Human-wildlife conflict (HWC) often arises in shared landscapes, where human settlements overlap with wildlife habitat, impacting multiple species (Batavia & Nelson, 2016;Madden, 2004). HWC refers to the negative impacts generated by the interaction of wildlife and humans and creates numerous challenges for the conservation of threatened species around the world (Dickman, 2010;Distefano, 2005). These negative impacts can refer to the loss of human life, property, or the loss of wild species and their habitat or
Background The risk of losing traditional knowledge of medicinal plants and their use and conservation is very high. Documenting knowledge on distribution and use of medicinal plants by different ethnic groups and at spatial scale on a single platform is important from a conservation planning and management perspective. The sustainable use, continuous practice, and safeguarding of traditional knowledge are essential. Communication of such knowledge among scientists and policy makers at local and global level is equally important, as the available information at present is limited and scattered in Nepal. Methods In this paper, we aimed to address these shortcomings by cataloguing medicinal plants used by indigenous ethnic groups in Nepal through a systematic review of over 275 pertinent publications published between 1975 and July 2021. The review was complemented by field visits made in 21 districts. We determined the ethnomedicinal plants hotspots across the country and depicted them in heatmaps. Results The heatmaps show spatial hotspots and sites of poor ethnomedicinal plant use documentation, which is useful for evaluating the interaction of geographical and ethnobotanical variables. Mid-hills and mountainous areas of Nepal hold the highest number of medicinal plant species in use, which could be possibly associated with the presence of higher human population and diverse ethnic groups in these areas. Conclusion Given the increasing concern about losing medicinal plants due to changing ecological, social, and climatic conditions, the results of this paper may be important for better understanding of how medicinal plants in use are distributed across the country and often linked to specific ethnic groups.
Human–wildlife conflict is increasing globally, particularly in the areas, where wildlife and humans coexist and share resources. Large mammalian predators such as common leopards not only kill livestock but they are also killing humans. Baitadi is among the top ranked districts in Nepal in terms of number of human common leopard conflict events in last 10 years. The fieldwork for this study was carried out between January and June 2020 in the villages of Bishalpur, Udayadev, Pancheshor and Aamchaura of Baitadi district. Field observation, questionnaire survey, key informant interview and literature review were used for the data collection. Our study found that common leopards killed 23 and injured eight people between 2011 and 2019 in the district. In retaliation, people killed 26 common leopards in the same period, which must have spelt disaster for these rare cats. Despite the increasing number of conflict events, the local people, in general, were found to have positive attitude towards wildlife conservation. Therefore, improved prey species management, awareness raising among the local people and detailed study on habitat assessment, population status of leopards and their prey species are the urgent needs for the mitigation of human common leopard conflict in the district.
Small carnivores are able to adapt to patchy forests and human dominated landscape in proximity to water sources. Small carnivore’s population is declining due to anthropogenic effects, and in most of the areas, their occurrence is little known. We aimed to identify the spatial occurrence of crab-eating mongoose, the factors affecting the occurrence of species and coexistence with other species using camera trap. The crab-eating mongoose mostly preferred the shrub-land habitat (65%) and followed by agriculture land, forest and grassland. Almost all preferred habitats were near to water sources. The occurrence of crab-eating mongoose was influenced by human disturbances. Their occurrences were decreased with increasing disturbances. In addition, the crab-eating mongoose’s occurrence was also decreased with increasing distance to water sources. The movement activities of crab-eating mongoose were varied according to time period (F = 6; df = 14; p < 0.013), and was mostly active at day to mid-night (16.00 to 12.00 hours) and mid-night to early morning (12.00 to 8.00 hours). The crab-eating mongoose co-exists with other carnivores including Leopard, Jungle cat, Masked-palm civet, Small Indian mongoose, Leopard cat, Yellow-throated martin, and Large Indian civet. In addition, its occurrence was affected by human interference. The data available from this study can be used to develop site/species-specific conservation plans that aid stewardship for biodiversity conservation.
Background There are handful hypothesis-driven ethnobotanical studies in Nepal. In this study, we tested the non-random medicinal plant selection hypothesis using national- and community-level datasets through three different types of regression: linear model with raw data, linear model with log-transformed data and negative binomial model. Methods For each of these model, we identified over-utilized families as those with highest positive Studentized residuals and underutilized families with highest negative Studentized residuals. The national-level data were collected from online databases and available literature while the community-level data were collected from Baitadi and Darchula districts. Results Both dataset showed larger variance (national dataset mean 6.51 < variance 156.31, community dataset mean 1.16 < variance 2.38). All three types of regression were important to determine the medicinal plant species selection and use differences among the total plant families, although negative binomial regression was most useful. The negative binomial showed a positive nonlinear relationship between total plant family size and number of medicinal species per family for the national dataset (β1 = 0.0160 ± 0.0009, Z1 = 16.59, p < 0.00001, AIC1 = 1181), and with similar slope and stronger performance for the community dataset (β2 = 0.1747 ± 0.0199, Z2 = 8.76, p < 0.00001, AIC2 = 270.78). Moraceae and Euphorbiaceae were found over-utilized while Rosaceae, Cyperaceae and Caryophyllaceae were recorded as underutilized. Conclusions As our datasets showed larger variance, negative binomial regression was found the most useful for testing non-random medicinal plant selection hypothesis. The predictions made by non-random selection of medicinal plants hypothesis holds true for community-level studies. The identification of over-utilized families is the first step toward sustainable conservation of plant resources and it provides a baseline for pharmacological research that might be leading to drug discovery.
Wildlife conservation in human‐dominated landscapes faces increased challenges due to rising conflicts between humans and wildlife. We investigated the human and wildlife loss rates due to human–wildlife conflict between 2000 and 2020 in Nepal. We concentrated on Asian elephant ( Elephas maximus ), greater one‐horned rhino ( Rhinoceros unicornis ), tiger ( Panthera tigirs ), and leopard ( Panthera pardus ) mortality, as well as human mortality caused by these species. Over the 21‐year period, we recorded 1139 cases of wildlife mortality and 887 cases of human mortality. Leopard mortality was the highest, followed by that of greater one‐horned rhinos, tigers, and Asian elephants. Overall, the rate of wildlife mortality has been increasing over the years. Asian elephants were found to be more responsible for crop damage than greater one‐horned rhinos, while leopards were found to be more responsible for livestock depredation than tigers. The generalized linear model indicated that the mortality of wildlife in the districts is best predicted by the additive effect of human mortality, the proportion of agricultural land, and the literacy rate of the districts. Retaliatory wildlife mortality was the most challenging issue for wildlife conservation, especially for the large mammals. Findings from this study are important for mitigation of human–wildlife conflicts, controlling retaliatory killing, and conserving these threatened large mammals.
To assess threats to the population of native mammals and their survival, we performed a retrospective study utilizing a rescue and rehabilitation database from Nepal. Based on a total number of 1013 cases involving six taxonomic families of mammals admitted over five years, the outcome (mortality and survivability) differed significantly among six taxa (χ2[df = 5, N = 1013] = 65.08, p < .001). The mortality rate was highest in Felidae (74%), followed by Herpestidae (69%), Viverridae (62%), Bovidae (50%), Cervidae (50%), and Cercopithecidae (38%). The outcome also differed significantly among the causes of admission (χ2[df = 9, N = 1013] = 241.48, p < .001). The prevalence of mortality was highest in the cases of gunshot and poisoning, followed by collision with a vehicle, diseases/infection, entanglement/trapped, injured by dogs/cats, abandoned/orphaned, injured by humans, unknown causes, and domestic/captivity issues. Multiple logistic regression analysis showed the significant influence of taxonomic family, age group, and cause of admission on the likelihood of mortality of the rescued mammals. The odds ratio of mortality was higher for carnivore taxa, and juveniles were more likely to succumb to death than adults. Our study provides important information associated with the mortality of rescued mammals, thereby assisting in the development and formulation of strategies for threat mitigation and an efficient rehabilitation process.
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