Fire and land use effects on biodiversity in the southern Sumatran wetlands

We studied the long-term effects of an intensified fire regime following logging and altered land use practices on the biodiversity and successional dynamics of forests on three sites (Sugihan, Mesuji, and Pampangan) of roughly 300 km2 each, distributed across the continuous wetland ecosystem of southern Sumatra. Satellite image analysis and ecological and socio-economic surveys were combined to reveal the vegetation characteristics, and links to fire, land use history, and site conditions. Since the 1970s–1980s, this ecosystem has been subject to widespread repeated fires associated with or following intensive logging, transmigration, and plantation development, sonor or swamp rice cultivation, and other local resource use. Burn traces in the soil profile suggest that earlier fire episodes were far more limited in their coverage than the severe and frequent burning of the recent past. The result has been a rapid transformation from mature, high mixed species forests to sedge grasslands, savannas, and open to dense mono-specific stands of fast-growing fire-adapted species. Current vegetation types are largely differentiated by structural rather than compositional differences, which are significantly linked to fire frequency or time since last fire. The more frequent and recent the fires, the more open the landscape, with reduced density and basal area of trees. At present, the area is very species-poor. Most patches in Sugihan and Mesuji are dominated by a single species—Melaleuca cajuputi—in the tree, sapling, and seedling layers except for degraded mixed forests which have a mix of species in all layers. Degraded mixed forests were more recently logged and burnt just once in 1991. Pampangan has a different species composition with all patches dominated by Combretocarpus rotundatus in the tree layer, which is linked to greater organic matter depth. However, in the deep peats of Pampangan the sapling and seedling layers are also dominated by Melaleuca cajuputi in most patches suggesting a future shift in overstory composition to this more freshwater wetland-adapted species. This compositional shift is likely due to peast subsidence and increased likelihood of flooding following repeated burning. The live fuel structure with tall, dense lower strata to mid-strata of flammable herbaceous and woody species and scattered to dense tree cover renders all the vegetation types extremely fire-prone in dry years. The flammable vegetation combined with increased development and population pressures on these last frontiers makes contiued wides pread fires highly likely. This will lead to further simplification of species composition and structure, and degradation of the landscape into treeless plains. Resource depletion has led to falling incomes and fewer livelihood options in southern Sumatra. Fires and their negative impacts have expanded into the northern provinces of Sumatra as well with timber and oil palm plantation development and/or migrating populations in search of livelihood options. Given the large contribution of peatland fires to trans-boundary haze, carbon emissions, and global warming, reducing and controlling fires in the wetlands of Sumatra is of high priority. Fire management issues and options for the wetlands of southern Sumatra are discussed.

Trends, drivers of change and possible solutions to address deforestation and loss of forest habitat in the Kenya-Somalia cross-border area

This report first presents historic vegetation maps that localize the lowland tropical rainforests and the drylands forests that are the habitats of the biodiversity of the East African Coastal Forest Biodiversity Hotspot. Next, using information from Global Forest Watch (GFW), this study reports significant deforestation in the lowland tropical rainforests in southern and central Lamu County and adjacent Tana River County.

To segregate – or to integrate? The question of balance between production and biodiversity conservation in complex agroforestry systems

The paper uses Indonesian examples to define the agroforests that are used in the paper as a reference for integrated systems. Agroforest means the mature productive phase of complex agroforestry systems, specially systems that begin with slashing and burning the existing vegetation, planting various commercial and useful tree species, followed by successional phases in forest regeneration process. However in agroforests farmers do not systematically eliminate other species but allow the regeneration and preservation of numerous forest species, those that are perceived as having no detrimental impact on the system’s production.

Global change and multi-species agroecosystems: Concepts and issues

Complex (multi-species) agroecosystems change rapidly as a result of farmers’ decisions based on their perception of opportunities and constraints. Overall, the major trend is still one of reducing complexity. This review addresses the driving forces as well as consequences of this change and discusses the hypothesis that complex agricultural systems are more dependable in production and more sustainable in terms of resource conservation than simple ones. Farmer decisions regarding planned diversity on the farm have consequences not only for the harvested produce, but also for associated diversity and non-harvested components which may contribute to ecological sustainability. Functional attributes of plants which can lead to complementarity in resource capture include root architecture and phenology. Three hypotheses on biodiversity and ecosystem function are formulated (ranging from weak negative to strong positive interactions) and discussed. Evidence is not yet conclusive

The effects of forest conversion on annual crops and pastures: Estimates of carbon emissions and plant species loss in a Brazilian Amazon colony

The municipality of Theobroma in Rondonia, Brazil, covers 2165 km2, of which 43% was deforested by 1993. Between 1973 and 1993, the national government continued to improve highway BR364 connecting the area to Brazil’s south-central region and established a colony in Theobroma. During this period, 98% of the deforestation occurred. Some 1800 settler families continue to convert forest into pasture in a system based on the slash-and-burn agriculture and dual-purpose cattle production. Trends in carbon emissions and plant species losses during the 20-year history of Theobroma were analyzed by combining observed shifts in land-use types with estimates for the carbon stocks and plant species richness of each of these types. Carbon stocks declined from about 200 t ha1 in the forest to 28 t ha1 in the pasture and of 326 plant species encountered in the forest, only 20 remained in pastures (along with 66 species not found in forests). The effects of converting more than 93000 ha of forest into other uses over 20 years include approximate losses of 14 million tons of C to the atmosphere and substantial losses of plant species. Land use alternatives that would store more C include agroforestry and – given the strong incentives for settlers to convert lands into pasture –improving pasture management or developing silvopastoral systems. Plant species conservation may be improved with proposed ways to add private value to the forest.

Shortcuts for Biodiversity Conservation Planning: The Effectiveness of Surrogates

Biodiversity is not completely known anywhere, so conservation planning is always based on surrogates for which data are available and, hence, assumed effective for the conservation of unknown biodiversity. We review the literature on the effectiveness of surrogates for conservation planning based on complementary representation. We apply a standardized approach based on a Species Accumulation Index of surrogate effectiveness to compare results from 575 tests in 27 studies. Overall, we find positive, but relatively weak, surrogacy power. Cross-taxon surrogates are substantially more effective than surrogates based on environmental data. Within cross-taxon tests, surrogacy was higher for tests within the same realm (terrestrial, marine, freshwater). Surrogacy was higher when extrapolated (rather than field) data were used. Our results suggest that practical conservation planning based on data for well-known taxonomic groups can cautiously proceed under the assumption that it captures species in less well-known taxa, at least within the same realm.

Fungal Biodiversity Profiles 1-10

The authors describe ten new taxa for science using mostly both morphological and molecular data. In Ascomycota, descriptions are provided for Bambusistroma didymosporum gen. et spec. nov. (Pleosporales), Neodeightonia licuriensis sp. nov. (Botryosphaeriales) and Camposporium himalayanum sp. nov. (Fungi imperfecti). In Zygomycota, Gongronella guangdongensis sp. nov. (Mucorales) is described. Finally, in Basidiomycota descriptions are provided for Boidinia parva sp. nov. and Russula katarinae sp. nov. (Russsulales), Gloiocephala parvinelumbonifolia sp. nov. (Agaricales), Hypochnicium austrosinensis sp. nov. (Polyporales), Phallus ultraduplicatus sp. nov. (Phallales) and Suillus lariciphilus sp. nov. (Boletales).

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