Are Soils in Degraded Dipterocarp Forest Ecosystems Deteriorated? A Comparison of Imperata Grasslands, Degraded Secondary Forests, and Primary Forests

2000 ◽  
pp. 49-57 ◽  
Author(s):  
Seiichi Ohta ◽  
Kazuhito Morisada ◽  
Nagaharu Tanaka ◽  
Yoshiyuki Kiyono ◽  
Syarif Effendi
Keyword(s):  
Forest Ecosystems ◽  
Secondary Forests ◽  
Dipterocarp Forest ◽  
Primary Forests

Bewirtschaftung von tropischen Sekundärwäldern

2002 ◽  
Vol 46 (1) ◽  
Author(s):  
Dietrich Schmidt-Vogt
Keyword(s):  
Land Use ◽  
Forest Cover ◽  
Stand Structure ◽  
Secondary Forest ◽  
Secondary Forests ◽  
Tropical Asia ◽  
Land Use Systems ◽  
The Future ◽  
The Tropics ◽  
Primary Forests

AbstractManagement of secondary tropical forests: a new perspective for sustainable use of forests in Asia. The decline of primary forests in the tropics is leading to a reassessment of the role secondary forests might play within the context of tropical forest management. Recent research has shown that secondary forests in the tropics can be both rich in species and complex in terms of stand structure. There is, moreover, a growing recognition of the importance of secondary forests for traditional subsistence economies in the tropics and of their economic potential for land use systems in the future. Management of secondary forests in Asia as an alternative to the extraction of timber from primary forests but also as one among other options to intensify traditional land use systems has a potential for the future especially because of the existence of vast tracts of valuable secondary forest cover, and because of the store of traditional knowledge that can still be found in tropical Asia.

scholarly journals ANALISIS KEBERADAAN PAKAN ORANGUTAN DAN INDEKS SHANNON-WIENER PADA AREA REBOISASI ASRI DI KAWASAN TAMAN NASIONAL GUNUNG PALUNG

2020 ◽  
Vol 10 (1) ◽  
Author(s):  
Nurul Ihsan Fauzi ◽  
Erina Safitri ◽  
Juliansyah Juliansyah ◽  
Farah Diba
Keyword(s):  
Data Collection ◽  
Forest Restoration ◽  
National Park ◽  
Forest Ecosystems ◽  
Stable Condition ◽  
Wiener Index ◽  
The Past ◽  
Restoration Site ◽  
A Value ◽  
Primary Forests

Gunung Palung National Park had lost 35% of its primary forests over the past 30 years. A forest restoration program is thus vital to restore the damaged forest ecosystems. This study aims to analyze the presence of orangutan food supply and Shannon-Wiener index at Alam Sehat Lestari (ASRI) restoration site in Gunung Palung National Park. The method applies a species data collection of orangutan food (in 91 sample plots) and calculation of Shannon-Wiener index (in six 2009's plots). The result depicted approximately 65 species from 25 families found in ASRI restoration site. Eighty percent of those species indicated orangutan food.  In addition, the restoration site is believed to prevent the orangutan conflict with a human due to food availability in restoration areas for orangutans. Analysis of the Shannon-Wiener index (H') demonstrated a value of H' = 2.789, which indicated that the reforestation forest was in stable condition. The effect of increasing biodiversity as characterized by orangutan nests at restoration sites escalates the presence of wildlife.Keywords: Forest Restoration, Gunung Palung National Park, OrangutanTaman Nasional (TN) Gunung Palung telah kehilangan 35% hutan primer selama 30 tahun terakhir. Program reboisasi diperlukan untuk mengembalikan ekosistem hutan yang telah rusak. Tujuan penelitian ini adalah untuk menganalisis keberadaan pakan orangutan dan indeks Shannon-Wiener di area reboisasi yang dilakukan oleh Yayasan Alam Sehat Lestari (ASRI) di kawasan TN Gunung Palung. Metode yang digunakan adalah monitoring terhadap 91 plot untuk identifikasi pakan orangutan dan 6 plot penanaman tahun 2009 untuk perhitungan indeks Shanon-Wiener. Hasilnya terdapat 65 spesies dari 25 suku yang ditemukan di lokasi reboisasi ASRI. Sebanyak 85% dari spesies tersebut adalah pakan orangutan. Selain itu, keberadaan area reboisasi membantu mencegah konflik ini karena orangutan dapat mencari makanan di area reboisasi. Analisis indeks Shannon-Wiener (H’) didapatkan nilai H’ = 2,789, yang menunjukkan hutan hasil reboisasi berada dalam kondisi menengah atau stabil. Efek peningkatan biodiversitas ditandai dengan sarang-sarang orangutan ditemukan di lokasi reboisasi dan keberadaan satwa liar telah meningkat. Kata kunci: Gunung Palung, Orangutan, Restorasi hutan

scholarly journals Recovery of Functional Diversity Following Shifting Cultivation in Tropical Monsoon Forests

Forests ◽  
2018 ◽  
Vol 9 (9) ◽  
pp. 506 ◽  
Author(s):  
Fuying Deng ◽  
Yunling He ◽  
Runguo Zang
Keyword(s):  
Functional Diversity ◽  
Functional Traits ◽  
Shifting Cultivation ◽  
Forest Ecosystems ◽  
Recovery Process ◽  
Secondary Forests ◽  
Old Growth ◽  
Old Growth Forests ◽  
Tropical Monsoon ◽  
Monsoon Forests

The relationship between biodiversity and ecosystem functioning is an important issue in ecology. Plant functional traits and their diversity are key determinants of ecosystem function in changing environments. Understanding the successional dynamics of functional features in forest ecosystems is a first step to their sustainable management. In this study, we tested the changes in functional community composition with succession in tropical monsoon forests in Xishuangbanna, China. We sampled 33 plots at three successional stages—~40-year-old secondary forests, ~60-year-old secondary forests, and old growth forests—following the abandonment of the shifting cultivation land. Community-level functional traits were calculated based on measurements of nine functional traits for 135 woody plant species. The results show that the community structures and species composition of the old-growth forests were significantly different to those of the secondary stands. The species diversity, including species richness (S), the Shannon–Weaver index (H), and Pielou’s evenness (J), significantly increased during the recovery process after shifting cultivation. The seven studied leaf functional traits (deciduousness, specific leaf area, leaf dry matter content, leaf nitrogen content, leaf phosphorus content, leaf potassium content and leaf carbon content) changed from conservative to acquisitive syndromes during the recovery process, whereas wood density showed the opposite pattern, and seed mass showed no significant change, suggesting that leaf traits are more sensitive to environmental changes than wood or seed traits. The functional richness increased during the recovery process, whereas the functional evenness and divergence had the highest values in the 60-year-old secondary communities. Soil nutrients significantly influenced functional traits, but their effects on functional diversity were less obvious during the secondary succession after shifting cultivation. Our study indicates that the recovery of tropical monsoon forests is rather slow; secondary stands recover far less than the old growth stands in terms of community structure and species and functional diversity, even after about half a century of recovery, highlighting the importance of the conservation of old growth tropical monsoon forest ecosystems.

scholarly journals Diversity and distribution of oribatid mites (Acari:Oribatida) in a lowland rain forest in Peru and in several environments of the Brazilians States of Amazonas, Rondônia, Roraima and Pará

2006 ◽  
Vol 66 (4) ◽  
pp. 999-1020 ◽  
Author(s):  
E. Franklin ◽  
E. M. R. Santos ◽  
M. I. C. Albuquerque
Keyword(s):  
Rain Forest ◽  
Oribatid Mites ◽  
Taxonomic Resolution ◽  
Home Ranges ◽  
Secondary Forests ◽  
Lowland Rain Forest ◽  
Central Amazon ◽  
Current State ◽  
Northern Brazil ◽  
Primary Forests

We are summarizing the current state of knowledge of the diversity and distribution of oribatid mites in 26 environments in northern Brazil and of a rain forest in Peru. the published studies were mostly concentrated in central amazon. Only one report is a result from an agricultural polyculture. We are providing the first lists of species for savannas and for the brazilian states of Roraima and Pará. up to date, 146 species are definitively identified from a total of 444 taxa with 188 known genera, reinforcing the notion of a rich biodiverse area. the high number of 298 non-described species (morphospecies) clearly shows the inadequacy of the current taxonomic knowledge for the region. most of the registers are from forest environments. in the soil from primary forests, we registered the highest diversity (54-155 species/morphospecies). eighty-nine species were unique to primary forests, followed by 34 for savannas, 32 in trees, 10 in "igapó", 4 in caatinga, 3 in secondary forests, two in "várzea" and one in polyculture. twenty genera were the most speciose. the species with the largest home ranges were Rostrozetes foveolatus, Scheloribates sp. a, and Galumna sp. a. our numbers reflect the lack of taxonomists and show that the taxonomic knowledge must be improved for the region or we will continue to work with taxonomic resolution of order or family and a high percentage of morphospecies, which will probably be appropriate to the question being asked in each study, but not for a comparison among environments.

scholarly journals Stock de carbone dans les gros débris ligneux végétaux : cas des forêts tropicales pluvieuses de la Likouala, République du Congo

2017 ◽  
Vol 13 (12) ◽  
pp. 384
Author(s):  
Suspense Averti Ifo ◽  
Mackline Mbemba ◽  
Félix Koubouana ◽  
Stoffenne Binsangou
Keyword(s):  
Coarse Woody Debris ◽  
Woody Debris ◽  
Carbon Stocks ◽  
Congo Basin ◽  
Large Woody Debris ◽  
Primary Forest ◽  
Secondary Forests ◽  
Republic Of Congo ◽  
Primary Forests ◽  
Experimental Plots

In order to improve the knowledge of the functioning of tropical rainfall forests in the Congo basin ,a study on the quantification of the stocks of carbon in coarse woody debris was done in Likouala’s area, in Republic of Congo. To achieve this goal,14 squares plots of 50mx50m had installed on the whole study area, including ten plots in primary forest and four in secondary forests. The method used was to make an inventory of woody debris lying on the ground or Log and snags in the different study plots. There sults of this study revealed average stocks of 603.45kg MS.ha -1 in primary forests, 468.64 kg MS.ha-1 in secondaryforestsand392.68 kgMS.ha- 1 in agroforestry, with no significant differences between stocks in primary forests and secondary forests (P = 0.05). In addition this study revealed that carbon stocks varied from one locality to another in all the study area, as well as between the experimental plots (p = 0.005). This study helps to understand that the Chablis played a key role in the production of large woody debris.

scholarly journals KEANEKARAGAMAN DAN KEMERATAAN BURUNG PADA BERBAGAI TIPE HABITAT DI DESA ARTAIN KECAMATAN ARANIO KABUPATEN BANJAR KALIMANTAN SELATAN

2021 ◽  
Vol 9 (2) ◽  
pp. 405
Author(s):  
Basuki Rahman ◽  
Abdi Fithria ◽  
Basir Achmad ◽  
Danang Biyatmoko
Keyword(s):  
Secondary Forest ◽  
Habitat Type ◽  
Bird Species ◽  
Observation Point ◽  
Primary Forest ◽  
Secondary Forests ◽  
And Function ◽  
The Village ◽  
Primary Forests ◽  
Forest Habitats

Artain is a village located opposite the Riam Kanan reservoir in Aranio District, Banjar Regency, South Kalimantan Province. There are various types of habitat in the Village, from the edge of a reservoir to primary forest which is thought to be home to various birds species, which over time has the potential to degrade or change due to human activity which then reduces its quality and function as habitat for many birds species. It is necessary to research the diversity and evenness of birds in each habitat type in Artain, so that the existence of various bird species can be known. The research was conducted from May to June 2020, the method used in the study was the cruising circumference point, which is determining the observation point and its radius and then making observations by exploring the observation path continue. The results showed that there were 9 types of bird's habitat in Artain, they are Settlements, Periphery Reservoirs, Shrubs, Mixed Gardens, Rubber Gardens, Reeds, Fields, Secondary Forests, and Primary Forests. The lowest diversity value (H' = 1.25) was identified in field habitats and the highest (H' = 3.17) in scrub habitats, meaning that the level of diversity in all habitats was classified as moderate. The lowest evenness value in secondary forest habitats (E = 0.80) and the highest is mixed garden habitats and rubber gardens (E = 0.97), which means that evenness in each habitat is in the high category.

scholarly journals ANALISIS KANDUNGAN BIOMASSA DAN KARBON TERSIMPAN (Carbon Stock) PADA PSP (Plot Sampling Parmanent) HUTAN NEGERI SOYA KOTA AMBON.

2016 ◽  
Vol 1 (1) ◽  
pp. 72 ◽  
Author(s):  
Yulianus D Komul ◽  
Gun Mardiatmoko ◽  
Rohny S. Maail
Keyword(s):  
Carbon Stock ◽  
Secondary Forest ◽  
Forest Biomass ◽  
Carbon Stocks ◽  
Primary Forest ◽  
Total Biomass ◽  
Secondary Forests ◽  
Plot Sampling ◽  
Primary Forests ◽  
Sampling Plot

Carbon stocks while amount of carbon stored on vegetation, other biomass and soil. Effort to reduce greenhouse gas concentrations at atmosphere (emissions) ito reduce CO2 into air. Amount of CO2 on air must be controlled by increasing of CO2 by plants as much as possible and reducing release of emissions as low as possible. Carbon stored reserves should be measured as attempt to carbon stocks in forest to decrease carbon emissions and adverse effects. Research do in September 2015 at parmanent sampling plot on 2012 at Soya included Mount Sirimau . Method of biomass and carbon stocks on Measurement and Calculation of Carbon Stock overall primary forests and secondary forests consist of 409. Total biomass content for For strata of primary forest biomass is 510 with 3590 tons / ha - 786.6950 tons / ha with average content of biomass at 640.4733 tons/ ha. .At secondary forest is 210.1608 tons / ha to 436.6976 tons / ha with 289.4509 tons / ha. Carbon-stored at primary forest is 239.9190 tons / ha to 369.0228 tons / ha with 301.1112 tons / ha. On secondary forest amount of carbon stored is 88.9805 tons / ha to 139.7868 tons / ha and 110.1785 tons / ha.

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