Patterns of forest cover change and their association with forest management regimes of forest reserves in the high forest zone of Ghana

2019 ◽  
Vol 14 (3) ◽  
pp. 242-257 ◽  
Author(s):  
Frank Ankomah ◽  
Boateng Kyereh ◽  
Winston Asante ◽  
Michael Ansong
2020 ◽  
Vol 2020 ◽  
pp. 1-14
Author(s):  
Frank Ankomah ◽  
Boateng Kyereh ◽  
Michael Ansong ◽  
Winston Asante

Forest cover loss, particularly those arising from deforestation and forest degradation, is largely driven by human activities and has attracted global attention over the decades. Globally, countries have adopted strategies to manage and conserve forests in response to these human disturbances. Ghana’s strategy to ensure sustainable management of the forest and its estate was to zone the forest into management regimes based on the resource availability and the object of managing those particular areas. Whilst forest degradation and its drivers and actors have been widely reported in Ghana, it is not known how forest management regimes influence these issues. Focusing on four forest reserves in the high forest zone of Ghana, this paper used interviews of key forest stakeholders, analysis of Forestry Commission field reports, and field verification to demonstrate the effect of forest management regimes on drivers of forest degradation. A combination of many proximate and underlying factors was observed to drive degradation in a synergetic way. The main drivers which were identified and their corresponding actors varied and manifested differently across management regimes. The strive by forest landowners to earn revenue from the protected forest, perceived unfair payment of ground rents for protected areas by Timber Utilization Contract holders, poor forest management practices on the part of forestry personnel, nondeterrent penalties, poor forest monitoring, the granting of compartment re-entry permits to harvest residual yield, overdependence on few species, weak enforcement of forest regulations, and perceived corruption on the part of forestry officials were the major underlying factors that impact on how the drivers manifested in various regimes. Our study reveals that the primary forest stakeholders of the country are the main actors of forest degradation and have developed various means convenient for specific regimes that enable them to benefit from the forest at the expense of conservation.


2018 ◽  
pp. 38-44
Author(s):  
B. K. Pokharel ◽  
D. R. Uprety ◽  
R. R. Niraula ◽  
P. R. Pokharel

A study was conducted in the Churia region in 2014 to assess the change in forest cover as an outcome of the performance of various forest management regimes and silvicultural practices with the main objective to find the gap between those two. Geographic Information System (GIS) and Remote Sensing (RS) were used to compare the satellite imageries for the period of 1992 to 2014 in order to analyse the state of forest cover change. The demarcation of community forest boundaries was conducted based on available boundary maps and transferred to Google earth and GIS platform. Results showed that overall forest cover in the Churia region was increased by 7500 ha (1%) in 22 years, i.e. 1.35 million ha (76%) in 1992 to 1.36 million ha (77%) in 2014. The rate of deforestation in the Churia region was reduced as compared to the national average. However, degradation of landscape was visible at riverbeds and cultivation lands close to the riverbeds. It was also found that the area of dense forest was increased by 42,000 ha, whereas the area covered by bushes and grassland was reduced by 39,000 ha. The study further showed that there was a decline in cultivated land by 20,000 ha. Comparing the forest cover change in community forests with that of other management regimes, silvicultural practices in community forest areas have brought relatively better positive changes in the forest condition. It may be due to periodic silviculture operations carried out collectively by local communities. In the assessment, however, various elements of tenure rights and responsibilities of community, government and private forest and tree owners were identified and key silvicultural practices adopted by these regimes were highlighted as the drivers of positive or negative outcomes of forest cover change. Banko JanakariA Journal of Forestry Information for Nepal Special Issue No. 4, 2018, Page : 36-44 


2013 ◽  
Vol 02 (01) ◽  
pp. 1-9 ◽  
Author(s):  
Japhet J. Kashaigili ◽  
Makarius V. Mdemu ◽  
Augustino R. Nduganda ◽  
Boniface P. Mbilinyi

2007 ◽  
Vol 46 (4II) ◽  
pp. 1189-1203 ◽  
Author(s):  
Lubna Hasan

Deforestation remains one of the most intractable environmental problems of today. About one third the size of the original forest cover has disappeared so far. Despite continuous efforts by the world community to curb this process, deforestation continues unabated in most parts of the world, with serious consequences for the human livelihoods, eco systems, and global climate. Pakistan also faces serious problem of depletion of its forest reserves. Approximately 39000 ha of forest are being cleared every year.1 If deforestation continues at this pace, it is feared that Pakistan will lose most of its forest within the next thirty to forty years. Being a forest poor country, with forest occupying less than 5 percent of total land area,2 protection of its forest resources is a vital task. Forest management faces many challenges in Pakistan. Forests face tremendous pressure, not only from a population of 160 million people for meeting their needs3 (be it only subsistence needs), but also from market forces which have seen soaring timber prices for many years now. Forest department is ill equipped to counter these challenges. It lacks human and financial resources, and relevant technical expertise.


2020 ◽  
Author(s):  
Andrey N. Shikhov ◽  
Alexander V. Chernokulsky ◽  
Igor O. Azhigov ◽  
Anastasia V. Semakina

Abstract. Severe winds are among the main causes of natural disturbances in boreal and temperate forests. Here, we present a new GIS database of stand-replacing windthrows in the forest zone of the European Russia (ER) for the 1986–2017 period. Delineation of windthrows was based on the full archive of Landsat images and two Landsat-derived products on forest cover change, namely the Global Forest Change and the Eastern’ Europe Forest Cover Change datasets. Subsequent verification and analysis of each windthrow was carried out to determine a type of related storm event, its date or date range, and geometrical characteristics. The database contains 102 747 elementary areas of damaged forest that were combined into 700 windthrows caused by 486 convective or non-convective storm events. The database includes stand-replacing windthrows only, which an area > 5 ha and > 25 ha for events caused by tornadoes and other storms, respectively. Additional information contained weather station reports and event description from media sources is also provided. The total area of windthrows amounts to 2966 km2, that is 0.19 % of the forested area of the study region. Convective windstorms contribute 82.5 % to total wind-damaged area, while tornadoes and non-convective windstorms are responsible for 12.9 % and 4.6 % of this area, respectively. Most of windthrows in the ER happen in to summer that is in contrast to Western and Central Europe, where windthrows mainly occur in autumn and winter. The compiled database provides a valuable source of spatial and temporal information on windthrows in the ER and can be successfully used both in forest science and severe storm studies. The database is available at https://doi.org/10.6084/m9.figshare.12073278.v3 (Shikhov et al., 2020).


2011 ◽  
Vol 10 ◽  
pp. 16-21
Author(s):  
Rabindra Man Tamrakar

Greenhouse effect causes global warming and its main consequence is the climate change. Average global temperature is rising significantly over the period. Despite the contribution of total GHG emission by Nepal to the global community is insignificant compared to the developed countries, Nepal has already encountered several adverse effects due to the global climate change, leading to the melting of Himalayan glaciers, reduced agriculture production, loss of biodiversity and ecosystems and changes in social structure and livelihoods. Forest land use change is responsible for CO2 emissions. Forest management therefore can play a significant role in climatic change mitigation. REDD has become the key mechanism in mitigating climate change. The success of REDD mechanism however depends primarily on availability of reliable forestry data including biomass changes and forest carbon estimates. Various Remote Sensing data including optical sensor data have been used for the analysis of forest cover change and estimation of degree of deforestation and degradation. LiDAR however has been widely used in estimating forest biomass for the climate change mitigation.


2020 ◽  
Vol 12 (4) ◽  
pp. 3489-3513
Author(s):  
Andrey N. Shikhov ◽  
Alexander V. Chernokulsky ◽  
Igor O. Azhigov ◽  
Anastasia V. Semakina

Abstract. Severe winds are among the main causes of disturbances in boreal and temperate forests. Here, we present a new geographic information system (GIS) database of stand-replacing windthrow events in the forest zone of European Russia (ER) for the 1986–2017 period. The delineation of windthrow areas was based on the full Landsat archive and two Landsat-derived products on forest cover change, namely the Global Forest Change and the Eastern Europe's forest cover change datasets. Subsequent verification and analysis of each windthrow was carried out manually to determine the type of related storm event, its date or date range, and geometrical characteristics. The database contains 102 747 elementary areas of damaged forest that were combined into 700 windthrow events caused by 486 convective or non-convective storms. The database includes stand-replacing windthrows only with an area > 0.05 and > 0.25 km2 for the events caused by tornadoes and other storms, respectively. Additional information such as weather station reports and event descriptions from media sources is also provided. The total area of stand-replacing windthrows amounts to 2966 km2, which is 0.19 % of the forested area of the study region. Convective windstorms contribute 82.5 % to the total wind-damaged area, while tornadoes and non-convective windstorms are responsible for 12.9 % and 4.6 % of this area, respectively. Most of the windthrow events in ER happened in summer, which is in contrast to Western and Central Europe, where they mainly occur in autumn and winter. Due to several data and method limitations, the compiled database is spatially and temporally inhomogeneous and hence incomplete. Despite this incompleteness, the presented database provides a valuable source of spatial and temporal information on windthrow in ER and can be used by both science and management. The database is available at https://doi.org/10.6084/m9.figshare.12073278.v6 (Shikhov et al., 2020).


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