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• The Formation of Social and Economic Peripheries in Hungary after the Change of Regime

  179-187

  István Süli-Zakar

  Views:

  181

  The Hungarian industrial revolution started in the second half of the 19th century, which caused the revaluation of the geographical peripheries in Hungary. After the Trianon Treaty the rural areas of Hungary lost their foreign markets and became the "country of three million beggars". The socialist industrialization of the systems of Rákosi and Kádár absorbed the surplus of rural labour, but the industrialization meant the redistributive exploitation of the agricultural areas and the further impoverishment. After the political transition in 1989, the rural Hungary could not be the "pantry of the Council for Mutual Economic Assistance", and the final crisis of the Hungarian agricultural sales finalized the deformation of the three-quarters of Hungary, the major part of the rural areas in Hungary. In the recent decades the brain drain worked in the Hungarian peripheries, the disinvestment and the pauperization increased. The emerging of the new latifundia and the monoculture commodity production operate independently, separated from the Hungarian rural people in the sense of ownerships and production. As the result of these negative processes, significant part of the society in the peripheral areas declassed. In this hopeless situation awareness only a conscious regional policy and above all, a very well-considered education is only able to offer a chance for break.

• Agricultural sector, rural environment and biodiversity in the Central and Eastern European EU member states

  46-64

  Jaan Liira

  Tsipe Aavik

  Oliver Parrest

  Martin Zobel

  Views:

  50

  During the second half of the 20th century, agriculture and the rural environment diverged in Western and Central and Eastern European countries (CEEC). CEE countries itself are heterogeneous in the respect of land use intensity and history. In the current review we focus on the comparison of the agricultural sector and threats on biodiversities of EU new-member countries from Central and Eastern Europe and the old EU(15) member states. The clustering of countries revealed groups distinguished according to the level of their economic productivity, discriminating mostly among eastern and western European countries. CEE countries sub-divided according to geographic region, including also some old members of the EU. Within the western cluster, two large sub-clusters became evident according to economy affected by altitudinal and climatic differences. Partly because there are still areas where the intensity of land use remained low, the biological diversity in many regions of Central and Eastern Europe has remained high. However, loss of extensively used habitats, the restoration on intensive agriculture, reforestation with exotic species and urbanization are major threats to nature in CEE countries. The estimated variability among CEE countries is caused by different historical and cultural backgrounds of those countries. Due to the complexity and geographical diversity of driving forces, there remains much uncertainty in the possible impacts of particular factors on land use. This complexity and diversity have to be considered when planning economic as well as ecological means for developing the agricultural sector and conserving biodiversity in the future of CEE countries.

• Landuse/landcover change process in a tropical semi-arid zone: case of two rural communes (Chadakori and Saé-Saboua) in Maradi region, Republic of Niger

  1-12

  Doulay Kadiza

  Abdoulaye Diouf

  Abou-Soufianou Sadda

  Ibrahim Baba Yakubu

  Views:

  221

  The study aimed to analyze the process of Landuse/Landcover change of two rural communes (Saé Saboua and Chadakori) of Maradi region (Republic of Niger) over the past 28 years (1986 – 2014), through landscape structure analysis by diachronic cartographic approach and landscape indices. Mixed classification of temporal series of Landsat images led to identifying six Landuse/Landcover (LULC) classes, namely ”cultivated land under shrubs and trees”, ”cultivated land under trees”, “continuous cropland”, ”fallow/pasture land”, ”forest reserve”, and ”settlement”. The composition and structure of the studied landscapes have greatly changed from 1986 to 2014. The class ”cultivated land under trees” was the landscape matrix in 1986 with 38.65% of landscape total area but in 2001 and 2014 the class ”continuous cropland” became the landscape matrix. The changes also affected the ”forest reserve” which was transformed to smallholder agricultural land from 1986 to 2014. The area occupied by classes ”cultivated land under trees” changed from 38.65% in 1986 to 8.78% in 2014; and from 1986 to 2014, the area occupied by ”fallow/pasture land” has decreased of about 16%. The decrease in these classes was in favor of ¨continuous crop land¨, ¨settlement¨ and “cultivated land under shrubs and trees” which respectively gained 38%, 0.3% and 8.15% of their areas in 1986. The results of this study reflect the problem of access to land and even land saturation in semi-arid region, a consequence of strong population growth. They also contribute to a better rethinking of agricultural practices in order to initiate adaptation and resilience strategies for the population facing food insecurity and poverty.