scholarly journals Land Use and Access in Protected Areas: A Hunter’s View of Flexibility

Forests ◽  
2020 ◽  
Vol 11 (4) ◽  
pp. 481
Author(s):  
Ayonghe Akonwi Nebasifu ◽  
Ngoindong Majory Atong

Anthropologists sometimes ask what flexible practices mean when used in instances of land use and access among protected area regimes which control the land and the indigenous or local people who claim rights to the land. In the Mount Cameroon National Park (MCNP), West Africa, this question comes with urgency because of the historical disputes associated with defining access and user-rights to land within this park. In this case, we present an ethnographic study using a transect walk with a native Bakweri hunter to map and analyze his opinions about land use and access into the park. The findings show that, despite State prohibitions for this park, customary practices still occur for mutual reasons, whereas, in situations of disputes, other practices continue on the land unnoticed. We conclude that this flexibility is indicative of reciprocal negotiations and cultural resilience that preserve not only the biodiversity of the park but also the culturally relevant needs of people.

Author(s):  
LIU Menghao ◽  
XI Jianchao

The optimization of the spatial structure and layout is to determine an optimal and cost-effective land-use allocation plan for protected areas. The key goal is to maximizing the value of ecosystem services. This paper establishes a framework for optimizing the spatial structure and layout of the protected area based on ecosystem services. With the objective of maximizing the value of ecosystem services, it uses the CoMOLA (Constrained Multi-objective Optimization of Land-use Allocation) model for multi-objective optimization under the constraints of area and conversion rules. Taking the Yellow River’s headwaters region in the Three-River-Source (Sanjiangyuan) National Park as the study area, this paper uses the data of the year 2015 as a benchmark, and obtains the optimization results of the study area by 2035. The results show that the total value of ecosystem services of the Yellow River’s headwaters region after optimization will reach RMB [Formula: see text], with a total increase of RMB [Formula: see text] (8.47%). The land covers that contribute most to the value of ecosystem services are rivers, lakes and wetlands (51.55%), and grasslands (40.71%). Among the various types of ecosystem services, the value of provisioning services will increase by RMB [Formula: see text], regulating services by RMB [Formula: see text], supporting services by RMB [Formula: see text], and cultural services by RMB [Formula: see text]. The research results can provide a scientific basis for the spatial optimization of protected areas and the management of national parks.


Author(s):  
Murat Atasoy

Protected areas are one the most important nature conservation landscapes and during the last few decades, the importance of natural areas have been considered as a priority for lifestyle preferences of people around the world. Karatepe Aslantaş National Park is one of the examples for these protected areas in Turkey, however; there have been limited studies focusing on the preservation and development of a socioeconomic plan for the aforementioned national park. Therefore, this study aims to develop planning and management priorities of Karatepe Aslantaş National Park and determine tourism potential towards future-oriented conservation. In this regard, a SWOT analysis was performed to develop sustainable planning and design proposals. To determine the historical transformation of a protected area and its surroundings, Land use/land cover-change (LUCC) detection was performed using Landsat 7 ETM and Landsat TIRS/OLI satellites images of the study area for the years 1990 and 2018. The results showed that in 1990, the mixed forest class dominated the study area (2376.6 ha), likewise, it was the most effective land cover class in 2018 (2178.14 ha). Agricultural land with natural vegetation class occupied the second largest area for both 1990 and 2018 with 1264.72 ha and 880.13 ha, respectively. A marked decrease was found for the transitional woodland/shrubs cover (565.8 ha in 1990 to 330.35 ha in 2018). Among the all land use classes, the highest percentage of change was found for broad-leaved forest cover at 200% between 1990 and 2018, while the lowest percentage of change occurred to water bodies with 8.82% in the same time frame. Regarding the findings, management proposals have been developed to conserve the protected area considering its tourism potential and archeological heritage values. Therefore, it is recommended that the lack of planning and management strategies needs to be fulfilled as a legal commitment by government agencies.


2021 ◽  
Author(s):  
AISDL

Creation of protected areas for biological conservation often conflicts with sustenance of livelihood of local people living inside or nearby regions. Combination between biological conservation and livelihood development has been much remained to be done in protected regions.


2019 ◽  
Vol 12 ◽  
pp. 194008291987037 ◽  
Author(s):  
Antonia Nyamukuru ◽  
John-Arvid Grytnes ◽  
John R. S. Tabuti ◽  
Ørjan Totland

Protected areas generally occur within a matrix of intensively human-modified landscapes. As a way to maintain the biodiversity in these areas, enclosure by fencing is often preferred. This strategy, however, is costly and little is known about the effectiveness of the alternative of unfenced borders on the vegetation and fauna. The objectives of this study are to assess whether there is a distinct difference in biodiversity and composition of plants and mammals between the protected Lake Mburo National Park and the adjacent ranchlands across an unfenced border and to determine the associations between vegetation and faunal species over the same border. We recorded herbaceous vegetation, woody vegetation, and mammal species composition in plots 300 to 500 m away from the border both inside the protected area and in the adjacent ranchlands. The species composition of herbs and mammals in the protected area differ from the adjacent ranchlands, but there is no difference for trees and shrubs. After accounting for land-use type, distance from the border did not significantly account for any additional variation. We also find a correlation between the species composition of vegetation and fauna. Our results suggest that unfenced borders around protected areas create a clear effect.


2019 ◽  
Vol 38 (5) ◽  
pp. 486-507
Author(s):  
Issara Phromma ◽  
Adcharaporn Pagdee ◽  
Ananya Popradit ◽  
Atsushi Ishida ◽  
Somkid Uttaranakorn

2020 ◽  
Author(s):  
Crescenzo Violante ◽  
Francesco Paolo Buonocunto ◽  
Eliana Esposito ◽  
Luciana Ferraro ◽  
Laura Giordano ◽  
...  

<p>The main goal of this study is to investigate the anthropic influence on benthic habitats in the Punta Campanella Marine Protected Area (MPA). This area is located at the western end of the Sorrento Peninsula in the Bay of Naples, southern Italy. It is a rocky coast consisting of vertical or near vertical limestone cliffs of structural control, with marine areas characterized by suboutcropping rocky substrate. Seabed sediments are mainly coarse and biogenic in origin with skeletal grains and coralligenous bioconstructions occurring widely [1].</p><p>The Punta Campanella seabed habitats have been characterized and mapped on the base of geophysical and sedimentological data together with results from benthic communities. In addition, several environmental components both marine and terrestrial have been analysed in order to evaluate the anthropic influence on the recognized benthic habitats. Such environmental components include foraminiferal assemblages, water column features and inorganic pollutants (heavy metals) as well as terrestrial biota, fresh water supply and quality, land use and natural hazard.</p><p>First results indicate 1) anomalous values of specific heavy metals (Ni, Hg) in the marine sediments, 2) the presence of benthic foraminiferal assemblages distinctive of human-impacted environmental conditions, and 3) the occurrence of morphological deformities affecting some foraminiferal species. At present, as next step of this study, we are applying a methodology based on the Environmental Functional Analysis (EFA) in order to combine and analyse terrestrial and marine environmental components together with territorial data and selected socio-economic components of the coastal zone (i.e. human pressure, land use, etc.) [2]. This method was originally developed by Cendrero and Fischer (1997) [3] and successively employed as management tool and monitoring technique for coastal areas [4] and terrestrial protected areas [5]. Such a holistic-based approach can be used to evaluate the anthropic disturbance in the Punta Campanella MPA and to compare the potential for conservation and the potential for use of the study area.</p><p><strong>References</strong></p><p>[1] D'Argenio B., Violante C., Sacchi M., Budillon F., Pappone G., Casciello E., Cesarano M., 2004: Capri, Bocca Piccola and Punta Campanella (southern Italy), marine and onland geology compared. In: G. Pasquarè and C. Venturini (Eds), Mapping Geology in Italy, APAT, Roma, 35-42.</p><p>[2] Hopkins, T.S., Bailly, D., Støttrup, J.G., 2011. A Systems Approach Framework for Coastal Zones. Ecol. Soc. 16(4), 25.</p><p>[3] Cendrero A., Fischer D.W., 1997: A procedure for assessing the environmental quality of coastal areas for planning and management. Journal of Coastal Research 13(3), 732-744.</p><p>[4] Giordano L., Ferraro L., 2020. Conservation or development? An environmental function analysis assessment of the Volturno River coastal zone (central Tyrrhenian Sea - Italy). Journal of Coastal Conservation, 24(6), 5-12.</p><p>[5] Calado H., Bragagnolo C., Silva S., Vergílio M., 2016: Adapting environmental function analysis for management of protected areas in small islands e case of Pico Island (the Azores). Journal of Environmental Management 171, 231-242.</p>


2015 ◽  
Vol 370 (1681) ◽  
pp. 20140274 ◽  
Author(s):  
Vanessa M. Adams ◽  
Samantha A. Setterfield ◽  
Michael M. Douglas ◽  
Mark J. Kennard ◽  
Keith Ferdinands

Protected areas remain a cornerstone for global conservation. However, their effectiveness at halting biodiversity decline is not fully understood. Studies of protected area benefits have largely focused on measuring their impact on halting deforestation and have neglected to measure the impacts of protected areas on other threats. Evaluations that measure the impact of protected area management require more complex evaluation designs and datasets. This is the case across realms (terrestrial, freshwater, marine), but measuring the impact of protected area management in freshwater systems may be even more difficult owing to the high level of connectivity and potential for threat propagation within systems (e.g. downstream flow of pollution). We review the potential barriers to conducting impact evaluation for protected area management in freshwater systems. We contrast the barriers identified for freshwater systems to terrestrial systems and discuss potential measurable outcomes and confounders associated with protected area management across the two realms. We identify key research gaps in conducting impact evaluation in freshwater systems that relate to three of their major characteristics: variability, connectivity and time lags in outcomes. Lastly, we use Kakadu National Park world heritage area, the largest national park in Australia, as a case study to illustrate the challenges of measuring impacts of protected area management programmes for environmental outcomes in freshwater systems.


Oryx ◽  
2010 ◽  
Vol 44 (3) ◽  
pp. 352-357 ◽  
Author(s):  
Jörn P. W. Scharlemann ◽  
Valerie Kapos ◽  
Alison Campbell ◽  
Igor Lysenko ◽  
Neil D. Burgess ◽  
...  

AbstractForest loss and degradation in the tropics contribute 6–17% of all greenhouse gas emissions. Protected areas cover 217.2 million ha (19.6%) of the world’s humid tropical forests and contain c. 70.3 petagrams of carbon (Pg C) in biomass and soil to 1 m depth. Between 2000 and 2005, we estimate that 1.75 million ha of forest were lost from protected areas in humid tropical forests, causing the emission of 0.25–0.33 Pg C. Protected areas lost about half as much carbon as the same area of unprotected forest. We estimate that the reduction of these carbon emissions from ongoing deforestation in protected sites in humid tropical forests could be valued at USD 6,200–7,400 million depending on the land use after clearance. This is > 1.5 times the estimated spending on protected area management in these regions. Improving management of protected areas to retain forest cover better may be an important, although certainly not sufficient, component of an overall strategy for reducing emissions from deforestation and forest degradation (REDD).


2015 ◽  
Vol 22 (3) ◽  
pp. 201-205
Author(s):  
Ludwik Mazurkiewicz ◽  
Justyna Pacelt

Abstract Introduction. Recreation is very popular in protected areas where the number of visitors is increasing from year to year. They are attracted by benefits provided by natural resources in the form of favorable conditions to spend time for leisure. These benefits have a specified value which is known as a recreational one. In this paper a method is presented how to measure it. Material and methods. The method is an extension of an approach known as the travel cost method. The extension consists in taking additional assumptions into account like needs that drive people to recreate in protected areas and as a result the recreational and health value of the area is estimated more precisely. The calculation was realized on data collected by a survey based on an interview questionnaire among 60 respondents in the Kampinoski National Park in the second half of July 2014. Results. The recreational and health value estimated on the results obtained from 60 respondents amounted to 235 837 PLN and 165 194 PLN respectively. The article presents also more detailed calculations of the selected surveys. Conclusions. The factors which contribute in a decisive way into the area recreational and health value are the number of visits, the share of a health motive and the length of stay. There are also other factors of lesser contribution into the value like: the time of getting the area, the cost of its reaching and the sum respondents declared to pay for the area protection.


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