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Research Detail

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Ummay Habiba Khatun
Department of Zoology, University of Chittagong, Chittagong, Bangladesh.

Md. Farid Ahsan
Department of Zoology, University of Chittagong, Chittagong, Bangladesh.

Eivin Røskaft*
Department of Biology, Norwegian University of Science and Technology, Trondheim, Norway.

This paper analyses human-langur interactions and people’s attitudes towards common langur (Semnopithecus entellus) conservation in six villages of Keshabpur Upazila, Jessore, Bangladesh. The data for this study are based on responses to a questionnaire administered over a period of 12-months from September 2009 to August 2010. Habitat alterations have increased the number of human-langur interactions in this area of Bangladesh. Langurs depend primarily on foods cultivated in home gardens and orchards, a fact that creates significant problems with the locals, some of whom are afraid of being damaged or bitten. Despite the anxiety regarding potential damages and crop damage, many people enjoy seeing langurs as their ancestors used to do. Overall, 90% of people had a positive view of langur conservation and the establishment of a langur park in the area. Seventy-five percent were optimistic that the establishment of a park would provide economic benefits through job creation. A logistic regression analysis showed that factors such as the conservation status, religion, occupation, and landholding status of the respondents significantly influenced their attitudes towards conservation. Therefore, these aspects need to be clearly addressed to generate support for the conservation of common langurs by the local people, which may lead to the sustainable conservation of this species in Bangladesh.

  Bangladesh, Common langur, Attitudes, Conservation.
  Six villages of Keshabpur Upazila, Jessore, Bangladesh
  00-09-2009
  00-08-2010
  Socio-economic and Policy
  Attitude, Langur

The aim of this study was therefore to gather knowledge concerning whether local people understand the conservation status of langurs and their perceptions towards the conservation of this critically endangered species. We recorded the customs (e.g., human-langur interactions, problems caused by langurs, competition for resources, etc.) of how locals interact with langurs and the factors that shape their attitudes towards langur conservation.

Study area This study was conducted in six villages (Keshabpur, Baliadanga, Brahmakati, Ramchandrapur, Durgapur, and Madhyakul) of KeshabpurUpazila (a sort of sub-district) in southwestern Bangladesh from September 2009 to August 2010. Upazila is approximately located between 22° 25' and 23° latitude and 89° 25' and 89° 38' longitude. Upazila's area is 259 km2, and it comprises 9 union parishads, 142 mouzas and 143 villages. In 2009, the total population was approximately 200,229, and the majority of inhabitants were Muslims (80.1%) (BBS, 2009). Most households are predominately dependent on agriculture. In general, men are the primary breadwinners, and women spend most of their time as homemakers. Langurs have been residing in KeshabpurUpazila for over 100 years. One pair of Hanuman langurs was released into Ramchandrapur village by devotees. Since the initial release, the langurs have been living in the area and spread to the other villages of the Upazila (personal communication with an octogenarian Hindu person). Currently, a sizable population lives in the study villages, especially Ramchandrapur, Durgapur and Madhyakul, which are home to the majority of the langurs. Eight of eleven groups live in these three villages (Khatun et al., in press). Langurs come into conflict with humans because of their crop-raiding habits (Khatun et al., 2012a). To minimise crop damage, as well as for the conservation of the langurs, the governmental „Biodiversity Conservation and Nature Development Project. supplies food to the langurs in the study villages. We, therefore, divided the study villages into the following two areas based on how much additional food was distributed to the villages by the conservation project: (1) A high conservation status area (Keshabpur, Baliadanga, and Brahmakati), which is close to the Upazila headquarters. The langurs also received handouts from the villagers. (2) A low conservation status area (Ramchandrapur, Durgapur, and Madhyakul), which is approximately 12 km north of the Upazila headquarters. Visitors hardly visit the area to see the langurs.

Data collection We collected data on people's attitudes and perceptions towards the conservation of crop-raiding langurs using a semi-structured questionnaire (Box 1). In total, 410 people were randomly interviewed: 51% were males, and 49% were females. Additionally, 57.4% were Muslims, and 42.6% were Hindus. Data were collected by a main researcher (UHK, female PhD candidate) and three trained field assistants who were familiar with the local language. Among those interviewed were the household heads, their wives, and other adults (≥18 years) in the house who were willing to answer the questions because some adults felt too shy to speak in front of the researcher and the assistants. The questionnaire had a combination of closed- and open-ended questions regarding background information (age, gender, level of education, religion, and household size) and socio-economic status (occupation, landholding status, and cultivated farm size in acres) of the household. The open-ended questions asked for an assessment of the respondent's thoughts concerning the conservation of common langurs in the area (Box 1). 

Statistical analyses Demographic variables were coded as follows: gender (male or female), age (young ≤ 40 years or old > 40 years), household size (small household ≤ 4 or large household > 4), and religion (Muslim or Hindu). Socio-economic variables included the following: access to mass media (yes or no), education (uneducated- no schooling/less than three years of basic education or educated- at least three years of basic education), landholding status (low < 0.1 acres, 0.1 < medium < 0.5, and high > 0.5 acres), and occupation (farmers, who were engaged in crop production and farming, and non-farmers, who were service holders, businessman, students, elected representatives of villages, day labourers, van pullers, etc.). All demographic and socio-economic variables were considered as independent variables in the analyses. Pearson Chi-square tests were used to evaluate differences in the answers of respondents. Stepwise regression analyses were applied to determine which independent variables controlled the locals? attitudes in relation to the various dependent variables. In the analyses, independent variables were coded as dummy variables. Only significant results are reported in the results. For all tests, p < 0.05 was considered to be statistically significant. The SPSS (version 16) statistical package was used to perform all analyses. Throughout the text, respondents are referred to as households, people, locals, or villagers. A household is defined as those who reside under the same roof, share income, and are typically close relatives. We considered “do not know” responses to be missing values in the analyses.

  International Journal of Biodiversity and Conservation Vol. 4(11), pp. 385-399, August 2012
  DOI: 10.5897/IJBC12.035
Funding Source:
1.   Budget:  
  

From the above discussion, it appears that the positive attitudes of locals represent a significant source of hope for langur conservation. The study suggests that the conservation attitudes of the locals have not yet been severely affected by the present human-langur interactions in the area. Despite this, careful consideration of the locals' fear of langur damages, langur-related problems, locals' interest in planting non-edible Hanuman foods, their attitudes towards conservation laws regarding langur protection, the poverty levels of locals, and respondent's perceptions towards establishing a langur park must be given prior to planning any conservation strategy in the area. Otherwise, the results could be detrimental for both humans and langurs. In this regard, further studies are recommended to investigate the behavioural adaptations of langurs in the area and to characterise langur raiding behaviour.

Our results have led us to the following conclusions. Initially, a community-based conservation education programme is essential to improve people?s awareness, which could lead to a social movement for Hanuman langur conservation. Second, the reintroduction of plant species that were once present in the area would provide food for the langurs and would be a critical step towards langur conservation. To do this effectively, a thorough understanding of the importance of habitat protection and resource preservation for langurs is essential. Third, the management of planting should take into account the preferred foods of langurs. The natural foods of the langur that are not edible by humans but are ecologically important (e.g., Leucaena leucocephala, Albizia procera, Samanea saman, Polyalthia longifolia, Mimusops elengi, Acacia nilotica, Azadirachta indica, Moringa oleifera, Eugenia operculata, Anthocephalus cadamba, Aegele marmelos, and Salmalia malabarica) should be planted in public areas, such as roadsides and surrounding homesteads, to establish viable habitats for the langur and to minimise crop damage. The conservation value of such areas, particularly of agro-forest vegetation, has received increasing recognition by conservation biologists throughout the world. Finally, the establishment of a langur park is fundamental for the sustainable development of langurs. A park would result in the development of the area, and people would benefit from new jobs and might be encouraged to participate in income-generating programmes that might improve their socio-economic conditions. The promotion of tourism in the area would positively change the perceptions of the local community towards langur conservation. Protected area management regarding biodiversity conservation is now being highly appreciated in developing countries.

  Journal
  


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