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Revista Cubana de Ciencias Forestales

versión On-line ISSN 2310-3469

Rev CFORES vol.12 no.3 Pinar del Río sept.-dic. 2024  Epub 01-Sep-2024

 

Original article

Information and tourist use of terrestrial mammals

0000-0002-8596-5121Sonia Rosete Blandariz1  *  , 0000-0002-8006-0825Romina Stephania Saénz Veliz1  , 0000-0002-9674-3591Yumileika Sulay Quimis Lascano1  , 0000-0001-5914-5720Héctor Simón Pinargote Velez1 

1Universidad Estatal del Sur de Manabí, Ecuador

ABSTRACT

The cultural relevance of terrestrial mammals in driving wildlife tourism is addressed by assessing their cultural value and importance to local communities. This study aimed to record the knowledge and tourist use of terrestrial mammals in Jipijapa, Manabí, Ecuador. Surveys were conducted among local residents and experts to collect the mammals and their uses, followed by calculating the importance value of each species. The results revealed the presence of 52 mammal species, most of them threatened. The uses were education and awareness (86 mentions), wildlife observation (81), photo hunting tourism (80), ecotourism (74), adventure tourism (73) and theme park attractions (22). The species of greatest importance and cultural value are Ateles fusciceps, Bradypus variegatus, Desmodus rotundus, Didelphis marsupialis, Glyphonycteris daviesi, Lycalopex sechurae, Nasua narica, Simosciurus stramineus, Tamandua mexicana and Vampyrum spectrum, associated with cultural landscapes. This ethnozoological approach provides a solid basis for the planning and analysis of tourism activities focused on local fauna, which contributes to the conservation of biodiversity and the sustainable development of the region.

Key words: ethnozoology; informant consensus factor; relative citation frequency; relative importance; cultural value.

INTRODUCTION

Ethnozoological studies are fundamental to understanding bioecology and sociocultural links between humans and animals (Nóbrega et al., 2018). Through them, it is possible to identify and understand the use of wildlife for various purposes, such as food, traditional medicine, trade, religion, culture and tourism. Wildlife tourism has emerged as a growing industry, with an increasing demand for authentic and sustainable experiences that allow visitors to connect with nature (Sthapit et al., 2024).

Terrestrial mammals play a crucial role in this type of tourism due to their cultural and ecological appeal. Their presence not only contributes to biodiversity, but also has a deep symbolic and emotional value in diverse cultures around the world.

In many cultures, land mammals are seen as symbols of strength, freedom and wisdom. For example, elephants in Africa are not only a pillar of the ecosystem, but are also respected in many local cultures for their intelligence and longevity, making them a key attraction for tourists seeking a deeper connection with the natural and cultural environment (Blake et al., 2008).

The appeal of land mammals is also reflected in the economy. Gidebo (2023) pointed that wildlife tourism represents a significant source of income for many developing countries, providing employment and promoting natural habitat conservation. Furthermore, the experience of observing mammals in their natural environment offers tourists a unique opportunity for education and awareness about the importance of conserving endangered species (Duffus and Dearden, 1990).

Despite the relevance of terrestrial mammals, their integration into tourism programs is not always easy, due to the complex relationship between these animals and human cultures. This study focuses on documenting the knowledge and tourist use of terrestrial mammals in Jipijapa, Manabí, Ecuador. The findings will contribute to the formulation of conscious tourism strategies that value the cultural heritage linked to these species, promote the conservation of biological diversity and generate income for local communities.

MATERIALS AND METHODS

Area of study

The study was carried out in the Jipijapa canton, Manabí, coastal region of Ecuador. Its territorial extension is 1,419.086 km and it is located at the geographic coordinates 1°20'00''S and 80°35'00''W. It is limited to the north by the Montecristi, Portoviejo and Santa Ana cantons; to the south by the Guayas Province and the Puerto López Canton, to the east by the Paján and 24 de Mayo Cantons and to the west by the Pacific Ocean. Jipijapa has a human population of 78,117, where the majority is mestizo (73.1 %) and montubia (24.5 %).

Ethics statement

All participants were informed about the purpose of the study and their oral, free, prior and informed consent to interview, record, photograph and/or publish their knowledge was obtained at the beginning of each interview. All interviews were in accordance with the Code of Ethics of the International Society of Ethnobiology (ISBE, 2008. Considering also the obligations of the Nagoya Protocol, it was approved that "the right of use and ownership of any traditional knowledge of all informants remains with them, and that any use of the information, except for scientific publication, requires the additional consent of the traditional owners and consensus on access to the benefits derived from its possible further use" (Convention on Biological Diversity, 2011).

Data collection

This study combines ethnozoological data, zoological data on mammals (Brito et al., 2023) and conservation information (IUCN, 2024). Ethnozoological data on tourism use of terrestrial mammals were collected between May 2022 and January 2024 through semi-structured interviews. The sampling process was purposive and participants were selected because they could provide relevant information for this study. Of the 100 experts identified as having knowledge of the species and working in the tourism sector, six agreed to participate in this study in greater depth.

At the beginning of each interview, participants were given a brief description of wild terrestrial mammals, beginning with the importance of conducting their study in the area and their use in tourism. They were told that these are animals such as foxes, armadillos, bats, monkeys, mice, and opossums, and that we wanted to know what mammals they had seen in the area. After the introduction, participants were asked to comment on the points about terrestrial mammals that immediately came to mind (~15 min). Next, they were shown photos of mammals and asked to identify vernacular names and usage (~45 min). Information about wild terrestrial mammals was documented, specifically with data on (1) their popular names, (2) where they can be found most easily, and (3) tourist uses. In addition, observations were made and photographs were taken at relevant locations, whenever possible to document unmentioned uses and also to observe ethnozoological practices. Depending on the weather and the willingness of the participants, a "walk through the area" was conducted to observe the species (~45 min). To confirm previous information and gain more knowledge about various mammals, participants were shown an illustrated catalogue of mammals (Brito et al., 2023), which included the species of the region (~45 min). Some participants were visited a second time to complete the first interview or to confirm information. The illustrated catalogue of mammals (Brito et al., 2023) was used to identify species. Species were not collected.

Data analysis

For data analysis, all reported species and their relevant ethnozoological data (potential use in tourism) were entered into a Microsoft® Excel spreadsheet in a report-of-use (UR) order, following the categories of the ethnozoological data collection standard (Terrance, 2014). Six broad tourism use categories were determined for several emic subcategories (MOSTOWLANSKY and ROTA, 2020) (Table 1). For example, the "wildlife observation" category reflects the knowledge and perception of local communities regarding these species, including cultural or religious uses (mammals that have a symbolic, cultural or religious meaning for the community), impact of mammals on agriculture and livestock (perceptions about how terrestrial mammals affect agricultural and livestock activities), myths and legends (local stories, beliefs and legends involving terrestrial mammals), as well as dangers and precautions (knowledge about the dangers associated with certain terrestrial mammals and the precautions to be taken) among others.

Table 1.  - Categories of tourist uses assigned for tourist activities 

Categories (Codes) Description of tourist activities
Theme Park Attractions (APT) Theme Park attractions offer recreational and educational experiences in environments that replicate natural habitats, allowing for the safe observation of terrestrial mammals. These facilities promote wildlife awareness and conservation through interactive programs and educational activities, contributing to local economic development and the preservation of biodiversity.
Ecotourism (ECT) Ecotourism is a form of sustainable tourism that allows visitors to explore and enjoy natural areas, focusing on the observation and conservation of terrestrial mammals. It promotes respect for the environment and local cultures, educating tourists about the importance of preserving biodiversity.
Education and awareness raising (ESD) Education and awareness-raising in the context of wildlife tourism refers to activities designed to inform and raise awareness among visitors about the importance of conserving terrestrial mammals and their habitats. These activities include talks, workshops and interactive programs that highlight the ecological and cultural value of these species, encouraging responsible attitudes and behaviors toward nature.
Wildlife Observation (WVO) Wildlife watching is a tourist activity that allows visitors to see and study terrestrial mammals in their natural habitat. This practice promotes the appreciation and conservation of local fauna, offering an educational and recreational experience that enhances the value of ecosystems and fosters respect for biodiversity.
Adventure tourism (TAV) Adventure tourism is a type of tourism that offers exciting and challenging experiences in natural environments. Focused on activities like hiking. Climbing, and exploring terrestrial mammal habitats, this type of tourism promotes connection with nature and biodiversity conservation, while providing visitors with a unique and stimulating experience.
Photo Hunting Tourism (TCF) Photo hunting tourism is an activity where visitors seek to capture images of terrestrial mammals and other species in their natural environment, without causing harm or disturbing the animals. This practice promotes respect for wildlife and conservation, providing an exciting and educational experience that contributes to the appreciation and protection of natural ecosystems.

ethnobotanyR package (Whitney, 2022) was used within the R environment. The basic values of Citation Frequency (CF), Number of Uses Reports (UR), Number of Uses (NU), as well as the Cultural Importance (CI), Relative Citation Frequency (RFC), Relative Importance (RI) and Cultural Value (CV) indices were obtained (Tardio and Pardo-de-Santayana, 2008).

RESULTS AND DISCUSSION

A total of 52 species of terrestrial mammals were inventoried in the rural area of Jipijapa canton, Ecuador (Table 1). One endemic species (Simosciurus stramineus). According to the IUCN status (2024), 49 species are at risk of extinction (94.2 %). Ateles fusciceps was listed as critically endangered (CR); Heteromys teleus has been classified as endangered (EN), while Caluromys derbianus, Lichonycteris obscura, Lycalopex sechurae and Sigmodontomys Alfari were assessed as Vulnerable (VU). Forty species have been assessed in the less threatened group described as Least Concern (LC), these include Bradypus variegatus, Didelphis marsupialis, Marmosa simonsi, Nasua nose, Philander melanurus, Simosciurus stramineus, Syntheosciurus granatensis and Mexican Tamandua.

According to the results obtained, all these species are closely linked to cultural landscapes, i.e. areas transformed by human intervention, which adds a unique component to their study. Agricultural expansion, driven mainly by the cultivation of corn and other short-cycle species, constitutes the most significant threat to the mammal population in the area. In addition to this pressure on the habitat, other worrying threats were identified, such as the overexploitation of species for the manufacture of artisanal objects with their skin (Syntheosciurus granatensi), the persecution of species considered harmful, such as some mice (Aegialomys xantheolus) and bats (Vampyressa thyone), poisoning (Philander melanurus), mortality caused by human-made equipment and disruptions caused by climate change.

Despite the wide distribution of these terrestrial mammals in the country (de la Torre et al., 2012; Barros-Diaz et al., 2023), they face many dangers, the most important being death on the roads, in addition to urban expansion in rural areas, which threatens their natural habitat, in addition to the lack or absence of rainfall in the coastal region of Ecuador. This list reflects the diversity of mammals in the area, and highlights the importance of implementing conservation measures, especially for Ateles fusciceps and Heteromys teleus which are in the most threatened categories according to the IUCN (2024).

Terrestrial mammals have different tourist uses, among the most reported we have: education and awareness (48 species), photographic hunting tourism (48), adventure tourism (47), wildlife observation (46), ecotourism (42) and attractions in theme parks (10) (Table 2). These results show the experiential, social, functional, financial and spiritual motivations for the use of wildlife (Thomas-Walters et al., 2021).

Table 2.  - List of mammal species from Jipijapa, Manabí, Ecuador. Endemism. Uses.APT - Theme Park Attractions, ECT - Ecotourism, EDS - Education and Awareness Raising, OVS - Wildlife Observation, TAV - Adventure Tourism, TCF - Photographic Hunting Tourism 

Scientific name Threat Category Uses
Aegialomys xantheolus (Thomas, 1894) Least Concern ECT, EDS, OVS, TAV, TCF
Artibeus aequatorialis (Larsen et al. 2010) Least Concern ECT, EDS, OVS, TAV, TCF
Artibeus fraterculus (Anthony, 1924) Insufficient data ECT, EDS, OVS, TAV, TCF
Ateles fusciceps (Gray, 1866) Critical danger APT, ECT, EDS, OVS, TAV, TCF
Bradypus variegatus (Schinz , 1825) Least Concern ECT, EDS, OVS, TAV, TCF
Caluromys derbianus (Waterhouse, 1841) Vulnerable APT, EDS, OVS
Carollia brevicaudum (Schinz , 1821) Least Concern EDS, TAV, TCF
Carollia perspicillata (Linnaeus , 1758) Least Concern EDS, OVS, TAV, TCF
Centronycteris (Thomas, 1912) Least Concern EDS, TAV, TCF
Chiroderma villosum (Peters, 1860) Least Concern EDS, OVS, TAV, TCF
Chironectes minimus (Zimmermann, 1780) Near Threatened APT, EDS, OVS, TCF
Desmodus rotundus (Geoffroy, 1810) Least Concern ECT, EDS, OVS, TAV, TCF
Diclidurus albus Wied-Neuwied , 1820 Least Concern ECT, EDS, OVS, TCF
Didelphis marsupialis (Linnaeus , 1758) Least Concern APT, ECT, EDS, OVS, TAV, TCF
Gardnerycteris crenulatum (Geoffroy, 1803) Least Concern ECT, OVS, TAV, TCF
Glossophaga soricin (Pallas, 1766) Least Concern ECT, EDS, OVS, TAV, TCF
Glyphonycteris daviesi (Hill, 1964). Insufficient data ECT, EDS, OVS, TAV, TCF
Handleyomys Alfaroi (Allen, 1891) Least Concern ECT, EDS, OVS, TAV, TCF
Heteromys teleus (Anderson and Jarrin, 2002) Endangered ECT, EDS, OVS, TAV, TCF
Lichonycteris obscura (Thomas, 1895) Vulnerable EDS, OVS, TAV, TCF
Lonchophylla concave (Goldman, 1914) Least Concern ECT, EDS, OVS, TAV, TCF
Lonchophylla robusta (Miller, 1912) Least Concern ECT, OVS, TAV, TCF
Lonchorhina aurita (Tomes, 1863) Least Concern ECT, EDS, OVS, TAV, TCF
Lycalopex sechurae (Thomas, 1900) Vulnerable APT, ECT, EDS, OVS, TAV, TCF
Marmosa simonsi (Thomas, 1899) Least Concern ECT, EDS, OVS, TAV, TCF
Melanomys caliginosus (Tomes, 1860) Least Concern ECT, EDS, OVS, TAV, TCF
Micronycteris hirsuta (Peters, 1869) Least Concern ECT, OVS, TAV, TCF
Micronycteris megalotis (Gray, 1842) Least Concern EDS, OVS, TAV, TCF
Molossus molossus (Pallas, 1766) Least Concern ECT, OVS, TAV, TCF
Myotis nigricans (Schinz , 1821) Least Concern ECT, EDS, OVS, TAV, TCF
Myotis riparius (Handley, 1960) Least Concern ECT, EDS, OVS, TAV
Nasua nose (Linnaeus , 1766) Least Concern ECT, EDS, OVS, TAV, TCF
Nyctinomops macrotis (Gray, 1839) Least Concern ECT, EDS, TAV
Oecomys bicolor (Tomes, 1860) Least Concern ECT, EDS, OVS, TAV, TCF
Philander melanurus (Thomas, 1899) Least Concern APT, EDS, OVS
Phyllostomus discoloured (Wagner, 1843) Least Concern OVS, TAV, TCF
Platyrrhinus umbratus (Lyon, 1902) Least Concern ECT, EDS, TCF
Proechimys decumanus (Thomas, 1899) Least Concern ECT, EDS, OVS, TAV, TCF
Proechimys semispinosus (Thomas, 1860) Least Concern ECT, EDS, OVS, TAV, TCF
Rhinophylla alethina (Handley, 1966) Insufficient data ECT, EDS, OVS, TAV, TCF
Sigmodon peruanus (Allen, 1897) Least Concern ECT, EDS, OVS, TAV, TCF
Sigmodontomys Alfari (Allen, 1897) Vulnerable ECT, EDS, TAV, TCF
Simosciurus stramineus (Eydoux and Souleyet, 1841) Least Concern APT, ECT, EDS, OVS, TAV, TCF
Sturnira bakeri (Velazco and Patterson, 2014) Not evaluated ECT, EDS, OVS, TAV, TCF
Sturnira luis (Davis, 1980) Least Concern ECT, EDS, TAV, TCF
Syntheosciurus granatensis (Humboldt, 1811) Least Concern APT, EDS, OVS, TCF
Mexican tamandua (Saussure, 1860) Least Concern ECT, EDS, OVS, TAV, TCF
Trachops cirrhosus (Spix , 1823) Least Concern ECT, EDS, TAV
Transandinomys bolivaris (Allen, 1901) Least Concern ECT, EDS, OVS, TAV, TCF
Transandinomys talamancae (Allen, 1891) Least Concern ECT, OVS, TCF,
Vampyressa thyone (Thomas, 1909) Least Concern ECT, EDS, OVS, TAV, TCF
Vampyrum spectrum (Linnaeus, 1758) Near Threatened APT, ECT, EDS, OVS, TAV, TCF

The results of the analysis of use reports, based on the frequency of citations by informants, revealed a total of 416 total use reports (URs), with the majority being in education and awareness (86 mentions), followed by wildlife observation (81), photo-hunting tourism (80), ecotourism (74), adventure tourism (73), and theme park attractions (22) (Table 3). Various studies have examined the impact of tourism on wildlife. In South America, the most common tourism uses have been observed to include education and awareness, wildlife observation, and photo-hunting tourism (Carlos and García-Londoño, 2023). These approaches not only provide exciting experiences for visitors, but also generate economic revenue and promote conservation. However, it is crucial to approach tourism sustainably to protect mammals and their natural environment.

Table 3.  - Number of use reports (UR) and percentage of use categories 

Categories (codes) UR Percentage
Education and awareness raising (ESD) 86 20.67
Wildlife Observation (WVO) 81 19.47
Photo Hunting Tourism (TCF) 80 19,23
Ecotourism (ECT) 74 17.79
Adventure tourism (TAV) 73 17.55
Theme Park Attractions (APT) 22 5.29
Total 416 100

The most commonly used category was Education and Awareness Raising (EDS), followed by Wildlife Observation (WVO) and Photographic Hunting Tourism (PHT) (Figure 1). Biodiversity and conservation education plays an essential role in raising awareness among tourists about the importance of protecting these species in their natural environment. This is in line with the educational value pointed out by Meng. et al. (2024), who identify the intrinsic and educational value of intangible cultural heritage as a key factor for the development of educational tourism. Furthermore, photographic hunting tourism is presented as an ethical alternative to physical hunting, promoting the responsible observation of species such as Chironectes minimus and Glyphonycteris daviesi, aligning with the sustainable tourism strategies proposed by Roblek et al. (2021).

Fig. 1.  - Distribution of species and their contribution to the use categories. The six (6) tourism activities (upper half) related to each of the 52 terrestrial mammal species (lower half) are shown. EDS = Education and awareness, OVS = Wildlife observation, TCF = Photographic hunting tourism, ECT = Ecotourism, TAV = Adventure tourism and APT= Theme Park attractions 

The species of greatest cultural importance (CI) and cultural value ( CV) is Vampyrum spectrum (CI = 4.167; CV = 4.167 ), followed by Ateles fusciceps (CI = 4.000; CV = 4.000 ), Tamandua mexicana (CI = 4.000; CV = 3.333 ), Lycalopex sechurae (CI = 3.833; CV = 3.833 ), Simosciurus stramineus (IC = 3,500; CV = 3,500 ), Desmodus rotundus (CI = 2,500; CV = 1,042 ), Bradypus variegatus (CI = 2.333; CV = 0.972), Didelphis marsupialis (CI = 2.167; CV = 1.083), Glyphonycteris daviesi (CI = 2.167; CV = 0.903) and Nasua nose (CI = 2.167; CV = 0.903 ) (Figure 2, Table 4). Each of these species has a cultural meaning that is reflected in legends, rituals and traditional uses, being key elements in the cultural identity and heritage of the communities.

Vampyrum spectrum, known as the spectral bat, is enigmatic and respected in Jipijapa, known for its size "larger than other bats" and rarity or "very scarce in the area". In the local culture, it is seen as a link between the earthly and spiritual world, acting as a messenger of supernatural forces. Its presence is associated with protection and fear, as it is believed to guard against evil spirits and announce significant changes. In cultural rituals, its guidance is invoked and its habitat is respected, recognizing its crucial role in both the ecosystem and the cultural heritage of the region. This cultural perception aligns with scientific documentation, such as the study by Pacheco-Figueroa et al. (2022), which first reported the species in Tabasco, Mexico, that highlight the importance of conservation and the need to protect its habitat from threats such as habitat loss and human interaction, topics also addressed by Saldaña-Vázquez et al. (2023), in this analysis of threats to bats in the Anthropocene. In addition, the first record of Vampyrum spectrum in Imbabura Province, Ecuador by Cueva et al. (2013) highlights the species' adaptation to diverse habitats and reinforces the need to integrate conservation with cultural respect for local fauna. This combination of cultural and scientific perspectives is crucial to understanding and preserving the ecological and cultural role of the spectral bat in different regions.

Ateles fusciceps plays a crucial role in the ecosystems of Jipijapa, Ecuador, mainly as a seed disperser. Its agility in moving between trees and consuming various fruits makes it an essential agent for the regeneration of tropical forests, contributing to the diversity and ecological health of its habitat. In addition to its ecological importance, this primate has a deep cultural meaning for Jipijapa communities, where it is seen as a symbol of freedom and connection with nature. Local legends consider it a protective spirit of the forest, capable of guiding travelers and predicting good harvests. This cultural perception coincides with that pointed out by Sánchez (2024), who states that Ateles fusciceps acts as a seed disperser over long distances, being perceived as a messenger of fertilization and vital activation in Andean-Amazonian representations. The protection and respect for this species in Jipijapa reflects an integration of its ecological and cultural role, where hunting is prohibited and its preservation is promoted as an integral part of local identity and cultural heritage.

For its part, Lycalopex sechurae is a symbol of cunning and survival in challenging environments. This canine has been the subject of numerous legends, and its presence in regional folklore makes it a species of cultural relevance. In addition, its ability to adapt to dry environments and its varied diet make it an important ecological regulator in its habitat (Stahl, 2012). While Simosciurus stramineus, is a species that has been integrated into the daily life of rural communities. Its presence is common in agricultural areas, where it is seen both as a charismatic animal and as a competitor for crops. Despite this, the species has a restricted distribution and is little studied (Lizcano et al., 2016).

The data showed significant differences in the species ranking obtained by the different established indices (Table 4). Although the first four species (Ateles fusciceps, Lycalopex sechurae, Simosciurus stramineus, Tamandua mexicana and Vampyrum spectrum) are the same in all, the order varies depending on the index chosen. The RI and CV indexes place Vampyrum spectrum in the first place because these two indices assign greater importance to the multiplicity of uses and the species was mentioned in a greater number of use categories (NU=6). However, Ateles fusciceps and Simosciurus stramineus should logically be considered the most important, since they predominate in the landscape and are mentioned by a greater number of informants in the interviews carried out with the largest number of collaborators.

In addition, it was observed that some species, commonly called "rats or field mice" or "bats", generate feelings of fear among local inhabitants. Among the most notable species for tourists visiting the trails are Aegialomys xantheolus, Handleyomys alfaroi, Marmosa simonsi and Myotis nigricans. However, it is relevant to note that all these species have reduced populations in the study area, with Vampyrum spectrum that generates a greater feeling of fear. This analysis provides a solid basis for understanding mammal biodiversity in the region and its relevance to tourism and conservation.

Fig. 2.  - Distribution between tourism uses, species and key informants. Reports are shown for each of the six (6) tourism uses (left) related to each of the 10 species of terrestrial mammals of greatest importance and cultural value (center) and each of the 6 key informants or experts (right). Uses: EDS = Education and awareness, OVS = Wildlife observation, TCF = Photographic hunting tourism, ECT = Ecotourism, TAV = Adventure tourism and APT= Attractions in theme parks, *Endemism 

In this context, it is essential to develop a specific marketing strategy for Jipijapa that highlights the presence of mammals preferred by tourists and promotes the potential for observing these species in the area. It is also recommended to disseminate a list of "attractive" animals for visitors, which could contribute to strengthening ecotourism and promoting the conservation of biodiversity in the region.

Table 4.  - Evaluation of terrestrial mammals useful for tourism, using four quantitative indices. List of the 52 species following the CI index and classification of the species, based on each index. FC=frequency of citation, UR=number of reported uses, NU=number of uses, CI=cultural importance, RFC=relative frequency of citation, RI=relative importance, CV=cultural value 

Species Basic Values Indexes Ranking
FC UR NU CI RFC RI CV CI RFC RI CV
Vampyrum spectrum 6 25 6 4,167 1,000 1,000 4,167 1 5 4 1
Ateles fusciceps 6 24 6 4,000 1,000 1,000 4,000 2 1 1 2
Mexican Tamandua 6 24 5 4,000 1,000 0.917 3,333 3 4 5 5
Lycalopex sechurae 6 23 6 3,833 1,000 1,000 3,833 4 2 2 3
Simosciurus stramineus 6 21 6 3,500 1,000 1,000 3,500 5 3 3 4
Desmodus rotundus 3 15 5 2,500 0.500 0.667 1,042 6 8 8 7
Bradypus variegatus 3 14 5 2,333 0.500 0.667 0.972 7 7 7 8
Didelphis marsupialis 3 13 6 2,167 0.500 0.750 1,083 8 9 6 6
Glyphonycteris daviesi 3 13 5 2,167 0.500 0.667 0.903 9 10 9 9
Nasua nose 3 13 5 2,167 0.500 0.667 0.903 10 12 11 10
Myotis nigricans 3 12 5 2,000 0.500 0.667 0.833 11 11 10 11
Syntheosciurus granatensis 4 11 4 1,833 0.667 0.667 0.815 12 6 12 12
Aegialomys xanthaeolus 2 10 5 1,667 0.333 0.583 0.463 13 13 13 13
Lonchorhina aurita 2 9 5 1,500 0.333 0.583 0.417 14 21 18 14
Marmosa simonsi 2 9 5 1,500 0.333 0.583 0.417 15 22 19 15
Handleyomys Alfaroi 2 8 5 1,333 0.333 0.583 0.370 16 17 15 16
Heteromys teleus 2 8 5 1,333 0.333 0.583 0.370 17 18 16 17
Lichonycteris obscura 2 8 4 1,333 0.333 0.500 0.296 18 19 25 21
Lonchophylla concave 2 8 5 1,333 0.333 0.583 0.370 19 20 17 18
Artibeus aequatorialis 2 7 5 1,167 0.333 0.583 0.324 20 14 14 19
Micronycteris megalotis 2 7 4 1,167 0.333 0.500 0.259 21 23 27 22
Proechimys decumanus 2 7 5 1,167 0.333 0.583 0.324 22 25 20 20
Chiroderma villosum 2 6 4 1,000 0.333 0.500 0.222 23 15 22 23
Chironectes minimus 2 6 4 1,000 0.333 0.500 0.222 24 16 23 24
Myotis riparius 2 6 4 1,000 0.333 0.500 0.222 25 24 28 25
Artibeus fraterculus 1 5 5 0.833 0.167 0.500 0.116 26 26 21 26
Glossophaga soricin 1 5 5 0.833 0.167 0.500 0.116 27 33 24 27
Melanomys caliginosus 1 5 5 0.833 0.167 0.500 0.116 28 35 26 28
Oecomys bicolor 1 5 5 0.833 0.167 0.500 0.116 29 39 29 29
Proechimys semispinosus 1 5 5 0.833 0.167 0.500 0.116 30 43 30 30
Rhinophylla alethina 1 5 5 0.833 0.167 0.500 0.116 31 44 31 31
Sigmodon peruanus 1 5 5 0.833 0.167 0.500 0.116 32 45 32 32
Sturnira bakery 1 5 5 0.833 0.167 0.500 0.116 33 47 33 33
Transandinomys bolivaris 1 5 5 0.833 0.167 0.500 0.116 34 50 34 34
Vampyressa thyone 1 5 5 0.833 1,167 0.500 0.116 35 52 35 35
Carollia perspicillata 1 4 4 0.667 0.167 0.417 0.074 36 29 36 36
Diclidurus albus 1 4 4 0.667 0.167 0.417 0.074 37 31 37 37
Gardnerycteris crenulatum 1 4 4 0.667 0.167 0.417 0.074 38 32 38 38
Lonchophylla robusta 1 4 4 0.667 0.167 0.417 0.074 39 34 39 39
Micronycteris hirsuta 1 4 4 0.667 0.167 0.417 0.074 40 36 40 40
Molossus Molossus 1 4 4 0.667 0.167 0.417 0.074 41 37 41 41
Sigmodontomys Alfari 1 4 4 0.667 0.167 0.417 0.074 42 46 42 42
Sturnira luis 1 4 4 0.667 0.167 0.417 0.074 43 48 43 43
Caluromys derbianus 1 3 3 0.500 0.167 0.333 0.042 44 27 44 44
Carollia brevicaudum 1 3 3 0.500 0.167 0.333 0.042 45 28 45 45
Centronycteris centralis 1 3 3 0.500 0.167 0.333 0.042 46 30 46 46
Nyctinomops macrotis 1 3 3 0.500 0.167 0.333 0.042 47 38 47 47
Philander melanurus 1 3 3 0.500 0.167 0.333 0.042 48 40 48 48
Phyllostomus discoloured 1 3 3 0.500 0.167 0.333 0.042 49 41 49 49
Platyrrhinus umbratus 1 3 3 0.500 0.167 0.333 0.042 50 42 50 50
Trachops cirrhosus 1 3 3 0.500 0.167 0.333 0.042 51 49 51 51
Transandinomys talamancae 1 3 3 0.500 0.167 0.333 0.042 52 51 52 52

Descriptive statistics of the results obtained, using various indices and basic values, show that the RI index tended to overvalue the species (mean=0.542, standard deviation=0.181) compared to other indices. This is because the relative frequency of citations and the relative number of use categories are normalized by dividing by the maximum value, which ranges between 0.333 and 1.00. In contrast, the CV index assigned the highest values (mean=0.611, standard deviation=1.083) (Table 5). These findings underline the urgency of implementing effective tourism strategies that generate economic income for the conservation of these species, taking advantage of traditional knowledge about their uses in tourism activities. The research supports the viability of reconciling tourism activity with effective wildlife conservation in the Jipijapa canton. However, the importance of maintaining constant monitoring of mammal populations is emphasized, especially in light of the foreseeable increase in nature tourism and its possible impacts on species abundance.

Table 5.  - Descriptive statistics of the results obtained with four quantitative indices (N=6), FC=citation frequency, UR=number of reported uses, NU=number of uses, CI=cultural importance, RFC=relative citation frequency, RI=relative importance, CV=cultural value 

Basic values Indexes
FC UR NU CI RFC RI CV
Average 2,019 8 4,481 1,333 0.36 0.542 0.611
Pussycat 1 3 3 0.5 0.167 0.333 0.042
Maximum 6 25 6 4,167 0.167 1,000 4,167
Standard deviation 1,515 6,013 0.896 1,002 0.2781 0.181 1,083
Standard error 0.21 0.834 0.124 0.139 0.0391 0.025 0.15

CONCLUSIONS

52 species of wild terrestrial mammals were listed in Jipijapa, with tourist uses of education and awareness (48 species), photographic hunting tourism (48), adventure tourism (47), wildlife observation (46), Ecotourism (42) and attractions in theme parks (10).

Vampyrum spectrum and Ateles fusciceps are vital in Jipijapa, Ecuador, both ecologically and culturally. The spectral bat is respected for its link to the supernatural, and the spider monkey is crucial to forest regeneration and valued as a protector. Both reflect the connection between the community and its environment, with their conservation being key to ecological and cultural balance.

The species of greatest importance and cultural value are Ateles fusciceps, Bradypus variegatus, Desmodus rotundus, Didelphis marsupialis, Glyphonycteris daviesi, Lycalopex sechurae, Nasua nose, Simosciurus stramineus, Tamandua mexicana and Vampyrum spectrum.

ACKNOWLEDGEMENTS:

We express our gratitude to all participants for their informed consent at the beginning of the intervention in the area. This field study has been funded by the State University of Southern Manabí, for the research projects "Biodiversity of interest for tourism in the coastal region of Ecuador" (completed), "Inventory of biological resources of interest for local development in the parish El Anegado, Manabí, Ecuador" (in progress), "Community attitudes towards the development of ecotourism and environmental conservation in the natural reserve: a case of the protected areas of Manabí, Ecuador" (in progress) and "Tourist attractions of biological diversity in the coastal region of Ecuador" (in progress).

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Received: May 27, 2024; Accepted: August 07, 2024

*Autor para la correspondencia: sonia.rosete@unesum.edu.ec

Los autores declaran no tener conflictos de intereses.

Los autores han participado en la redacción del trabajo y análisis de los documentos.

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