*
 

iForest - Biogeosciences and Forestry

iForest - Biogeosciences and Forestry
*

Implications of ecotourism development in protected areas: a study from Rema-Kalenga Wildlife Sanctuary, Bangladesh

iForest - Biogeosciences and Forestry, Volume 3, Issue 1, Pages 23-29 (2010)
doi: https://doi.org/10.3832/ifor0520-003
Published: Jan 22, 2010 - Copyright © 2010 SISEF

Research Articles

This article is based on visitors profile study of protected area based tourist spots of Rema-Kalenga Wildlife Sanctuary (RKWS), Bangladesh to ascertain the potential of ecotourism. Study findings shows that 69% male constitute the visitors group while the maximum number of visitors was found in the age of below 30 years. Most of the visitors were literate and among them 43% visitors were student. Most (53%) of visitors preferred to get recreation in holidays as they were employed. Visitors were highly preferred to come with friends group. About 92% respondents showed positive mind to come here in future while 89% respondents view that park has tourism potential. Most of the respondents reported the presence of wildlife (48%) most notable followed by plant diversity and tribal community as recreational. From χ2 test it is found that highly significance association present between tourism potentiality of the wildlife sanctuary and some demographic variable like income of tourists (χ2 = 49.138, p < 0.000), visiting pattern (χ2 = 19.344, p < 0.000), education of tourists (χ2 = 50.226, p < 0.000), travelling distance (Km - χ2 = 11.427, p < 0.022), duration of staying (χ2 = 12.867, p < 0.002), frequency of visit (χ2 = 8.456, p < 0.015), visiting time (χ2 = 6.530, p < 0.011), problem in the study area (χ2 = 14.962, p < 0.021), occupation of tourists (χ2 = 8.848, p < 0.031). If the problems addressed by the visitors were solved, RKWS would be a bright place of eco-tourism in Bangladesh.

Ecotourism, Protected area, Tourism potential, Visitors, Bangladesh

  Introduction 

Worldwide, many countries and regions rich in biodiversity and poor in economy have been vigorously promoting ecotourism as a conservation tool in their protected areas (PAs) since the 1990s ([17]). PAs now cover more than 12% of the world’s land area. These PAs are on the front line in the campaign to conserve biodiversity as well as to promote eco-tourism on the planet Earth ([8], [15]). Tourism use of PAs basically involves the travel for the discovery and learning about wild environments. The importance of nature in attracting tourists is significant and stated that nature and cultural heritage represent a competitive advantage for many areas, for different kinds of protected areas ([40]), a chance to see wildlife and undisturbed nature is rated as very important reason for visits to PAs ([14]). PAs are becoming more popular destinations for wildlife tourists of national and international origin. Besides this, economic benefits from tourism are observed in different PAs. Protected area based eco-tourism that can give rise to economic benefits to local communities as well as to the nation ([15], [14], [37], [39], [16], [12], [13], [11], [18], [23], [29], [22], [35], [36]). Nature or forest based tourism is a key category of eco-tourism, one of the fastest growing sectors of the world ([21]). However in Bangladesh this promising sector is poorly utilized. From a source it has been found that, less than 10000 foreign visitors entered in 1992, domestic tourism on the other hand appears to be a strongly flourishing sector of the market ([34]).

Protected areas have played significant roles as tourist attractions in many countries since their establishment ([6]). PAs with their landscapes, flora and fauna as well as their cultural elements form attractions for tourists ([7]). Another thing is that eco-tourism continues to become a management strategy for protected areas. There are numerous opportunities for ecotourism in protected areas. Such opportunities are revenue generation (i.e., user fees, entranced fees and donations), employment creation, justification for protected areas, healthier economies, environmental education, and improved conservation efforts ([4], [10]). Presently, there are 19 notified protected areas (i.e., 11 national parks, seven wildlife sanctuaries and one game reserve) in Bangladesh ([27]). Compared to other regions of the world, this figure is still very poor. The PAs of Bangladesh cover nearly 1.7% of the total landmass of the country, which is the second lowest per capita area under PAs in any country ([31]). As the tourism industry is quickly becoming the most profitable industry in developing countries, Government of Bangladesh should give emphasis to increase protected areas for ecotourism development. As PAs has become a new tool to promote environmentally and culturally friendly tourism, but still now a little reliable or published information is available regarding the tourism potentialities of PAs of Bangladesh. Taking this view a head the present study was conducted in Rema-Kalenga Wildlife Sanctuary of Bangladesh to assess the recreation potential as a protected area, which will help the planner to provide an effective plan for its management and improvement. Also influence to increase protected areas for ecotourism development in Bangladesh.

  Methodology 

Site profile

Rema-Kalenga Wildlife Sanctuary (RKWS) is located approximately 130 km east-northeast of Dhaka and 80 km south-southeast of Sylhet in Chunarughat Thana, a sub-district of Habiganj District, Sylhet. The sanctuary is bounded by Tripura State (India) to the south and east, and Kalenga Forest Range to the north and west. Geographically, the area lies between 24°06’-24°14’N latitude and 91°34’-91°41’E longitude (Fig. 1). The area falls under the Sylhet Hills zones ([26]), and the administrative area is known as the Rema-Kalenga Forest Range. Table one describes the main features of the Rema-Kalenga Wildlife Sanctuary.

Data collection and analysis

To collect data and information, an opinion pull was conducted in the study areas. This was because most of recreation seekers were willing to pass their spare time in these eco-tourism spots. Visitor’s survey method was conducted for valuation of outdoor recreation. A total of 150 respondents were interviewed representing different socio-economic and occupational groups. The selection of respondents was done randomly to avoid serious biasness. The respondents were interviewed with a semi-structured questionnaires designed for this purpose. The aim of survey was to gather information related to demography of visitors as the major stakeholder (e.g., age, education and occupation), visits to the park (e.g., frequency, season, time, purpose, form of visit, willingness to further visit), tourism potential of the park and problems faced by the visitors during visits. Descriptive statistics were derived to summarise the property of the dataset, while analytical methods (correlation and chi-squared test) were used to analyse the data and test for differences (at 95% level of significance). Analysis was conducted using SPSS ver 10.0 (Statistical Package for the Social Sciences). Here, chi-squared test explains the relationship between tourism potential with other demographic variable.

  Results 

Demographic characteristics of visitors

The total visitors of the surveyed area were 150, of which 103(68.7%) were male and the rest 47 (31.3%) were female. Among the visitors, 60% male said that the RKWS is tourism potential (Tab. 1, Tab. 2). While 2.66% females view were negative. Majority of the visitors belong to younger groups (<30 years), which is about 84%. Older age groups (>30 years) represents only 16% (Fig. 2).

Tab. 1 - Description of the Rema-Kalenga Wildlife Sanctuary (RKWS - source: [24], [33]).

Items Description
Forest type Rema-Kalenga Wildlife Sanctuary is one of the protected areas of Bangladesh and is notified in 1982.
Location Chunarughat Upazilla of Habigonj District. Geographically, the area lies between 24°06’-24°14’ N latitude and 91°34’- 91°41’ E longitude.
Area Total area: 1 995 hectares.
Forest type Tropical evergreen to semi-evergreen forests.
Bio-ecological Zone The park falls under the Bio-ecological Zone-9b with broad zone “Sylhet” Hills.
Climate Mean annual temperature: 32°C; maximum in May and October; minimum (in January): 12°CMean annual humidity: 74% during December; 90% during July-August; Mean annual rainfall: 4162 mm; Monthly minimum rainfall (in December): 0.0mm; Monthly maximum rainfall (in July): 1250 mm.
Topographic characters Soil texture: sandy loam to silty clay and acidicThe area of the national park is undulating with slopes and hillocks, locally called tila, ranging from 10-50 m and are scattered in the forest. The forest is drained by a number of small, sandy-bedded streams.
Floral diversity Flora: about 606 plant species among which 82 have been identified as medicinal plants.
Faunal diversity Mammals: 37; Amphibians: 7; Reptiles: 18; Bird: 167; Key fauna: jackals, wild boar, porcupine, squirrel and deer.
Important attractive features Tea estates and Ethnic group: There are eight small indigenous groups (ethnic) living inside and outside the sanctuary. They are the Tripura/ Tipra (or Deb-Barma), Santal, Urang, Kharia, Kurmi, Goala, Munda, and Bunargi. One ethnic group (Tripura ethnic group), is located inside the park.
No. of villages 36
No. of households 1016
Average household size (Persons) 7.5

  Enlarge/Reduce  Open in Viewer

Tab. 2 - Chi-square test of relationship between demographic variable and potentiality of park (n = 150).

Parameter Variable Potentiality of the park (%) χ2 p
Yes No
Age of the tourists (Yr.) <20 10.66 2.66 2.811 0.422
20-25 39.33 4.66
25-30 23.33 3.33
30+ 15.33 0.66
Traveling distance (Km) <25 20.66 - 11.427 0.022
25-50 15.33 5.33
50-75 20.66 3.33
75-100 10.66 0.66
100+ 21.33 2.00
Traveling Cost (Tk.) <200 21.33 5.33 5.653 0.227
200-500 15.33 1.33
500-800 21.33 2.66
800-1100 18.66 2.00
1100+ 12.00 -
Duration of staying <2 8.66 4.66 12.867 0.002
2-5 71.33 6.00
5> 8.66 0.66
Frequency of visit First time 36.00 8.66 8.456 0.015
Second time 39.33 2.66
More than second time 13.33 -
Visiting time Holiday 50.00 2.66 6.530 0.011
Without holiday 38.66 8.66
Income of tourists <8000 (Low income group) 10.00 9.33 49.138 0.000
8000-15000 (Medium income group) 54.66 2.00
>15000 (Rich group) 24.00 -
Visiting pattern Individual 13.33 6.66 19.344 0.000
Group of friends 40.66 1.33
Family 22.66 2.66
Couple 12.00 0.66
Problem in the study area Sanitation 18.00 2.66 14.962 0.021
Drinking water 14.00 0.66
Security 11.33 -
Communication 12.00 2.00
Accommodation 16.66 -
Food 12.66 4.00
Guiding 4.00 2.00
Occupation of tourists Service 14.66 2.00 8.848 0.031
Business 16.00 3.33
Student 41.33 1.33
Un-employed 16.66 4.66
Education of tourists Illiterate 4.00 6.66 50.226 0.000
Primary & Secondary 14.66 2.66
Higher Secondary 27.33 1.33
Above 42.66 0.66
Sex of tourists Male 60.00 8.66 0.543 0.461
Female 28.66 2.66

  Enlarge/Reduce  Open in Viewer

Fig. 2 - Age group of the visitors.

  Enlarge/Shrink   Download   Full Width  Open in Viewer

Study shows that most (89.7%) of the visitors are literate. Among the visitors, education status of 17.3% visitors are the primary and secondary level and 28.7% are the higher secondary level (Fig. 3). Among the respondents, above higher secondary (Graduate, PhD) level visitors (42.66%) opined that the site is tourism potential (Tab. 2).

Fig. 3 - Educational status of the visitors.

  Enlarge/Shrink   Download   Full Width  Open in Viewer

Findings revealed that 78.7% visitors are employed. Students represent the highest number of visitors (42.7% - Fig. 4). Among the different occupational group 41.33% student’s attitude was positive about the RKWS that is the recreation potential (Tab. 2). Most of the visitors in the study area are visiting in a group with friends (42%) followed by family groups (25.3%). Couple category represents the lowest number of visitors (12.7% - Fig. 5). Maximum 40.66% group of friends told that the RKWS has tourism potential (Tab. 2).

Fig. 4 - Occupational status of the visitors.

  Enlarge/Shrink   Download   Full Width  Open in Viewer

Fig. 5 - Visiting pattern of respondents in RKWS.

  Enlarge/Shrink   Download   Full Width  Open in Viewer

Economics of the visitors

Maximum visitors (56.7%) are come from medium family followed by rich family (24%). Among the different income group highest (54.66%) visitors of medium family opined that the site is recreation potential (Tab. 2). Most of the visitors (26.7%) spend <200 Tk followed by 500-800 Tk (24%), 800-1100 TK (20.7%) and 200-500 Tk (16.7%) to visit the study area (Tk means Taka, Bangladeshi currency, 1US$ = 70Tk). Most of the visitor (21.33%) those who spend <200 Tk and 500-800 Tk told that RKWS is a tourism potential site respectively (Tab. 2).

Duration, visiting time, frequency of visit and traveling distance

Study revealed that 52.7% visitors preferred to pass their spare time during holidays and the remaining 47.3% visitors desired to enjoy the RKWS other than holidays (Tab. 3). 50% visitors those pass their time during holidays told that the RKWS is recreation potential (Tab. 2). It is found that most of the visitors (44.7%) visited RKWS for the first time followed by for the second time (42%) and more than twice (13.3%). 39.33% of the visitors those who came second time told that the site is tourism potential. The study indicate that most of the visitors (77.3%) stay at the RKWS for (2-5) h followed by less than 2 h (13.3%) and more than 5 h (9.3%). Among the respondents those spent (2-5) h, 71.33% told that the RKWS is recreation potential (Tab. 2). Findings showed that 24% visitors come from a distances range (50-75) Km followed by 100+ Km distances (23.3%), <25 Km distances (20.7%), (25-50) Km distances (20.7%) and 75-100 Km distances (11.3% - Fig. 6). Highest 21.33% visitors who came from 100+ Km distances told that the site has ecotourism potentiality (Tab. 2).

Tab. 3 - Visiting time, frequency of visit and duration of staying the visitors.

Category Visiting time Frequency of visit Duration of staying (h)
Holydays Free time without holydays Once Twice More than twice <2 2-5 >5
Number 79 71 67 63 20 20 116 14
Percentage 52.7 47.3 44.7 42 13.3 13.3 77.3 9.3

  Enlarge/Reduce  Open in Viewer

Fig. 6 - Travelling distance of the visitors.

  Enlarge/Shrink   Download   Full Width  Open in Viewer

Problems identified by the visitors

According to the visitors, the remarkable problems are insufficient toilets, accommodation problem, non-availability of food, non-availability of drinking water, and lack of proper communication facilities, lack of sufficient security and guiding (Fig. 7).

Fig. 7 - Problems faced by the visitors.

  Enlarge/Shrink   Download   Full Width  Open in Viewer

Tourism potential

Of the surveyed respondents, 88.7% were of the view that their visit experience at RKWS was recreational and only 11.3% respondents stated it was not so. The respondents, to whom visit to the RKWS appeared recreational, were asked specific question on what component provided them recreation most. In response to it, most of the respondents reported the presence of wildlife (48%) most notable followed by plant diversity (36%) and tribal community (16%) as recreational (Fig. 8).

Fig. 8 - Attractive recreation component of RKWS.

  Enlarge/Shrink   Download   Full Width  Open in Viewer

Another specific question was asked whether the respondents would like to make recurrent visit to the site in future. A high proportion of respondents (92%), after the visit experience at RKWS expressed their willingness to make further visits while only 8% respondents denied coming again.

Relationship between demographic variable and tourism potentiality of the park

From chi-square test it is found that highly significance association present between tourism potentiality of the wildlife sanctuary and some demographic variable like income of tourists (chi-square = 49.138, p < 0.000), visiting pattern (chi-square = 19.344, p < 0.000), education of tourists (chi-square = 50.226, p < 0.000), travelling distance (Km - chi-square = 11.427, p < 0.022), duration of staying (chi-square = 12.867, p < 0.002), frequency of visit (chi-square = 8.456, p < 0.015), visiting time (chi-square = 6.530, p < 0.011), problem in the study area (chi-square = 14.962, p < 0.021), occupation of tourists (chi-square = 8.848, p < 0.031 - Tab. 2). But on the other hand, there is no significant association found among sex, age and travelling cost of the tourist with tourism potentiality of the wildlife sanctuary.

  Discussion 

Establishment of protected areas (PAs) has been the most widely accepted means of biodiversity conservation so far, supported by national and international agencies ([15], [30], [36]). Tourism use of PAs basically involves the travel for the discovery and learning about wild environments. Tourism is viewed in many industrial nations as an environmentally friendly way to revitalize distressed rural communities and economies. A similar view is gaining momentum in developing countries like Bangladesh where PAs are becoming more popular destinations for wildlife tourists of national and international origin.

Study findings revealed that the visitors in the RKWS are varied with age, sex, education and occupation. In general male visitors are higher than female visitors in outdoor recreation ([2]) and youth groups are more interested in outdoor recreation ([1]). In the present study it was found that the young energetic males are very much willing to visit the park. The lack of safety, deficiency in proper facilities and the backwardness of women in our society might have discouraged them to come for recreation in this wildlife sanctuary. Educated people are more interested to visit the RKWS. The results also revealed that education can play a vital role in determining the demand for recreational activities at the RKWS. Considering occupation students can play the leading role to gear up the recreational activities in the RKWS. Ahmed ([1]) also repeated that students are the major groups of outdoor recreation. Another work done by Ahmed & Rahman ([2]) also showed that participation of outdoor recreation increase with increasing educational level but decreases after higher secondary level. The results also predict that RKWS might be a good recreational area for enjoying with family members and group of friends. Visitors were also asked to find out amount of money they spend or willing to pay for the recreation they get into the RKWS. From economic point of view the study area is major source of recreation for medium class people. Bangladesh is a developing country and a large percentage of people belong to the medium class for whose protected area is an important area for recreation. Generally we know mass gathering of people is seen in any recreational areas during holidays. This is not exceptional in context of our country. In RKWS it reflects that more visit followed less recreational demand and vice versa. Most of the recreationalist wished to stay inside the park for two to five hours only. Most of the visitors come from other district and also from the city area.

The RKWS comprises the remaining natural forests, and the plantations raised earlier by converting high forests of great biodiversity value. Large deciduous trees are mixed with evergreen smaller trees and bamboos. The top canopy includes Artocarpus chaplasha, Dipterocarpus turbinatus, Elaeocarpus floribundas, Dillenia pentagyna, Castanopsis tribuloides, etc. A total of 167 species (mammals, birds, reptiles and amphibians) including forest-dwelling and wetland-associated species were documented. Besides this Tipra polli, tea garden creates more interest for visitors ([3]). The field observation and the study on the visitors revealed that recreational facilities like wildlife, natural beauty and tribal community attract the visitors. This finding corresponds with the opinion of Ceballos-Lascurain ([7]) that green spaces with their landscapes, flora and fauna as well as their cultural elements form attractions for tourists. Besides the potentialities the respondents raised the issue of some problems they faced in the park. The similar trend of problems was found in the visitor survey in Sitakunda Botanical Garden and Eco-park of Bangladesh by Nath & Alauddin ([25]), where lack of security measures was the most important issue as visitor’s sometimes felled victim to mugging in remote and desolate corners of the WS. Okaka ([28]) reported the relatively lower number of visitors to some protected areas of Uganda due to inadequate security situation. Studies on people participation in outdoor recreation found that it revitalizes human sprit, restores people’s initiatives of life, produces feeling of well-being, satisfaction, creativeness and physical conditions ([38], [5], [9], [32], [20], [19]). So, from this study it can be concluded that RKWS might be a potential outdoor recreation area.

  Conclusion and recommendations for planners and managers 

Tourism in RKWS is a very new development. In order to develop this sector further, separate management plan and an action plan for tourism should be developed. Numerous people come to RKWS to see forests, wild life, and natural beauty and to visit the surrounding attractions. The park has a good potentiality for eco-tourism even though it does not offer any lodging facilities. Bangladesh government can create opportunities to develop the tourist industry (ecotourism) based on protected areas. Tourism as a wildlife and forest conservation and sustainable development tool can be promoted and from a community perspective it is expected to provide benefits that ultimately enhance local support for the conservation of natural resources. The result of the study did not reveal negative attitude about tourism development at RKWS but pattern of attitude involving tourism may change in the future as tourism develops. Therefore, further studies will be needed in the future to gather quantitative data on the performance of tourism at the protected areas in terms of ecological, socio economic and community conservation levels.

  References

(1)
Ahmed MR (1993). Outdoor recreation potentials of foy’s lake area, Chittagong. Bangladesh Journal of Forest Science 22 (2): 30-36.
Gscholar
(2)
Ahmed MR, Rahman MM (1997). Visitor’s participation in outdoor recreation activities Bhawal national park with respect to some socio economic variables. Bangladesh Journal of Forest Science 26 (1): 37-42.
Gscholar
(3)
Ali D (2008). Present status and tourism potentiality of Sylhet forest division, Bangladesh. B.Sc. (Hons.) Project paper, Department of Forestry, Shahjalal University of Science and Technology, Sylhet, Bangladesh, pp. 1- 55.
Gscholar
(4)
Borrie WT, McCool SF, Stankey GH (1998). Protected area planning principles and strategies. John Wiley and Sons Ltd, UK.
Gscholar
(5)
Brockman FC, Merriam LC (1979). Recreational use of wild lands. McGraw Hill, New York, USA, pp. 337.
Gscholar
(6)
Butler WR, Boyd WS (2000). Tourism and national parks: a long but uneasy relationship. In: “Tourism and national parks: issues and implications” (Butler WR, Boyd WS eds). John Wiley & Sons Ltd., UK, pp. 70-75.
Gscholar
(7)
Ceballos-Lascurain H (1993). Ecotourism as a worldwide phenomenon. In: “Ecotourism: a guide for planners and managers” (Lindberg K, Hawkins DE eds), Natraj Publishers, Dehradun, India, pp. 80-83.
Gscholar
(8)
Chape S, Blyth S, Fish L, Spalding M (2003). United nations list of protected areas. IUCN, Gland, Switzerland and UNEP-WCMC, Cambridge, UK, pp. 44.
Gscholar
(9)
Douglas WR (1982). Forest recreation. Pergamon Press, New York, USA, pp. 354.
Gscholar
(10)
Drumm A, Moore A (2005). Ecotourism development: a manual for conservation planners and managers. Volume I: An Introduction to Ecotourism Planning. The Nature Conservancy, Washington, DC, pp.31-42.
Gscholar
(11)
Fiallo EA, Jacabson SK (1995). Local communities and protected areas: attitudes of rural residents towards conservation and Machalilla national park, Ecuador. Environmental Conservation 22 (3): 241-249.
CrossRef | Gscholar
(12)
Ghimire BK, Pimbert MP (1997). Social change and conservation: an overview of issues and concepts. In: “Social change and conservation” (Krishna PG, Michel PP eds). Earthscan Publications Limited, London, UK, pp. 1-45.
Gscholar
(13)
GOI (1994). Government of India. National Tiger action plan. Ministry of Environment and Forests, Government of India, New Delhi, India.
Gscholar
(14)
Goodwin H (1996). In pursuit of ecotourism. Biodiversity & Conservation 5 (3): 277-292.
CrossRef | Gscholar
(15)
Hales D (1989). Changing concepts of national parks. In: “Conservation for the Twenty-First Century” (Western D, Pearl M eds). Oxford University Press, London, UK, pp. 139-144.
Gscholar
(16)
Hannah L (1992). African people, African parks: an evaluation of development initiatives as a means of improving protected area conservation in Africa. USAID, Biodiversity Support Program, Conservation International, Washington, USA.
Gscholar
(17)
He G, Chen X, Liu W, Bearer S, Zhou S, Cheng LY, Zhang H, Ouyang Z, Liu J (2008). Distribution of economic benefits from ecotourism: a case study of wolong nature reserve for giant Pandas in China. Environmental Management 42: 1017-1025.
CrossRef | Gscholar
(18)
Ite UE (1996). Community perceptions of the Cross River national park, Nigeria. Environmental Conservation 23 (4): 351-357.
CrossRef | Gscholar
(19)
Jashimuddin M, Alamgir M (2005). Visitors of urban green space based recreation: a case study from Chittagong Metropolitan Area: the Chittagong University. Journal of Science 29 (2): 45-52.
Gscholar
(20)
Jashimuddin M, Alamgir M, Majumder R, Patwari MRA, Bhuiyan MAR (2004). Potentials visitors of Mirpur zoological garden as an outdoor recreation area of Dhaka, Bangladesh. Pakistan Journal of Biological Science 7(9): 1509-1512.
CrossRef | Gscholar
(21)
Landell-Mills N, Porras IT (2002). Silver bullet or fools’ gold? A global review of markets for forest environmental services and their impact on the poor. International Institute for Environment and Development, London, UK, pp. 254.
Gscholar
(22)
Lindberg K, Enriquez J (1994). An analysis of ecotourism’s economic contribution to conservation and development in Belize. WWF/Ministry of Tourism and Environment, Belize City, Belize, pp. 105.
Gscholar
(23)
Mehta JN, Kellert SR (1998). Local attitudes towards community-based conservation policy and programmers in Nepal: a case study of the Makalu-Barun conservation area. Environmental Conservation 25 (4): 320-333.
CrossRef | Gscholar
(24)
NACOM (2003). Site level appraisal for protected area co-management, Rema-Kalenga wildlife Sanctuary. Nature conservation management. International Resources Group, Dhaka press, Bangladesh.
Gscholar
(25)
Nath TK, Alauddin M (2006). Sitakunda botanical garden and eco-park, Chittagong, Bangladesh: its impacts on rural community. International Journal of Biodiversity Science and Management 2 (1): 1-11.
CrossRef | Gscholar
(26)
Nishat A, Huq S, Imamul M, Barua S, Reza P, Ali AHM, Khan MAS (2002). Bio-ecological zones of Bangladesh. IUCN, Bangladesh.
Gscholar
(27)
NSP (2006). Protected areas of Bangladesh: A visitor’s guide. Nishorgo Support Project, Dhaka, Bangladesh, pp. 41.
Gscholar
(28)
Okaka W (2007). The role of media communications in developing tourism policy and cross cultural communication for peace, security for sustainable tourism industry in Africa. In: Proceedings of the 4<sup>th</sup> International Institute of Peace through Tourism (IIPT), African Conference on Peace through Tourism at Educators’ Forum, Kampala (Uganda) 19-22 May 2007.
Gscholar
(29)
Rao K (1996). Management problems: people in protected areas. In: Proceedings of the “SAARC Workshop on Wildlife Management”. Dehradun, India.
Gscholar
(30)
Sekhar NU (2003). Local people’s attitudes towards conservation and wildlife tourism around Sariska Tiger Reserve, India. Journal of Environmental Management 69: 339-347.
CrossRef | Gscholar
(31)
Sharma R, DeCosse P, Khan M, Mazumder A (2005). Co-Management of protected areas in South Asia with special reference to Bangladesh. Nishorgo Support Project, Dhaka, Bangladesh, pp. 16.
Gscholar
(32)
Torkildsen G (1992). Leisure and recreation management. E and FN Spon, London, UK, pp. 463.
Gscholar
(33)
Uddin MZ (2002). Exploration, documentation and germplasm collection of plant genetic resources of Rema-Kalenga Wildlife Sanctuary (Habigong) in Bangladesh, Ph. D. Thesis, University of Dhaka, Bangladesh.
Gscholar
(34)
Vantomme P, Markkula A, Leslie RN (2002). Non-wood forest products in 15 countries of tropical Asia: a regional and national overview. FAO-RAP, Bangkok, Thailandia, pp. 15-24.
Gscholar
(35)
Walpole MJ, Goodwin HJ (2000). Local economic impacts of dragon tourism in Indonesia. Annals of Tourism Research 27: 559-576.
CrossRef | Gscholar
(36)
Walpole MJ, Goodwin HJ, Ward KGR (2001). Pricing policy for tourism in protected areas: lessons from Komodo National Park, Indonesia. Conservation Biology 15: 177-185.
CrossRef | Gscholar
(37)
Wells M, Brandon K, Hannah L (1992). People and Parks: linking protected area management with local communities. World Bank, Washington, DC, USA.
Gscholar
(38)
Wenger KF (1984). Forestry handbook. John Wiley and Sons, New York, USA.
Gscholar
(39)
Western D, Wright M (1994). Natural connections: perspectives in community-based conservation. Island Press, Washington, DC, USA.
Gscholar
(40)
Williams PW (1992). A local framework for ecotourism development. Western Wildlands 18 (3): 14-19.
Gscholar

Authors’ Affiliation

(1)
MP Rana
MSI Sohel
S Akhter
Q Chowdhury
Department of Forestry and Environmental Science, School of Agriculture and Mineral Sciences, Shahjalal University of Science and Technology, Sylhet- 3114 (Bangladesh)
(2)
SA Mukul
Institutute of International Forestry and Forest Products, Dresden University of Technology, 01735 Tharandt (Germany)
(3)
MSH Chowdhury
M Koike
Forest Policy Laboratory, Department of Forest Science, Faculty of Agriculture, Shinshu University, 8304 Minamiminowa-Mura, 399-4598 Nagano-Ken (Japan)

Corresponding author

Citation

Rana MP, Sohel MSI, Mukul SA, Chowdhury MSH, Akhter S, Chowdhury Q, Koike M (2010). Implications of ecotourism development in protected areas: a study from Rema-Kalenga Wildlife Sanctuary, Bangladesh. iForest 3: 23-29. - doi: 10.3832/ifor0520-003

Academic Editor

Marco Borghetti

Paper history

Received: Aug 07, 2009
Accepted: Oct 28, 2009

First online: Jan 22, 2010
Publication Date: Jan 22, 2010
Publication Time: 2.87 months

© SISEF - The Italian Society of Silviculture and Forest Ecology 2010

  Open Access

This article is distributed under the terms of the Creative Commons Attribution-Non Commercial 4.0 International (https://creativecommons.org/licenses/by-nc/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.

Creative Commons Licence

Breakdown by View Type

(Waiting for server response...)

Article Usage

Total Article Views: 57210
(from publication date up to now)

Breakdown by View Type
HTML Page Views: 48528
Abstract Page Views: 2669
PDF Downloads: 5255
Citation/Reference Downloads: 75
XML Downloads: 683

Web Metrics
Days since publication: 5201
Overall contacts: 57210
Avg. contacts per week: 77.00

Article citations are based on data periodically collected from the Clarivate Web of Science web site
(last update: Feb 2023)

Total number of cites (since 2010): 6
Average cites per year: 0.43

 
 

Publication Metrics

by Dimensions ©

List of the papers citing this article based on CrossRef Cited-by.

 

iForest Similar Articles

 

This website uses cookies to ensure you get the best experience on our website. More info