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  1. Trees as savings and security for the rural poor: World Development, Vol. 17, No. 3. (March 1989), pp. 329-342.Profes sionals have rarely seen trees as savings banks for poor people. But while trees and their products have become more valuable and easier to market, many poor people have become more vulnerable as contingencies cost more and traditional supports weaken. Consequently, trees have increasing importance and potential as savings and security for the poor, and for use to meet contingencies. For savings and security, trees compare quite well with jewelry, large stock, small stock, land, and bank deposits. Disadvantages of trees can include insecure or unclear rights, restrictions on cutting and selling when needed, and problems with marketing; but common advantages include cheap and easy establishment, rapid appreciation in value, divisibility to meet needs closely, and regeneration after cutting. More empirical studies are needed on the use and potential of trees as poor people's savings banks. The policy implications of present evidence and analysis include tree reform, improved marketing and prices, and above all investing poor people with secure and full ownership of trees, with rights to harvest, cut and sell similar to the withdrawal rights of depositors in savings banks.

    Source: World Development, Vol. 17, No. 3. (March 1989), pp. 329-342.

  2. High spatial resolution remote sensing of forest trees: Trends in Ecology & Evolution, Vol. 13, No. 8. (1 August 1998), pp. 300-301.

    Source: Trends in Ecology & Evolution, Vol. 13, No. 8. (1 August 1998), pp. 300-301.

  3. The integration of field survey and remote sensing for biodiversity assessment: a case study in the tropical forests and wetlands of Sango Bay, Uganda: Biological Conservation, Vol. 86, No. 3. (December 1998), pp. 379-391.Field surveys of plants and animals were combined with satellite remote sensing of broad vegetation types to map biodiversity and thereby help plan conservation in the Sango Bay area, some 30 by 100 km bordering Lake Victoria in Uganda. A statistical classifier applied to satellite images identified 14 land-cover classes including water, swamp, dry grasslands, degraded woody vegetation, semi-natural forest classes and intensive land uses. Validation, using 240 sample sites, recorded 86% correspondence between field and map data. Intensive land use makes up 23% of the area, water and swamps 27%, dry grasslands 29%, woody vegetation 21%, with semi-natural forests covering 15% of the area. The species data from sample-based field surveys included flowering plant species, dragon/lies, butterflies, fish, amphibians, reptiles, birds and mammals. The species data were used to generate biodiversity ratings, based on species ?richness' and ?rarity', which could be related to the vegetation cover. This inter-relation helped to generate a biodiversity map of the Sango Bay area which has since been used to aid conservation planning.

    Source: Biological Conservation, Vol. 86, No. 3. (December 1998), pp. 379-391.

  4. Estimation, by remote sensing, of deforestation in central Rondonia, Brazil: Forest Ecology and Management, Vol. 38, No. 3-4. (February 1991), pp. 291-304.Rondon ia, Brazil has been the focus of extensive immigration, colonization, and deforestation since the early 1970s. We have documented the land-clearing activities in Rondonia through the use of remotely sensed data from the Landsat and the NOAA AVHRR series of satellites, with the objectives of defining the rates and area of forest loss. We found that the total area cleared in the common area of the Landsat scenes increased 3160 km2 from 230 km2 of clearing in 1980 to a total of 3390 km2 of clearing in 1986, that the majority of new clearings were in the 10-100-and 100-1000-ha range. The largest individual forest clearings, however, which ranged up to 28 km2, had been established since 1980. We also found that the total road length in the region has increased from 110 km in 1973 to at least 4660 km in 1986. Although the majority of clearing was to pasture and not for roads, road building allows access to new areas and virtually guarantees future clearing by legal settlers or by squatters. We estimated that the total area of forest cleared in Rondonia by 14 July 1988 was between 37 200 and 37 900 km2 based on two classification s of NOAA9 AVHRR satellite data.

    Source: Forest Ecology and Management, Vol. 38, No. 3-4. (February 1991), pp. 291-304.

  5. Land cover change in two protected areas of Guinea-Bissau (1956-1998): Applied Geography, Vol. 22, No. 2. (April 2002), pp. 139-156.The objective of this work was to quantify and spatially characterize land cover change in the regions of the Cacheu and Orango protected areas (Guinea-Bissau ). Land cover maps from 1956 and 1998 were co-registered and rasterized to the same spatial resolution in a geographic information system (GIS) and the land cover classes of both maps aggregated to a new common legend. Classification of Landsat Thematic Mapper images and field checking were used to generate the 1998 map. Comparisons between the two dates indicate that major changes have occurred in the Cacheu area, both in the extent and the spatial distribution of some vegetation classes, with decreases in areas of mangrove, dry forest and palm grove, and large increases in mudflats and savanna. In Orango, changes are less extensive, but the onset of some of the trends verified in Cacheu can be identified. The results are interpreted, taking into account land use practices in the two study regions, and will hopefully become a management and conservation tool for the local park authorities.

    Source: Applied Geography, Vol. 22, No. 2. (April 2002), pp. 139-156.

If you would like to find additional social bookmark based links on the topic of Forests we recommend the Open Tag Directory > Forests. If you would like to find related tags we recommend Tag Patterns > Forests.



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