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Landscapes Forest and Global Change - ESA - Escola Superior ...

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A. Ruskule et al. 2010. Patterns of afforestation process in ab<strong>and</strong>oned agriculture l<strong>and</strong> in Latvia<br />

98<br />

afforestation, its spatial character <strong>and</strong> species composition will depend on factors like soil (its<br />

chemical properties <strong>and</strong> humidity), terrain, initial herb layer, nearby forest, as well as former<br />

l<strong>and</strong> use (Prach et al. 2001a; Prach et al. 2001b; Barth et al 2003; Alard et al. 2005; Daugaviete<br />

2009; Kopecký <strong>and</strong> Vojta 2009; Rosenthal (in press)). Depending on interaction of these factors<br />

ecological succession might be either arrested or stimulated as well as leading to different<br />

succession patterns.<br />

Afforestation of ab<strong>and</strong>oned l<strong>and</strong>scape has significant effect on l<strong>and</strong>scape structure <strong>and</strong> its<br />

ecological functions (Reger et al. 2007; Stoate et al. 2009). Impacts on biodiversity might<br />

varying – at the initial stage of afforestation habitat diversity is increasing, while in long term<br />

perspective l<strong>and</strong>scape becomes more homogenous thus reducing also biological diversity<br />

(Fjellstad et al. 1999; Nikodemus et al. 2005; Sitzia 2010). Ab<strong>and</strong>onment of agricultural l<strong>and</strong> is<br />

reducing areas important for resting, feeding or breeding of migratory birds. However secondary<br />

succession process might be used also for restoration of natural habitats <strong>and</strong> increasing of<br />

abundance of related animal species (Prach et al. 2001a; Stoate et al. 2009).<br />

L<strong>and</strong> ab<strong>and</strong>onment also influence the scenic quality of l<strong>and</strong>scape <strong>and</strong> its identity which might<br />

psychologically deject inhabitants causing feelings like isolation, poverty, shame etc. (Bürgi<br />

2004; Palang et al. 2006; Benjamin 2007). Better underst<strong>and</strong>ing the role on environmental<br />

factors in the process of l<strong>and</strong>scape ecological succession would help to predict the course of its<br />

development <strong>and</strong> to make optimal choice for the future use of the ab<strong>and</strong>oned l<strong>and</strong>.<br />

2. Methodology<br />

The study analyses the spatial character of l<strong>and</strong>scape ecological succession <strong>and</strong> its influencing<br />

environmental factors at the local level within selected pilot areas. The study area comprise an<br />

ab<strong>and</strong>oned agriculture l<strong>and</strong> in Vidzeme, central part of Latvia, which represents typical rural<br />

l<strong>and</strong>scape including scarcely populated areas in the Gauja River valley bordering the strict<br />

reserve zone of the Gauja National Park, as well as more densely populated areas in vicinities of<br />

towns Sigulda, Līgatne <strong>and</strong> Taurene. The pilot areas of the study have been chosen by visual<br />

analysis of the latest available ortophoto images from 2007. The most distinct patterns of<br />

l<strong>and</strong>scape ecological succession within the study area were selected, covering different spatial<br />

character of shrub <strong>and</strong> tree patches <strong>and</strong> their species composition. As result 5 pilot areas have<br />

been chosen representing 4 patterns of l<strong>and</strong>scape ecological succession (see Table 1).<br />

During the field visits actual borders of woody patches have been mapped as well as density <strong>and</strong><br />

composition of woody species have been assessed at the sampling sites of 10x10m, by recording<br />

each tree <strong>and</strong> measuring their height. Sampling sites were selected within each patch, thus their<br />

number was dependent on size of pilot area <strong>and</strong> complexity of the secondary succession pattern<br />

(20 sampling sites in 1st pilot area; 24 - in 2nd pilot area; 26 - in 3rd pilot area; 14 - in 4th pilot<br />

area <strong>and</strong> 15 - in 5th pilot area).<br />

Environmental conditions <strong>and</strong> factors were described in the investigation areas. Altogether 13<br />

soil profiles were described during field works according to the international FAO WRB<br />

classificator (IUSS Working Group WRB, 2007), 57 soil samples were collected from soil<br />

profile diagnostic horizons <strong>and</strong> physical <strong>and</strong> chemical analyses were done in the laboratory<br />

according to the methodology of ICP <strong>Forest</strong> monitoring (Manual on methods…, 2006). Impacts<br />

of nearby forest st<strong>and</strong> <strong>and</strong> its species composition on the character of ecological succession have<br />

been defined by analysing the forest taxation maps obtained from the State <strong>Forest</strong> Service.<br />

Impacts of drainage systems have been analysed using the melioration maps of the former<br />

collective farms. Information on former l<strong>and</strong> use <strong>and</strong> period since agriculture practice has been<br />

given up were obtained from local inhabitants <strong>and</strong> l<strong>and</strong>owners by direct interviews at the pilot<br />

<strong>Forest</strong> <strong>L<strong>and</strong>scapes</strong> <strong>and</strong> <strong>Global</strong> <strong>Change</strong> -New Frontiers in Management, Conservation <strong>and</strong> Restoration. Proceedings of the IUFRO L<strong>and</strong>scape Ecology<br />

Working Group International Conference, September 21-27, 2010, Bragança, Portugal. J.C. Azevedo, M. Feliciano, J. Castro & M.A. Pinto (eds.)<br />

2010, Instituto Politécnico de Bragança, Bragança, Portugal.

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