coral
reef restoration efforts, with a focus on princi-
ples 1 and 4 (Table 1). Principle 1 addresses the
values of stakeholders and states that “a deep
commitment to intrinsic values about people,
their natural endowments and their agency
is integral to inclusive (and effective) engage-
ment.” We chose to focus on this principle to
incorporate inquiries about diverse engagement
methods from the community perspective. We
also focused on principle 4, which is an ana-
lytical approach to engagement methodologies
that suggests “qualitative methods can be a use-
ful technique for inclusive engagement.
4Revista de Biología Tropical, ISSN: 2215-2075 Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
Study Areas: We selected two coral reef
restoration efforts implemented within Marine
Protected Areas (MPAs) in the Caribbean: the
Seaflower Biosphere Reserve in Colombia and
the Laughing Bird Caye National Park in Belize.
These sites were chosen because both initiatives
explicitly prioritize community engagement as
a central component of coral reef restoration.
The Seaflower Biosphere Reserve, located
in the western Caribbean, encompasses the
San Andrés Archipelago and represents the
largest MPA in the region. It is managed by the
Corporation for the Sustainable Development
of the Archipelago of San Andrés, Providen-
cia, and Santa Catalina (CORALINA) under
an integrated, multi-level management frame-
work, with zoning developed collaboratively to
promote ecosystem conservation, sustainable
development, and equitable benefit-sharing
(Taylor et al., 2013). Despite a local economy
heavily dependent on tourism, the Seaflow-
er MPA faces persistent challenges, including
overfishing, coral reef degradation, and illegal
fishing, which have prompted targeted efforts
to engage local communities in coral reef resto-
ration initiatives (Taylor et al., 2013).
Laughing Bird Caye National Park is a
UNESCO World Heritage Site of high ecologi-
cal and economic value, generating nearly USD
5 million annually through tourism (Nawaz et
al., 2017). The park is managed by the Southern
Environmental Association under a participa-
tory management framework that integrates
biodiversity conservation, sustainable tourism,
and long-standing coral reef restoration efforts
supported by active community involvement
(Alicea, 2010). These initiatives are closely
linked to the socio-economic dynamics of
the Placencia Peninsula, where rapidly grow-
ing coastal communities depend heavily on
marine resources and tourism, making local
participation essential for the long-term suc-
cess of conservation and restoration actions
(Webb et al., 2024).
Participatory Research Tools: we con-
ducted a multiple study case, which involves
the analysis of a particular issue by examin-
ing a series of cases within a defined system
(Creswell, 2007). We collected data over eight
months of fieldwork across the two marine
protected areas, which included in-depth semi-
structured interviews with key stakeholders
and restoration practitioners, a SWOT analysis
(Leigh, 2009) with community members, and
surveys of the broader community. A detailed
description of each research method can be
found in Uribe-Castañeda et al. 2024. Inter-
views with restoration practitioners and key
stakeholders were conducted using snowball
sampling until saturation and were comple-
mented by a SWOT workshop and surveys
designed to capture broader community per-
ceptions, motivations, barriers, and desired
participation in restoration activities. Quali-
tative data were transcribed, translated, and
Table 1
Ethical community engagement framework (Carter et al., 2022).
Principle Statement
1A deep commitment to intrinsic values about people, their natural endowments and their agency is integral to
inclusive (and effective) engagement
2An empathetic attitude along with specific interpersonal skills are essential to the engagement process
3Situational awareness is paramount to building trust and achieving inclusion
4In a research context, qualitative methods can be a useful technique for inclusive engagement
5Participatory monitoring, evaluation, and learning enhance facilitators and communities’ ability to reflect,
collaborate, co-create, and adapt to situations
6Without sufficiently deep commitment and ownership of engagement processes, initiatives are less likely to
sustain over time
5
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
coded through a multi-stage thematic analysis,
using MAXQDA 2022 qualitative analysis soft-
ware (Kuckartz & Rädiker, 2019) and com-
pared community surveys responses using an
unpaired two-sample t-test to assess differences
in responses between the two communities (De
Winter et al., 2016).
Research Permits: we obtained approval
for this research from the Institutional Review
Boards (IRBs) of the University of Florida, USA
(IRB202100741); the University of Rosario,
Colombia (Institutional Review Board CEI-UR
492-CS304); and the National Institute of Cul-
ture and History in Belize (ISCR/H/2/132). IRB
approvals were obtained to ensure the protec-
tion of research participants’ welfare and rights
in accordance with federal and state laws, local
policies, and ethical principles. All data col-
lected from respondents were kept anonymous,
de-identified, and confidential.
RESULTS
Interview data revealed that building local
capacity was the strategy most frequently men-
tioned in both communities (Table 2). More
than three-quarters of key stakeholders and
restoration practitioners identified it as the
primary action needed to enhance commu-
nity engagement in coral reef restoration. The
next most important component was strategic
planning and budgeting, which the Seaflower
Biosphere community ranked as a much higher
priority than the creation and enforcement of
new policies; in contrast, policy development
and enforcement were considered of roughly
equal importance at Laughing Bird Caye.
Surveys of the broader community in
both study areas, revealed that the community
believes in the importance of both community
and individual responsibility in protecting coral
reefs (Table 3). Both communities also indi-
cated low levels of trust or confidence regarding
the ability of environmental agencies to take
care of the corals, the future of the corals, and
whether current regulations are effective for
protecting coral reefs (Table 3).
Three significant differences emerged
between these two communities (Table 3). In
the Seaflower Biosphere, respondents expressed
a greater concern about coral reef declines
and a greater sense of identity with the coral
reefs. They also recognized that they would be
personally affected (e.g., economically, qual-
ity of life, etc.) if local coral reefs declined.
Conversely, in Laughing Bird Caye the com-
munity expressed less concern, a reduced sense
of identity, and generally indicated that they did
not feel they would be personally affected if the
health of the coral reefs declined.
Surveys were also used to identify and
prioritize strategies to promote community
engagement. The top seven strategies repre-
sented 90 % of ideas put forward by both com-
munities (Fig. 1). Educational strategies about
coral reefs and why they are valuable were
deemed to be highly important by both com-
munities, especially for youth. Adult educa-
tional and informational strategies were varied
Table 2
Importance of strategies for community engagement strategies identified from interviews with key stakeholders and
restoration practitioners from coral reef restoration programs at Laughing Bird Caye and Seaflower Biosphere Reserve.
Values represent the percentage of total responses (n = number of total interview segments).
Overall strategy Laughing Bird Caye
Response (%), n = 283
Seaflower Biosphere
Response (%), n = 237 Total (%)
Build local capacity 36.62 35.59 72.21
Strategic planning and budgeting 6.81 12.28 19.09
Policies creation and strengthening 6.58 2.14 8.71
Total 50.01 50.01 100.0
Values represent percent of total responses. n: number of total interview segments.
6Revista de Biología Tropical, ISSN: 2215-2075 Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
and included suggestions such as social media
campaigns, community meetings, and infor-
mational materials like billboards, flyers, and
brochures. Educational programs that also cre-
ated economic opportunities, such as the devel-
opment of a coral reef festival and educational
programs led by locals were suggested by both
communities.
Community members from Laugh-
ing Bird Caye were much more interested in
how coral reef restoration could contribute
to jobs and indicated greater interest in com-
munity meetings and passive forms of edu-
cation such as social media campaigns and
printed information.
Fig. 2. presents the strategies identified
during interviews with key stakeholders and
Table 3
Broad community perceptions about coral reefs were assessed on a 5-point Likert scale and analyzed using an unpaired t-test.
Laughing Bird Caye,
n = 60
Seaflower Biosphere,
n = 60 Unpaired T test
Mean SD Mean SD T test p
Community responsibility 4.28 0.64 4.47 0.83 1.35 0.18
Individual responsibility 4.10 0.66 4.32 0.81 1.61 0.11
Trust in organizations 3.65 0.80 3.35 1.20 1.61 0.11
Optimistic about future 3.67 0.86 3.40 1.12 1.46 0.15
Enough regulations 2.92 0.79 2.90 1.04 0.92 0.10
Concern 3.83 0.92 4.38 0.64 3.79 <0.01
Identity 4.00 0.82 4.47 0.70 3.34 <0.01
Personally affected 2.97 1.62 4.53 0.81 6.71 <0.01
Likert scale: 5 strongly agree - 1 strongly disagree; n: number of people surveyed.
Fig. 1. Community engagement strategies for coral reef restoration between Laughing Bird Caye National Park (Belize) and
the Seaflower Biosphere Reserve (Colombia). Points represent the percentage of survey respondents (n = 60 per site) selecting
each strategy, with lines connecting values across sites to highlight differences.
7
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
restoration practitioners, whose perspectives
on what was most important included, but
ranked differently, priorities identified by the
broader public. The most frequently mentioned
strategy identified was the importance of devel-
oping long-term cooperative planning and
budgeting among key stakeholders, particularly
those in reef-related businesses and govern-
ment. Enhancing and formulating outreach
strategies was also recognized as important in
both MPAs, with in-person meetings being
the most cited outreach method, followed by
social media campaigns. The results indicated
that outreach campaigns should prioritize pro-
moting behavioral change. Transdisciplinary
knowledge exchange was noted in both study
areas for its role in training and empowering
practitioners and community members.
DISCUSSION
Our study reveals both similarities and dif-
ferences in how local communities viewed coral
reef restoration across the two study areas. Both
interview and survey data highlight the central
role of building local capacity as the primary
strategy to enhance community engagement,
identified by key stakeholders and practitio-
ners in both areas. Similarly, broader commu-
nity surveys indicate a shared recognition of
the importance of community and individual
responsibility in protecting coral reefs, despite
low levels of trust in environmental agen-
cies and skepticism regarding the effectiveness
of current regulations. Educational initiatives,
particularly those targeting youth, and out-
reach strategies such as community meetings,
social media campaigns, and locally led pro-
grams were also consistently prioritized by both
communities. These convergences suggest that,
regardless of contextual differences, there is a
common understanding across diverse Carib-
bean MPAs that empowering local stakeholders
and fostering awareness are foundational com-
ponents for successful coral reef conservation.
In the Seaflower Biosphere, the community
demonstrated a stronger personal connection
to coral reefs, expressing greater concern for
reef decline, recognizing its potential personal
impacts, and viewing reefs as integral to their
identity. In contrast, responses from the Laugh-
ing Bird Caye community reflected less concern
about reef health or its impacts and greater
interest in how coral reef restoration could con-
tribute to local employment.
These findings provide insights into how
both shared values and context-specific priori-
ties can be leveraged to design locally adapted
engagement strategies, with practical relevance
not only for the studied MPAs but also for
Fig. 2. Local capacity building strategies for coral reef restoration between the two MPAs. Points represent the percentage
of times each strategy was mentioned by key stakeholders and restoration practitioners, with lines connecting values across
sites to highlight differences.
8Revista de Biología Tropical, ISSN: 2215-2075 Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
similar coastal communities elsewhere (Barnes
et al., 2019; McClanahan et al., 2015). Building
on these insights, we develop guidelines for
strengthening local capacity in coral reef res-
toration. These guidelines are designed to sup-
port both established and emerging programs,
thereby enhancing the overall effectiveness of
restoration efforts (Fig. 3).
The strategies in Fig. 3 reflect those in
Fig. 2 but are organized on a scale from low to
high levels of involvement to generate guide-
lines for building local capacity in coral reef
restoration. These guidelines encompass five
levels structured along a progressive continuum
of engagement, each representing increasing
influence over decision-making and greater
local empowerment in coral reef restoration.
The engagement process begins with rais-
ing awareness through outreach strategies,
then progresses to education programs that
include more structured and longer-term strat-
egies. The third level involves collaborative
and transdisciplinary training with focus on
knowledge exchange. Well-trained and edu-
cated community members will be able to
seek and create opportunities for cooperation
among stakeholders, representing the fourth
level of engagement. The final level culminates
in individuals who are locally aware, edu-
cated, trained, capable of fostering cooperation,
and empowered to lead restoration programs.
Throughout this research, both communities
identified fundamental human values under-
pinning these strategies: trust, respect, inclu-
sion, and transparency. These values form the
foundation of the guidelines and permeate
all actions for building local capacity (Fig. 3).
These findings encompass the ones identified
in the Standard of Practice for Ecological Resto-
ration, particularly Principle 2, which promotes
inclusive governance, social fairness, and equity
(FAO et al., 2021). Carter et al. (2019) further
emphasize that situational awareness is critical
for building trust and achieving inclusion. Our
results align with these findings and extend
them by providing insights derived from real-
world case scenarios. The following sections
further explain the five actions proposed in the
guidelines for building local capacity in coral
reef restoration.
Outreach: Effective outreach should aim
to raise awareness and understanding of the
Fig. 3. Guidelines for building local capacity in coral reef restoration based on data collected through surveys, interviews, and
SWOT analysis from the broad public, key stakeholders, and restoration practitioners associated with Seaflower Biosphere
Reserve, Colombia, and Laughing Bird Caye National Park, Belize.
9
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
critical importance of coral reefs while promot-
ing responsible environmental behavior (Rodrí-
guez-Martínez & Ortiz, 1999). The necessity for
outreach campaigns that foster behavior change
is illustrated by the following quote: “We need
to start working on the minds of the people to
achieve conservation outcomes. We must engage
with psychology to change mindsets. To effect this
change, a promoter is needed—an approach that
resonates with peoples self-satisfaction (Envi-
ronmental Educator).
To achieve this, outreach strategies should
be dynamic, engaging, creative, and rooted in
experiential learning. These strategies could
include a variety of activities suggested by com-
munity members, such as local coral reef festi-
vals, workshops, face-to-face meetings, social
media engagement, annual meetings, distrib-
uting informative materials, participating in
clean-up campaigns, sharing conservation mes-
sages at community events, and creating inno-
vative merchandise.
Research has shown that a deeper under-
standing of the coral reefs ecology, along with
collaborative conservation efforts, plays a cru-
cial role in preserving significant reef areas for
future generations (Sebens, 1994). In this con-
text, involving volunteers and citizen scientists
in coral reef restoration represents a valuable
strategy for enhancing the stewardship of natu-
ral resources (Hein et al., 2019). Citizen science
programs are specifically designed to facilitate
public participation in conservation, monitor-
ing, and research efforts (Pocock et al., 2015).
Education of youth: Youth education
represents a primary step towards building
local capacity in coral reef restoration pro-
grams. This approach recognizes that children
are a receptive demographic, eager to learn
and capable of taking on future leadership
roles in environmental practices. This strategy
aligns with the United Nations’ priorities in the
Decade on Ecosystem Restoration (Nelson et
al., 2024), which emphasizes educational initia-
tives aimed at shaping the values and actions
of future generations. Grimmette (2014) found
that students who participated in science camps
exhibited a significant shift in their perception
of the importance of nature to human well-
being and became more inclined to support
restoration efforts. Bai & Romanycia (2013)
assert that childrens education plays a crucial
role in fostering behavior change towards more
sustainable, caring, healthy, and regenerative
human-nature relations.
While various organizations have initiated
educational programs for children in both areas
of study, these initiatives tend to be isolated,
temporary, and limited in scope. The guide-
lines advocate for a continuous and structured
approach to youth education, ensuring that it
reaches children from diverse socio-cultural
backgrounds. A key strategy to make educa-
tion programs more inclusive and embedded
in coastal communities could be to introduce
an ocean literacy class into school curricula in
regions where children live closely with coral
reefs. The importance of including an ocean
literacy course in school curricula as part of
the education campaign is highlighted in the
following quote: “I believe environmental educa-
tion could be formally integrated into the curric-
ulum for schools. This is especially pertinent for
high schools and could extend to primary schools
as well” (Restoration practitioner).
Transdisciplinary and Collaborative
Training: This action focuses on knowledge
exchange between restoration practitioners and
local stakeholders. The integration of scientific,
traditional, and community-based knowledge
systems enhances understanding of the ecosys-
tem and improves the effectiveness of restoration
initiatives. This strategy aligns with Principle 6
of the Standard of Practice of Ecological Res-
toration (FAO et al., 2021), which states that
“Ecosystem restoration incorporates all types
of knowledge and promotes their exchange and
integration throughout the process.
This research underscores the significance
of formal certification training programs for
community members engaged in restoration
efforts. Restoration practitioners view certifica-
tions as an important step in their professional
development, providing pathways to future
10 Revista de Biología Tropical, ISSN: 2215-2075 Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
opportunities. This not only engages local com-
munities in restoration activities but also equips
community members with recognized qualifi-
cations that can advance their careers. Certi-
fication programs help establish and promote
professional standards, ultimately benefiting
public welfare (Nelson et al., 2017). However,
a standardized certification process for coral
restoration practitioners is currently lacking
in most Caribbean countries where coral res-
toration efforts are underway. The following
quote underscores the significance of certifica-
tion programs: “No other Caribbean nation has
a Tour Guide Restoration Licensing Program.
Their training is subsidized by grants, involving
approximately 160 hours of class time. After
completing the training, there are several sets of
exams” (Restoration Practitioner).
Cooperative long-term planning and
budgeting: emphasize the essential role of
sustained engagement and resource allocation
for long-term success. Long-term planning and
budgeting involve multiple stakeholders: gov-
ernment bodies, restoration organizations, aca-
demic institutions, community members, and
local businesses. Local stakeholder involvement
is crucial for biodiversity conservation, with
success depending on governance and socio-
cultural contexts (Sterling et al., 2017).
Recognizing the role of local businesses in
the economic benefits derived from coral reefs
is fundamental. Communities in both areas
highlight the need for businesses to contribute
more to restoration efforts. Financial commit-
ments from entities benefiting directly from
the reefs could enhance resource allocation
and local capacity. The necessity for sustained
funding and alternative strategies independent
of government cycles is reflected in a Deci-
sion Makers quote: “While it is crucial for the
state to acknowledge that nature operates on a
timescale beyond the annual, establishing strong
ties with the private sector is also a good strategy,
as they may not operate within these periodic
cycles. Innovative financing frameworks, such
as the Global Fund for Coral Reefs (GFCR),
offer alternatives to traditional grants, thereby
reducing dependence on foundations and diver-
sifying funding for reef restoration (Suggett et
al., 2023). Political support is vital for success-
ful long-term planning and budgeting. This
requires developing cooperative relationships
within government ministries, especially those
related to fisheries and tourism, to better sup-
port coral reef restoration. Integrating isolated
conservation programs into national strategies
will promote increased protection and stricter
enforcement of laws and regulations.
Economic empowerment and local lead-
ership: Empowering locals to take on leader-
ship roles fosters a sense of ownership and
pride in restoration efforts. Local leadership
enhances community-based conservation
interventions (Salerno et al., 2021). The ben-
efits of community-led conservation are encap-
sulated by a scientist who remarked: “Definitely,
get the community behind you. Make sure theyre
on board from the very start. If not, its not going
to work. Our reserve boundaries have expanded
multiple times since its establishment, all sparked
by the community recognizing the importance of
our work and requesting further expansion”.
This action aims to reduce social inequal-
ities and foster inclusive engagement. Such
inclusivity aligns with insights from Hallett et
al. (2023), emphasizing the need to address
disparities in the restoration process. Hiring
local professionals ensures that the restora-
tion is authentically rooted in the communi-
ty’s context, values, and aspirations. Fostering
local leadership and financial autonomy can
create self-sustaining initiatives that enhance
the social, economic, and environmental well-
being of communities involved in coral reef
restoration. Strategies must empower locals and
increase their participation in monitoring, stew-
ardship, and enforcement of natural resources,
promoting equitable community engagement.
Conclusion: Guidelines for building local
capacity in coral reef restoration (Fig. 3) were
developed from research in two Caribbean
marine protected areas with diverse cultures,
low-income communities, and significant
11
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
ecological value. The guidelines were designed
with an increasing level of engagement in
mind, though they do not necessarily reflect
the order in which actions should be taken.
They were developed by evaluating perspec-
tives and priorities among different stakeholder
groups within each community, which enabled
us to identify how these communities relate to
the resource, how they wish to be engaged and
empowered, the activities they want to par-
ticipate in, their needs and desires, and how to
prioritize these to build local capacity for resto-
ration programs. Our research benefited from,
and we recommend engagement of, diverse
stakeholder groups.
The two communities expressed different
perspectives on the importance of coral reef
ecosystems, which is likely due to differences in
environmental awareness and economic oppor-
tunities. Understanding the complex interac-
tions between humans, ecological systems and
the socio-cultural and economic characteristics
of the region is crucial for engaging local sup-
port and ultimately for the success of coral
reef restoration (Uribe-Castañeda et al., 2018).
Despite these differences, many similarities
emerged and the guidelines for building local
capacity (Fig. 3) are flexible, allowing them to be
tailored to local needs and desires. These guide-
lines can also be adapted to other geographic
areas and presumably other restoration and
conservation efforts, but doing so requires an
understanding of community needs, develop-
ing programs that are flexible and adaptable to
change, and establishing relationships built on
trust, respect, inclusiveness, and transparency.
Ethical statement: The authors declare
that they all agree with this publication and
made significant contributions; that there is no
conflict of interest of any kind; and that we fol-
lowed all pertinent ethical and legal procedures
and requirements. All financial sources are fully
and clearly stated in the acknowledgments sec-
tion. A signed document has been filed in the
journal archives.
ACKNOWLEDGMENTS
We are deeply grateful to several institu-
tions at the University of Florida for their sup-
port of this research, including the School of
Natural Resources and Environment, the Bio-
diversity Institute, the Tropical Conservation
and Development Program, the Department
of Wildlife Ecology and Conservation, and the
College of Agricultural and Life Sciences. We
also thank the International Coral Reef Society,
Wave of Change, and MAXQDA for their finan-
cial contributions. Special recognition is given
to Fulbright for supporting N. U.-C.s doctoral
studies. We further extend our appreciation
to the organizations, restoration practitioners,
community members, and key stakeholders
who partnered with us throughout this work.
Finally, we acknowledge Nia Morales, Jamie
Loizzo, Joshua Patterson for their support on
the development of this research.
REFERENCES
Alicea, E. (2010). Laughing Bird Caye National Park mana-
gement plan 2011-2016: A component of Belizes
World Heritage Site (NOAA Document No. 820).
United States National Oceanic and Atmospheric
Administration, Coral Reef Conservation Program.
https://repository.library.noaa.gov/view/noaa/820/
noaa_820_DS1.pdf
Agrawal, A., & Gibson, C. C. (1999). Enchantment and dis-
enchantment: the role of community in natural resou-
rce conservation.World Development, 27(4), 629–649.
https://doi.org/10.1016/S0305-750X(98)00161-2
Ayers, J., & Forsyth, T. (2009). Community-based adapta-
tion to climate change.Environment: Science and Poli-
cy for Sustainable Development, 51(4), 22–31. https://
doi.org/10.3200/ENV.51.4.22-31
Bai, H., & Romanycia, S. (2013). Learning from hermit
crabs, mycelia, and banyan. In R. B. Stevenson, M.
Brody, J. Dillon, & A. E. J. Wals (Eds.),International
handbook of research on environmental education(pp.
101–107). Routledge.
Barnes, M. L., Bodin, Ö., McClanahan, T. R., Kittinger, J. N.,
Hoey, A. S., Gaoue, O. G., & Graham, N. A. J. (2019).
Social-ecological alignment and ecological conditions
in coral reefs. Nature Communications, 10(1), 2039–
10. https://doi.org/10.1038/s41467-019-09994-1
Boström-Einarsson, L., Babcock, R. C., Bayraktarov, E.,
Ceccarelli, D., Cook, N., Ferse, S. C. A., Hancock, B.,
12 Revista de Biología Tropical, ISSN: 2215-2075 Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
Harrison, P., Hein, M., Shaver, E., Smith, A., Suggett,
D., Stewart-Sinclair, P. J., Vardi, T., & McLeod, I.
M. (2020). Coral restoration-A systematic review
of current methods, successes, failures and future
directions. PloS One, 15(1), e0226631. https://doi.
org/10.1371/journal.pone 0226631
Carter, L., Cosijn, M., Williams, L. J., Chakraborty, A.,
& Kar, S. (2022). Including marginalised voices in
agricultural development processes using an ethical
community engagement framework in West Bengal,
India.Sustainability Science, 17(2), 485–496. https://
doi.org/10.1007/s11625-021-01055-1
Carter, L., Williams, L., & Cosijn, M. (2019). The princi-
ples and practices of ethical community engagement:
Resources to support engaging for impact [Technical
report].Australian Centre for International Agricul-
tural Research, Australian Government.
Creswell, J. W. (2007). Qualitative inquiry and research
design: Choosing among five approaches (2nd Ed.).
SAGE.
De Winter, J. C. F., Gosling, S. D., & Potter, J. (2016). Com-
paring the Pearson and Spearman correlation coeffi-
cients across distributions and sample sizes: A tutorial
using simulations and empirical data. Psychological
Methods, 21(3), 273–290. https://doi.org/10.1037/
met0000079
FAO, IUCN, CEM, & SER. (2021).Principles for ecosystem
restoration to guide the United Nations Decade 2021–
2030. [Manual]. Food and Agriculture Organization
of the United Nations. https://openknowledge.fao.
org/handle/20.500.14283/cb6591en
Grimmette, K. A. (2014). The impacts of environmental
education on youth and their environmental awareness
[Undergraduate thesis]. University of Nebraska–Lin-
coln, United States of America.
Hallett, L. M., Aoyama, L., Barabás, G., Gilbert, B., Larios,
L., Shackelford, N., Werner, C. M., Godoy, O., Ladou-
ceur, E. R., Lucero, J. E., Weiss-Lehman, C. P., Chase,
J. M., Chu, C., Harpole, W, S., Mayfield, M. M., Faist,
A. M., & Shoemaker, L. G. (2023). Restoration ecolo-
gy through the lens of coexistence theory.Trends in
Ecology and Evolution, 38(11), 1085–1095. https://doi.
org/10.1016/j.tree.2023.06.004
Hein, M. Y., Birtles, A., Willis, B. L., Gardiner, N., Bee-
den, R., & Marshall, N. A. (2019). Coral restoration:
Socio-ecological perspectives of benefits and limita-
tions.Biological Conservation, 229, 14–25. https://doi.
org/10.1016/j.biocon.2018.11.014
Hein, M. Y., & Staub, F. (2021). Mapping the global funding
landscape for coral reef restoration [Technical report].
International Coral Reef Initiative (ICRI). icriforum.
org
Hein, M. Y., Vardi, T., Shaver, E. C., Pioch, S., Boström-
Einarsson, L., Ahmed, M., Grimsditch, G., & McLeod,
I. M. (2021). Perspectives on the use of coral reef
restoration as a strategy to support and improve reef
ecosystem services. Frontiers in Marine Science, 8,
618303. https://doi.org/10.3389/fmars.2021.618303
Kuckartz, U., & Rädiker, S. (2019). Analyzing qualitative
data with MAXQDA: Text, audio, and video. Springer.
https://doi.org/10.1007/978-3-030-15671-8
Leigh, D. (2009). SWOT analysis. In K. H. Silber, W. R. Fos-
hay, R. Watkins, D. Leigh, J. L. Moseley, & J. C. Des-
singer (Eds.), Handbook of improving performance in
the workplace (Vol. 1–3, pp. 115–140). Pfeiffer. https://
doi.org/10.1002/9780470592663.ch24
McClanahan, T. R., Graham, N. A. J., MacNeil, M. A.,
& Cinner, J. E. (2015). Biomass-based targets and
the management of multispecies coral reef fisheries.
Conservation Biology, 29(2), 409–417. https://doi.
org/10.1111/cobi.12430
Monroe, M. C. (2003). Two avenues for encouraging con-
servation behaviors. Human Ecology Review, 10(2),
113–125.
Nawaz, S., Bood, N., & Shal, V. (2017). Natural heritage,
natural wealth: highlighting the economic benefits of
the Belize Barrier Reef Reserve System World Heritage
Site [Technical Report]. World Wildlife Fund.
Nelson, C. R., Bowers, K., Lyndall, J. L., Munro, J., &
Stanley, J. T. (2017). Professional certification in
ecological restoration: improving the practice and the
profession.Restoration Ecology, 25(1), 4–7. https://doi.
org/10.1111/rec.12484
Nelson, C. R., Hallett, J. G., Romero Montoya, A. E.,
Andrade, A., Besacier, C., Boerger, V., Bouazza, K.,
Chazdon, R., Cohen-Shacham, E., Danano, D., Diede-
richsen, A., Fernandez, Y., Gann, G. D., Gonzales, E.
K., Gruca, M., Guariguata, M. R., Gutierrez, V., Han-
cock, B., Innecken, P. … Weidlich, E. W. A. (2024).
Standards of practice to guide ecosystem restoration
– A contribution to the United Nations Decade on
Ecosystem Restoration 2021–2030 [Technical report].
Food and Agriculture Organization of the United
Nations, Society for Ecological Restoration, & Inter-
national Union for Conservation of Nature. https://
doi.org/10.4060/cc9106en
Ojha, H. R., Ford, R., Keenan, R. J., Race, D., Carias
Vega, D., Baral, H., & Sapkota, P. (2016). Delocali-
zing communities: Changing forms of community
engagement in natural resources governance.World
Development, 87, 274–290. https://doi.org/10.1016/j.
worlddev.2016.06.017
Ostrom, E. (1990).Governing the commons: The evolution
of institutions for collective action. Cambridge Uni-
versity. Press.
Pocock, M. J. O., Roy, H. E., Preston, C. D., & Roy, D. B.
(2015). The biological records center: a pioneer of
citizen science. Biological Journal of the Linnean
13
Revista de Biología Tropical, ISSN: 2215-2075, Vol. 74 (S1): e20266957, abril 2026 (Publicado Abr. 22, 2026)
Society, 115(3), 475–493. https://doi.org/10.1111/
bij.12548
Rodríguez-Martínez, R., & Ortiz, L. M. (1999). Coral reef
education in schools of Quintana Roo, Mexico.Ocean
& Coastal Management, 42(12), 1061–1068. https://
doi.org/10.1016/S0964-5691(99)00061-7
Salerno, J., Andersson, K., Bailey, K. M., Hilton, T., Mwa-
viko, K. K., Simon, I. D., Bracebridge, C., Mangewa,
L. J., Nicholas, A., Rutabanzibwa, H., & Hartter,
J. (2021). More robust local governance suggests
positive effects of long-term community conserva-
tion. Conservation Science and Practice, 3(1), e297.
https://doi.org/10.1111/csp2.297
Sebens, K. P. (1994). Biodiversity of coral reefs: what are we
losing and why?Integrative and Comparative Biology,
34(1), 115–133. https://doi.org/10.1093/icb/34.1.115
Souter, D., Planes, S., Wicquart, J., Logan, M., Obura, D.,
& Staub, F. (2021). Status of coral reefs of the world:
2020 report [Technical report]. Global Coral Reef
Monitoring Network (GCRMN) and International
Coral Reef Initiative (ICRI). https://doi.org/10.59387/
WOTJ9184
Sterling, E. J., Betley, E., Sigouin, A., Gomez, A., Toomey,
A., Cullman, G., Malone, C., Pekor, A., Arengo, F.,
Blair, M., Filardi, C., Landrigan, K., & Porzecanski,
A. L. (2017). Assessing the evidence for stakeholder
engagement in biodiversity conservation. Biological
Conservation, 209, 159–171. https://doi.org/10.1016/j.
biocon.2017.02.008
Stern, P. C. (2000). New environmental theories: toward a
coherent theory of environmentally significant beha-
vior. Journal of Social Issues, 56(3), 407–424. https://
doi.org/10.1111/0022-4537.00175
Suggett, D. J., Edwards, M., Cotton, D., Hein, M., & Camp,
E. F. (2023). An integrative framework for sustai-
nable coral reef restoration. One Earth (Cambrid-
ge, Mass.), 6(6), 666–681. https://doi.org/10.1016/j.
oneear.2023.05.007
Taylor, E., Baine, M., Killmer, A., & Howard, M. (2013).
Seaflower marine protected area: governance for
sustainable development. Marine Policy, 41, 57–64.
https://doi.org/10.1016/j.marpol.2012.12.023
United Nations Environment Assembly. (2019). Report
of the United Nations Environment Assembly of the
United Nations Environment Programme. Fourth Ses-
sion (Nairobi, 11–15 March 2019). General Assembly,
Official Records (74th session, suppl. 25).
United Nations Environment Programme. (2021). Beco-
ming #GenerationRestoration: Ecosystem restoration
for people, nature and climate [Technical report]. UN
Environmental Programme, & Food and Agriculture
Organization of the United Nations.
Uribe-Castañeda, N., Morales, N., Loizzo, J., Patterson,
J., & Main, M. (2024). Community engagement in
coral reef restoration in the Seaflower MPA, Colom-
bia. Restoration Ecology, 32(8), e14268. https://doi.
org/10.1111/rec.14268
Uribe-Castañeda, N., Newton, A., & Le Tissier, M. (2018).
Coral reef socio-ecological systems analysis & res-
toration. Sustainability, 10(12), 4490. https://doi.
org/10.3390/su10124490
Webb, W. A., Wells, E. C., Prouty, C., Zarger, R., & Trotz,
M. (2024). Ethics and ambiguity in wastewater deve-
lopment on the Placencia Peninsula, Belize. Annals of
Anthropological Practice, 48(1), 130–145. https://doi.
org/10.1111/napa.12215