Primary forest cover loss in Indonesia over 2000–2012

2014 ◽  
Vol 4 (8) ◽  
pp. 730-735 ◽  
Author(s):  
Belinda Arunarwati Margono ◽  
Peter V. Potapov ◽  
Svetlana Turubanova ◽  
Fred Stolle ◽  
Matthew C. Hansen
Keyword(s):  
Forest Cover ◽  
Primary Forest ◽  
Forest Cover Loss

scholarly journals Forest Management Regimes and Drivers of Forest Cover Loss in Forest Reserves in the High Forest Zone of Ghana

2020 ◽  
Vol 2020 ◽  
pp. 1-14
Author(s):  
Frank Ankomah ◽  
Boateng Kyereh ◽  
Michael Ansong ◽  
Winston Asante
Keyword(s):  
Forest Management ◽  
Management Practices ◽  
Forest Cover ◽  
Forest Degradation ◽  
Forest Monitoring ◽  
Primary Forest ◽  
Forest Zone ◽  
Forest Reserves ◽  
Management Regimes ◽  
Forest Cover Loss

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.

scholarly journals Haiti’s biodiversity threatened by nearly complete loss of primary forest

2018 ◽  
Vol 115 (46) ◽  
pp. 11850-11855 ◽  
Author(s):  
S. Blair Hedges ◽  
Warren B. Cohen ◽  
Joel Timyan ◽  
Zhiqiang Yang
Keyword(s):  
Tropical Forests ◽  
National Parks ◽  
Mass Extinction ◽  
Forest Cover ◽  
Secondary Growth ◽  
Complete Loss ◽  
Primary Forest ◽  
The Difference ◽  
Primary Forests ◽  
Agricultural Organization

Tropical forests hold most of Earth’s biodiversity. Their continued loss through deforestation and agriculture is the main threat to species globally, more than disease, invasive species, and climate change. However, not all tropical forests have the same ability to sustain biodiversity. Those that have been disturbed by humans, including forests previously cleared and regrown (secondary growth), have lower levels of species richness compared with undisturbed (primary) forests. The difference is even greater considering extinctions that will later emanate from the disturbance (extinction debt). Here, we find that Haiti has less than 1% of its original primary forest and is therefore among the most deforested countries. Primary forest has declined over three decades inside national parks, and 42 of the 50 highest and largest mountains have lost all primary forest. Our surveys of vertebrate diversity (especially amphibians and reptiles) on mountaintops indicates that endemic species have been lost along with the loss of forest. At the current rate, Haiti will lose essentially all of its primary forest during the next two decades and is already undergoing a mass extinction of its biodiversity because of deforestation. These findings point to the need, in general, for better reporting of forest cover data of relevance to biodiversity, instead of “total forest” as defined by the United Nation’s Food and Agricultural Organization. Expanded detection and monitoring of primary forest globally will improve the efficiency of conservation measures, inside and outside of protected areas.

scholarly journals Causes for Deforestation in Indonesia: Corruption and Palm Tree Plantation

2015 ◽  
Vol 11 (27) ◽  
pp. 120
Author(s):  
Osama Eldeeb ◽  
Petr Prochazka ◽  
Mansoor Maitah
Keyword(s):  
Time Series ◽  
Palm Oil ◽  
Forest Cover ◽  
Palm Tree ◽  
Test Statistics ◽  
Crude Palm Oil ◽  
Tree Plantation ◽  
Long Run ◽  
Corruption Perception ◽  
Forest Cover Loss

<p>Indonesian biodiversity is threatened by massive deforestation. In this research paper, claims that deforestation in Indonesia is caused by corruption and supported by crude palm oil production is verified using time series analysis. Using Engel Granger cointegration test, three time series of data, specifically corruption perception index, rate of deforestation and price of crude palm oil are inspected for a long-run relationship. Test statistics suggests that there is no long-run relationship among these variables. Authors provide several explanations for this result. For example, corruption in Indonesia, as measured by CPI is still very high. This may mean that forest cover loss is possible even though there is a positive change in corruption level. According to the results, crude palm oil price has also no effect upon forest cover loss. This is likely due to very low shut-down price of crude palm oil for which production is still economical.</p>

scholarly journals Mountain wood-pastures and forest cover loss in Romania

2020 ◽  
pp. 1-13
Author(s):  
Magdalena Drăgan ◽  
Gabriela-Alina Mureşan ◽  
József Benedek
Keyword(s):  
Forest Cover ◽  
Forest Cover Loss

scholarly journals Realities of rarity: climatically and ecologically restricted, critically endangered Kandian Torrent Toads (Adenomus kandianus) breed en masse

2015 ◽  
Author(s):  
Madhava Meegaskumbura ◽  
Nayana Wijayathilaka ◽  
Nirodha Abayalath ◽  
Gayani Senevirathne
Keyword(s):  
Forest Cover ◽  
High Elevation ◽  
Habitat Associations ◽  
Egg Laying ◽  
Primary Forest ◽  
Isolated Populations ◽  
In The Wild ◽  
Suitable Habitats ◽  
Wide Geographic Distribution ◽  
Forest Habitats

Endemic to Sri Lanka, genus Adenomus contains two torrent-associated toad species whose ecology and natural history in the wild is virtually unknown. Adenomus kelaartii is relatively common, with a wide geographic distribution. Its sister species, A. kandianus, however, is restricted to two isolated populations in fast-disappearing montane and sub-montane forests. Formally declared extinct after not being recorded for over a century, a few A. kandianus were rediscovered in 2012 and redescribed as "the world's rarest toad". Here we report the results of a two-year study of the occurrence, habits and habitat associations of adult and larval A. kandianus using both general surveys and quadrat sampling. We show this to be a secretive species with a patchy distribution. Non-breeding female toads dwell in primary-forest habitats, but after heavy and sudden downpours they form large mating congregations in large streams. Amplexed pairs swim synchronously, enabling them to traverse fast currents. Egg-laying sites remain unknown, but the ability to dive and vocalize underwater, and characteristics of the eggs, suggest that they lay eggs in dark recesses of the stream. Tadpoles show microhabitat partitioning within the stream, with the greatest diversity of stages in slow-flowing rocky areas. The more robust stages possessing sucker discs exploit rocky-rapids, while metamorphic stages inhabit stream margins. We use DNA-barcoding to show the existence of two disparate toad populations. Distribution modeling with forest-cover layers added, predict a very small remaining area of suitable habitats. Conservation of this climatically and ecologically restricted species hinge largely on the preservation of high-elevation primary and riparian forests and unpolluted torrents.

scholarly journals Assessing Harvested Sites in a Forested Boreal Mountain Catchment through Global Forest Watch

2019 ◽  
Vol 11 (5) ◽  
pp. 543 ◽  
Author(s):  
Fernando Rossi ◽  
Johannes Breidenbach ◽  
Stefano Puliti ◽  
Rasmus Astrup ◽  
Bruce Talbot
Keyword(s):  
Forest Cover ◽  
Risk Mitigation ◽  
Landsat Imagery ◽  
Aerial Images ◽  
Catchment Management ◽  
South Central ◽  
Cable Yarding ◽  
The Mean ◽  
Steep Terrain ◽  
Forest Cover Loss

Global Forest Watch (GFW) provides a global map of annual forest cover loss (FCL) produced from Landsat imagery, offering a potentially powerful tool for monitoring changes in forest cover. In managed forests, FCL primarily provides information on commercial harvesting. A semi-autonomous method for providing data on the location and attributes of harvested sites at a landscape level was developed which could significantly improve the basis for catchment management, including risk mitigation. FCL in combination with aerial images was used for detecting and characterising harvested sites in a 1607 km2 mountainous boreal forest catchment in south-central Norway. Firstly, the forest cover loss map was enhanced (FCLE) by removing small isolated forest cover loss patches that had a high probability of representing commission errors. The FCLE map was then used to locate and assess sites representing annual harvesting activity over a 17-year period. Despite an overall accuracy of >98%, a kappa of 0.66 suggested only a moderate quality for detecting harvested sites. While errors of commission were negligible, errors of omission were more considerable and at least partially attributed to the presence of residual seed trees on the site after harvesting. The systematic analysis of harvested sites against aerial images showed a detection rate of 94%, but the area of the individual harvested site was underestimated by 29% on average. None of the site attributes tested, including slope, area, altitude, or site shape index, had any effect on the accuracy of the area estimate. The annual harvest estimate was 0.6% (standard error 12%) of the productive forest area. On average, 96% of the harvest was carried out on flat to moderately steep terrain (<40% slope), 3% on steep terrain (40% to 60% slope), and 1% on very steep terrain (>60% slope). The mean area of FCLE within each slope category was 1.7 ha, 0.9 ha, and 0.5 ha, respectively. The mean FCLE area increased from 1.0 ha to 3.2 ha on flat to moderate terrain over the studied period, while the frequency of harvesting increased from 249 to 495 sites per year. On the steep terrain, 35% of the harvesting was done with cable yarding, and 62% with harvester-forwarder systems. On the very steep terrain (>60% slope), 88% of the area was harvested using cable yarding technology while harvesters and forwarders were used on 12% of the area. Overall, FCL proved to be a useful dataset for the purpose of assessing harvesting activity under the given conditions.

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