Are There Any Land Use Dynamics in the Upper Bistrița Basin, Eastern Carpathians, Romania, in the Period 1990–2021?

Author:

Jujea Valentin12ORCID,Stoilov-Linu Valeriu3,Boboc Mihaela3,Popa Ionel34ORCID,Nedelea Alexandru5ORCID,Crăciun Nicolae6,Negrea Bogdan-Mihai237ORCID

Affiliation:

1. Simion Mehedinți—Nature and Sustainable Development Doctoral School, University of Bucharest, Nicolae Bălcescu Blvd., 010041 Bucharest, Romania

2. Non-Governmental Research Organization Biologic, 14 Schitului Str., 032044 Bucharest, Romania

3. CE-MONT, Mountain Economy Centre of the “Costin C. Kirițescu”, National Institute of Economic Research—INCE, Romanian Academy, 49 Petreni Str., 725700 Vatra Dornei, Romania

4. National Research and Development Institute for Forestry “Marin Dracea”, Calea Bucovinei 73 bis Str., 725100 Câmpulung Moldovenesc, Romania

5. Department of Geomorphology, Pedology and Geomatics, Faculty of Geography, University of Bucharest, 1 Nicolae Bălcescu Blvd., 010041 Bucharest, Romania

6. Faculty of Biology, University of Bucharest, 91–95 Splaiul Independenței Str., 050095 Bucharest, Romania

7. Doctoral School of Applied Sciences (Biology), Ovidius University of Constanța, 58 Ion Vodă Str., 900525 Constanța, Romania

Abstract

This paper aims to assess land use and land use change (LULC). For this purpose, supervised mapping on satellite imagery, using the European Space Agency (ESA) SNAP programme from LANDSAT databases, publicly accessible through the European Copernicus portal, was used. At the same time, an analysis of the degree of landscape fragmentation in the study area was carried out, which revealed that, because of the particular fragmentation of small polygons, the best results were obtained via analysis/supervised mapping on satellite images. This method, once validated in the field, reflects the most accurate land use pattern in the analysed area, with wide applications in studies of agriculture, biodiversity, geography, etc. Between 2000 and 2010, significant changes were registered. Artificial surfaces decreased by approximately 400 ha, showing a negative trend in the last period of the interval. Coniferous forests reached their maximum threshold in 2000 (with 114,400 ha) in conjunction with the “Grassland” class, which exceeded 16,700 ha. In 2010, a drastic decrease in “Grassland” was recorded, reaching half of the values of 1990 and 2000, now having only 15,684 ha. Land cover changes were significant when comparing the period before 1989 with 2021. This fact was due to socio-economic changes in society, in large part caused by changes in professions and the way of life of the population.

Funder

European Social Fund

Publisher

MDPI AG

Subject

Nature and Landscape Conservation,Agricultural and Biological Sciences (miscellaneous),Ecological Modeling,Ecology

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