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Abstract and Figures

The 15th UN Convention on Biological Diversity (CBD) (COP15) will be held in Kunming, China in October 2021. Historically, CBDs and other multilateral treaties have either alluded to or entirely overlooked the subterranean biome. A multilateral effort to robustly examine, monitor, and incorporate the subterranean biome into future conservation targets will enable the CBD to further improve the ecological effectiveness of protected areas by including groundwater resources, subterranean ecosystem services, and the profoundly endemic subsurface biodiversity. To this end, we proffer a conservation roadmap that embodies five conceptual areas: (1) science gaps and data management needs; (2) anthropogenic stressors; (3) socioeconomic analysis and conflict resolution; (4) environmental education; and (5) national policies and multilateral agreements.
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Received: June  Accepted:  July 
DOI: ./conl.
VIEWPOINT
A conservation roadmap for the subterranean biome
J. Judson Wynne1Francis G. Howarth2Stefano Mammola3,4
Rodrigo Lopes Ferreira5Pedro Cardoso3Tiziana Di Lorenzo6
Diana M. P. Galassi7Rodrigo A. Medellin8Bruce W. Miller9
David Sánchez-Fernández10 Maria Elina Bichuette11 Jayant Biswas12
Cory W. BlackEagle13 Chaichat Boonyanusith14 Isabel R. Amorim15
Paulo Alexandre Vieira Borges15 Penelope J. Boston16 Reynold N. Cal17
Naowarat Cheeptham18 Louis Deharveng19 David Eme20 Arnaud Faille21
Danté Fenolio22 Cene Fišer23 Žiga Fišer23 Samuel M. ʻOhukaniʻ¯
ohiʻa
Gon III24 Forough Goudarzi25 Christian Griebler26 Stuart Halse27
Hannelore Hoch28 Enock Kale29 Aron D. Katz30 Ľubomír Kováč31
Thomas M. Lilley3Shirish Manchi32 Raoul Manenti33 Alejandro Martínez4
Melissa B. Meierhofer3Ana Z. Miller34 Oana Teodora Moldovan35
Matthew L. Niemiller36 Stewart B. Peck37 Thais Giovannini Pellegrini5
Tanja Pipan38 Charity M. Phillips-Lander39 Celso Poot40 Paul A. Racey41
Alberto Sendra42,43 William A. Shear44 Marconi Souza Silva5Stefano Taiti45
Mingyi Tian46 Michael P. Venarsky47 Sebastián Yancovic Pakarati48,49,50
Maja Zagmajster23 Yahui Zhao51
Department of Biological Sciences, Center for Adaptable Western Landscapes, Northern Arizona University, Flagstaff, Arizona
Hawaii Biological Survey, Bishop Museum, Honolulu, Hawaii
Finnish Museum of Natural History Luomus, University of Helsinki, Helsinki, Finland
DarkMEG—Molecular Ecology Group, Water Research Institute, National Research Council of Italy, Verbania Pallanza, Italy
Centro de Estudos em Biologia Subterrânea, Setor de Biodiversidade Subterrânea, Departamento de Ecologia e Conservação, Universidade Federal de
Lavras, Minas Gerais, Brazil
Research Institute on Terrestrial Ecosystem of the Italian National Research Council, Florence, Italy
Department of Life, Health & Environmental Sciences, University of L’Aquila, L’Aquila, Italy
Instituto de Ecologia, Universidad Nacional Autónoma de México, México
Wildlife Conservation Society, Bronx Zoo, Bronx, NY (Ret.) and Bat Sound Services, Canadian Lakes, Michigan
 Departamento de Ecología e Hidrología, Universidad de Murcia, Murcia, Spain
 Laboratório de Estudos Subterrâneos, Departamento de Ecologia e Biologia Evolutiva, Universidade Federal de São Carlos, São Carlos, São Paulo,
Brazil
 National Cave Research and Protection Organization, Raipur, Chhattisgarh, India
 Department of Geosciences, Eastern Kentucky University, Richmond, Kentucky
This is an open access article under the terms of the Creative Commons Attribution License, which permits use, distribution and reproduction in any medium, provided the
original work is properly cited.
©  The Authors. Conservation Letters published by Wiley Periodicals LLC
Conservation Letters. ;:e. wileyonlinelibrary.com/journal/conl 1of6
https://doi.org/./conl.
2of6 WYNNE  .
 School of Biology, Nakhon Ratchasima Rajabhat University, Nakhon Ratchasima, Thailand
 Centre for Ecology, Evolution and Environmental Changes/Azorean Biodiversity Group and Universidade dos Açores, Faculty of Agrarian and
Environmental Sciences, Azores, Portugal
 NASA Ames Research Center, Moffett Field, California
 Runaway Creek Nature Reserve, Belmopan, Belize
 Department of Biological Sciences, Faculty of Science, Thompson Rivers University, Kamloops, British Columbia, Canada
 Museum National d’Histoire Naturelle, Paris, France
 IFREMER Centre Atlantique, Unité Ecologie et Modèles pour l’Halieutique, Nantes, France
 Stuttgart State Museum of Natural History, Stuttgart, Germany
 Center for Conservation and Research, San Antonio Zoo, San Antonio, Texas
 SubBio Lab, Department of Biology, Biotechnical Faculty, University of Ljubljana, Slovenia
 The Nature Conservancy, Honolulu, Hawaii
 Department of Environment, Isfahan University of Technology, Isfahan, Iran
 Department of Functional and Evolutionary Ecology, Division of Limnology, University of Vienna, Vienna, Austria
 Bennelongia Environmental Consultants, Perth, Australia
 Department Center for Integrative Biodiversity Discovery, Museum für Naturkunde, Leibniz Institute for Research on Evolution and Biodiversity,
Berlin, Germany
 Ecomate Management Ltd., Boroko, NCD, Papua New Guinea
 Engineer Research and Development Center, U.S. Army Corps of Engineers, Champaign, Illinois
 Department of Zoology, Institute of Biology and Ecology, P.J. Šafárik University, Košice, Slovakia
 Conservation Ecology Division, Salim Ali Centre for Ornithology and Natural History, Coimbatore, India
 Department of Environmental Science and Policy, Università degli Studi di Milano, Milan, Italy
 Laboratório HERCULES, University of Évora, Évora, Portugal and Instituto de Recursos Naturales y Agrobiología de Sevilla, Consejo Superior de
Investigaciones Científicas, Seville, Spain
 Emil Racovita Institute of Speleology, Cluj-Napoca Department, Cluj-Napoca, Romania
 Department of Biological Sciences, The University of Alabama in Huntsville, Huntsville, Alabama
 Canadian Museum of Nature, Ottawa, Ontario, Canada
 ZRC SAZU Karst Research Institute, Ljubljana, Slovenia and UNESCO Chair on Karst Education, University of Nova Gorica, Vipava, Slovenia
 Space Science and Engineering Division, Southwest Research Institute, San Antonio, Texas
 The Belize Zoo and Tropical Education Center, Belmopan, Belize and School of Natural Resources and Environment, University of Florida,
Gainesville, Florida
 Centre for Ecology and Conservation, University of Exeter, UK
 Colecciones Entomológicas Torres-Sala, Servei de Patrimoni Històric, Ajuntament de València, València, Spain
 Departament de Didàctica de les Cièncias Experimentals i Socials, Facultat de Magisteri, Universitat de València, València, Spain
 Department of Biology, Hampden-Sydney College, Hampden Sydney, Virginia
 Istituto di Ricerca sugli Ecosistemi Terrestri CNR-IRET, Museo di Storia Naturale, Sezione di Zoologia, Firenze, Italy
 Department of Entomology, College of Plant Protection, South China Agricultural University, Guangzhou, China
 Department of Biodiversity Conservation and Attractions, Government of Western Australia, Washington, Kensington, Australia
 Laboratorio de Socioecosistemas, Departamento de Ecología, Universidad Autónoma de Madrid, Madrid, Spain
 Consejo Asesor de Monumentos Nacionales de Chile - Rapa Nui, Chile
 Manu Project, Rapa Nui, Chile
 Key Laboratory of Zoological Systematics and Evolution, Institute of Zoology, Chinese Academy of Sciences, Beijing, China
Correspondence
J. Judson Wynne,Department of Biological
Sciences, Center for Adaptable Western
Landscapes, Northern Arizona University,
Flagstaff, AZ .
Email: jut.wynne@nau.edu
Abstract
The th UN Convention on Biological Diversity (CBD) (COP) will be held
in Kunming, China in October . Historically, CBDs and other multilat-
eral treaties have either alluded to or entirely overlooked the subterranean
biome. A multilateral effort to robustly examine, monitor, and incorporate the
WYNNE  . 3of6
subterranean biome into future conservation targets will enable the CBD to fur-
ther improve the ecological effectiveness of protected areas by including ground-
water resources, subterranean ecosystem services, and the profoundly endemic
subsurface biodiversity. To this end, we proffer a conservation roadmap that
embodies five conceptual areas: () science gaps and data management needs; ()
anthropogenic stressors; () socioeconomic analysis and conflict resolution; ()
environmental education; and () national policies and multilateral agreements.
KEYWORDS
biodiversity, caves, convention on biological diversity, hypogean, indicator species
The th UN Convention on Biological Diversity (CBD)
(COP) (UNEP, )willbeheldinKunming,China
in October . Historically, CBDs and other multi-
lateral treaties have either alluded to or entirely over-
looked the subterranean biome (Sánchez-Fernández et al.,
). Importantly, while the post- global biodiver-
sity framework (IUCN, ) briefly mentioned subter-
ranean ecosystems, the need for an effective protected area
network to safeguard biodiversity, freshwater, and ecosys-
tem services had been strenuously and broadly empha-
sized. Globally, only % of the modeled extent of the sub-
terranean biome overlaps with protected areas (Sánchez-
Fernández et al., ).
As the upcoming CBD meeting will be held in the
South China Karst, a region supporting the highest diver-
sity of subterranean-adapted fishes, beetles, and millipedes
globally (and likely to emerge as a subterranean biodi-
versity hotspot), we provide this roadmap for conserving
the world’s subterranean resources. Through a multilateral
effort to robustly examine, monitor, and incorporate the
subterranean biome into future conservation targets, the
CBD will further improve the ecological effectiveness of
protected areas by including groundwater resources, sub-
terranean ecosystem services, and the profoundly endemic
subsurface biodiversity (Elshall et al., ; Mammola
et al., ,). To this end, this roadmap embodies
five conceptual areas: () science gaps and data man-
agement needs; () anthropogenic stressors; () socioeco-
nomic analysis and conflict resolution; () environmen-
tal education; and () national policies and multilateral
agreements.
Perhaps even more than surface ecosystems, the terres-
trial subterranean biome is riddled by extensive knowl-
edgegaps(Box,Figure). For example, for most known
subterranean-obligate species, we have little more than
observational data from a few human-accessible locali-
ties (Mammola et al., ,); this makes assessing
species for protective management extremely challenging.
While the importance of ecosystem services associated
with groundwater quality and cave-roosting bats is rela-
tively well-documented (Elshall et al., ; Griebler et al.,
; Mammola et al., ), a substantial effort will be
required to quantify the scope, importance, and habitat
requirements of subterranean bioindicator and ecosystem
service species (Elshall et al., ).
Natural history information on the subterranean biome
lags equally behind. Data deficiencies to be addressed
should include developing a network of voucher speci-
men collections available both in brick-and-mortar loca-
tions and as digital archives. Additionally, the creation or
adoption of an array of digital archives, tantamount to
the World Karst Spring hydrograph database (Olarinoye
et al., ), will provide conservationists and resource
managers with the data to identify research needs and fos-
ter international and interdisciplinary collaborations. Such
archives must house information on the geospatial extent
of subterranean habitats, reference barcode/genetic and
functional trait data on subterranean species, and syner-
gistically contribute to or augment existing archives (Frick
et al., ) (e.g., GBIF, iDigBio, and BoldSystems).
Although researchers have qualitatively summarized
most of the likely anthropogenic stressors threatening sub-
terranean biodiversity and ecosystem function (Box )
(Elshall et al., ; Griebler et al., ; Leclère et al.,
; Mammola et al., ), their potential impacts have
not been quantified (Mammola et al., ). Strategically
focused, global studies to examine key impacts (in par-
ticular, surface habitat loss) (Hedrick et al., ) should
be conducted across a range of subterranean habitats, a
panoply of associated indicators, and ecosystem service
and short-range endemic species. Through such a coordi-
nated effort, researchers and policymakers can amass the
information required to develop mitigation strategies to
optimize decision-making.
Solutions (Box ) will require scientists and legisla-
tors to work closely with local communities and munic-
ipalities to both ameliorate future land-use disputes and
to find sustainable and economically viable pathways
4of6 WYNNE  .
FIGURE 1 Conservation roadmap flows from addressing data gaps and data management needs (green ovals with callout box) to policy
development and implementation (blue). Data acquisition and management moves in two directions: () toward a feedback loop of
monitoring, adaptive management, and local resource policy development with monitoring and management iteratively improved as
scientific data dictates; and () to providing information necessary to create educational outreach programs (yellow), which are further
sculpted by human activities (red). Socio-economic analyses (purple) aim to both characterize and lessen anthropogenic impacts and
stressors. This information then feeds into local resource management formulation; national policy and multilateral agreements are both
shaped and influenced by local decision-making
forward. Importantly, % of humans rely on groundwater
for consumption, while % use it for agricultural purposes
(Elshall et al., ). As we increasingly convert natural
ecosystems to agriculture, pastureland, and human habita-
tion, surface biodiversity, and ecosystem function (Gibson
et al., ), as well as aquifers and other groundwater habi-
tats will become increasingly threatened and degraded. To
maximize effectiveness and reduce conservation conflicts,
improved dialog between social and natural scientists must
occur so that social, political, and scientific contexts are
well articulated, and stakeholders can negotiate with com-
plete transparency (Gibson et al., ).
WYNNE  . 5of6
Successful environmental and conservation education
programs (Box ) should be crafted to: (i) address local
problems/topics; (ii) establish partnerships and programs
with local researchers and resource managers; (iii) empha-
size action focused projects (e.g., ecological restoration,
cave cleanups, and monitoring bioindicators and bat/bird
roosts); and (iv) create targeted projects that quantify
and report program outcomes (Redpath et al., ).
Educational efforts must be established in partnership
with local schools and universities, scientific organiza-
tions, indigenous and community groups, businesses, non-
governmental organizations, and government agencies.
Conservation policies (Box ) to protect significant
subterranean habitats are lacking at most regional and
national levels (Mammola et al., ). However, poli-
cies have been implemented to better manage local and
regional groundwater resources (Elshall et al., ).
Barring the European Union’s Habitat Directive (which
marginally considers subterranean habitats; EU, ), no
multilateral agreements have been adopted to specifically
include the subterranean biome (Sánchez-Fernández et al.,
). Solidly integrating surface with subsurface con-
servation targets through equitable stakeholder participa-
tion represents a foundational next step toward optimally
securing the groundwater supply (Elshall et al., ), safe-
guarding ecosystem services (Frick et al., ; Mammola
et al., ), and protecting subterranean diversity.
While numerous lacunae exist concerning subterranean
resources, sound directives can be enacted promptly with
adaptive management. This roadmap represents a viable
framework for near-term and longer duration conserva-
tion actions to protect the world’s subterranean ecosys-
tems. Formulating targets to further reduce threats to the
subterranean biome is essential to this year’s CBD meeting
in Kunming. We must act now.
AUTHOR CONTRIBUTIONS
J. Judson Wynne and Stefano Mammola conceived the
project. Francis Howarth developed the initial roadmap.
All other authors contributed to roadmap development
and finalization.
ETHICS STATEMENT
No data collection or scientific inquiries requiring ethics
considerations were undertaken. Thus, this work complies
with appropriate ethical standards.
DATA ACCESSIBILITY STATEMENT
We did not collect any primary data to develop this
manuscript. All references that aided in refining our posi-
tions are provided.
CONFLICT OF INTEREST
We declare no conflict of interest with this work.
ORCID
J. Judson Wynne https://orcid.org/---

Stefano Mammola https://orcid.org/---

Diana M. P. Galassi https://orcid.org/---

David Sánchez-Fernández https://orcid.org/--
-
Maria Elina Bichuette https://orcid.org/--
-
Jayant Biswas https://orcid.org/---
Cory W. BlackEagle https://orcid.org/---

Chaichat Boonyanusith https://orcid.org/--
-
Isabel R. Amorim https://orcid.org/---

David Eme https://orcid.org/---
Samuel M. ʻOhukaniʻ¯
ohiʻa Gon III https://orcid.org/
---
Ľubomír Kováč https://orcid.org/---
Thais Giovannini Pellegrini https://orcid.org/-
--
Stefano Taiti https://orcid.org/---
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... We currently have a limited quantitative understanding of population trends for subterranean insects and the threats affecting them (Mammola et al. 2019aWynne et al. 2021). Large-scale studies and long historical data series are missing, and our knowledge is biased in its geographic and taxonomic coverage (Nanni et al. 2023). ...
... Large-scale studies and long historical data series are missing, and our knowledge is biased in its geographic and taxonomic coverage (Nanni et al. 2023). As global monitoring programmes for insects are exceedingly rare (Cardoso et al. 2020), let alone for subterranean species (Wynne et al. 2021), it has been suggested that expert opinion may be the only valuable tool for understanding current threats until hard data becomes available (Fitzgerald et al. 2021;Miličić et al. 2021). Concerning subterranean insects, experts agree that the most significant threats to subterranean invertebrates are land use change at the surface, pollution, and partly climate change, poaching, and diseases ( Figure 24.3A). ...
... Inevitably, this chapter has been speculative in the discussion of threats and conservation measures, a direct consequence of the fact that cave and other subterranean environments are some of the least studied ecosystems on the planet Nanni et al. 2023). Thus, to make evidence-based decisions for the conservation of subterranean insects there is an urgent need to accelerate basic scientific research to document subterranean diversity, explore the abiotic and biotic factors that drive its distribution patterns across space and time, as well as establish effective monitoring programmes (Wynne et al. 2021;Box 24.2). Such basic knowledge is central to inform and support practical conservation, but also to conduct extinction risk assessments (Borges et al. 2019), to define conservation priorities given a scenario of limited resources invested in ...
Chapter
This chapter addresses the multiple threats faced by subterranean insects and their conservation. Subterranean insects are intrinsically vulnerable to anthropogenic threats due to their small distribution ranges, small population size, restricted habitat, and limited physiological and behavioural plasticities. Although we lack a quantitative understanding of population trends and long-term series of data, experts agree that habitat modification at the surface and climate changes are the most pervasive threats that may negatively affect subterranean insects. Beyond acquiring basic knowledge about subterranean insects and establishing monitoring programmes, their future conservation will be best achieved by (i) expanding protected areas’ coverage of global hotspot of subterranean diversity; and (ii) increasing awareness about subterranean insects and the important nature’s contribution they provide to people.
... In Europe, a latitudinal cave and groundwater fauna "biodiversity ridge" has been observed between approx. 42° N and 47° N, where both metazoan biodiversity and the number of known biodiversity hotspots is comparatively high (Culver & Sket 2000;Culver et al. 2006;Deharveng et al. 2009;Eme et al. 2017;Pipan et al. 2021;Zagmajster et al. 2023). This pattern reflects the maximum extent of glaciations during the last ice ages (Riss/Würm ice age), during which most aquatic species living in glaciated areas either became extinct, sought refuge in groundwater habitats or migrated southwards (Thienemann 1950;Culver et al. 2006). ...
... In parallel, species extinction risk should be assessed and threshold values for anthropogenic stressors defined to provide guidelines for the sustainable use of groundwater. Finally, an integrative groundwater management strategy should be implemented based on biological and ecological criteria and anchored in national and international legal frameworks (Wynne et al. 2021;Griebler et al. 2023a). This should specifically include standardized monitoring and sampling methods and guidelines for sustainable groundwater use (Ferreira et al. 2022). ...
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... Groundwater ecosystems harbour essential water resources for many people and other dependent ecosystems around the globe [1], yet the rare and mostly endemic species which are restricted to these environments are poorly understood, and consistently overlooked in management strategies [2][3][4]. Impacts of rapid climate change and anthropogenic activities that induce modifications in the physicochemical parameters of the environment (i.e. temperature, salinity and oxygen) are expected to affect groundwater communities [5][6][7][8][9], however, the impacts of these changes on groundwater species vary among species and the particular environmental change itself, which makes accurate projections for the future very difficult [4,6,[10][11][12][13]. ...
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Anchialine systems are coastal groundwater habitats around the world which host a unique community of cave adapted species (stygobionts). Such communities are expected to be separated by haloclines into either fresh or saline groundwater communities, hence climate changes (e.g., eustatic sea level shifts) and anthropic driven changes (e.g., salinization) may have a great impact on these stygobiont communities. Here we used cave-restricted species of Typhlatya from the Yucatan Peninsula as models to identify physiological capacities that enable the different species to thrive in marine groundwater (T. dzilamensis) or fresh groundwater (T. mitchelli and T. pearsei), and test if their distribution is limited by their salinity tolerance capacity. We used behavior, metabolic rates, indicators of the antioxidant system and cellular damage, and lactate content to evaluate the response of individuals to acute changes in salinity, as a recreation of crossing a halocline in the anchialine systems of the Yucatan Peninsula. Our results show that despite being sister species, some are restricted to the freshwater portion of the groundwater, while others appear to be euryhaline.
... Troglobitic species are characterized by their remarkable sensitivity and high degree of endemism (Wynne et al. 2021). It is common to find examples of troglobitic cixiids that are confined to a single cave, as evidenced by previous studies (e.g., Fennah 1975;D'Urso & Grasso 2009;Hoch & Ferreira 2012;Hoch 2013;Le Cesne et al. 2022). ...
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Notolathrus sensitivus holds the distinction of being the first cave-restricted planthopper species documented in South America, and currently stands as the sole known troglobitic Fulgoromorpha species in Argentina. This paper presents a comprehensive supplementary description of N. sensitivus, incorporating newly collected male and female specimens. Notably, this study provides the first-ever description of females for this species. In addition to photographs of structural details, we include images showcasing live specimens within their natural habitat. Furthermore, we highlight the primary threats that pose risks to the species’ survival. Based on these significant findings, we strongly advocate for the inclusion of N. sensitivus on the Argentine endangered species list, emphasizing the urgent need for conservation measures.
... Conserving caves is a challenge even in protected areas (Bejec et al., 2020). In fact, subterraneans ecosystems are among the most fragile, neglected and threatened in the world (Mammola et al., 2019;Sánchez-Fernández et al., 2021;Tanalgo et al., 2018;Trajano et al., 2016;Wynne et al., 2021). Therefore, regardless of the priority indicated by the BCVI, we believe that all the caves studied are important and unique, requiring urgent interventions to define priority areas for conservation, actions to strengthen and maintain protected areas and regulate anthropic activities in the region. ...
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The Carajás region is home to the largest number of iron caves in Brazil, but studies that integrate elements of biological diversity and landscape characteristics are scarce. We present the first study based on the bat cave vulnerability index (BCVI), which uses bats as a key species for prioritizing caves in South America, whose objective was to assess the biotic potential and vulnerability of caves in the Carajás region, determining priority sites and the most effective conservation actions. The study took place from August 2021 to March 2023, where an inventory of the chiropterofauna of 12 caves was carried out. We recorded 16 bat species, two of which are vulnerable to extinction – Furipterus horrens (Cuvier, 1828) and Natalus macrourus (Gervais, 1856) – and two endemics to the Amazon region – Hsunycteris aff. thomasi (Allen, 1904) and Phyllostomus latifolius (Thomas, 1901); as well as one species with insufficient data to delimit its endemicity or threat status (Lonchophyllinae sp.). Mining is the main anthropogenic activity in the region, but tourism is also present and acts as a potential source of disturbance to the caves. The BCVI revealed three high priority caves for conservation and four with medium priority, indicating that these habitats are vulnerable to species loss and population decline due to exposure to anthropogenic activities and habitat destruction, thus requiring more effective conservation strategies. Considering the uniqueness of the subterranean habitats, we recommend re‐evaluating the proposals for expanding mining activities, implementing controlled tourist visitation plans and conducting ecological studies and long‐term monitoring.
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