Land use changes induced by nature conservation regulation and management practices, especially in protected areas, often result in trade-offs between ecosystem services (ESs). Exploring trade-offs between ESs and linking them with stakeholders can help reveal the potential losers and winners of land use changes. In this paper, we demonstrate that ES trade-offs do not always go hand in hand with conflicts. The perception of local stakeholders about trade-offs between ESs at three protected sites in the Great Hungarian Plain were assessed through qualitative methods. In all areas significant conservation measures had been introduced since the 1990s resulting in land use changes. Locals (farmers at each site and inhabitants at one site) were the main 'losers' of the land use changes and related ES trade-offs, while there were many winners at different spatial and temporal scales. Conflicts appeared only between locals and the national park directorates, and not between locals and other beneficiaries of the new ESs. Due to scale mismatch, locals might not be in direct contact with other stakeholders, and vice versa, and therefore there is no interface between them for confrontation and negotiation. Integrating scale into the analysis also helps in advising policy instruments to minimise local-level conflicts.
1Questions: (1) Which species dominate mid-successional old-fields in Hungary? How does 2 the identity of these species relate to local (patch-scale) diversity and to the progress of 3 succession? (2) Which species have the strongest negative impact on diversity in spontaneous 4 old-field succession and what generalizations are possible about the traits of these species? 5 (3) Are these species dominant or subordinate components in mature target communities? (4) 6 Do native or alien species have stronger effects on the diversity and progress of succession? 7Location: Abandoned agricultural fields (abandoned croplands, orchards and vineyards) at 8 various locations scattered throughout Hungary. 9Methods: Vegetation patterns on 112 old-fields, in 25 sites varying in soils and climatic 10 conditions, topography, landscape contexts and land use histories were sampled. Most old-11 fields had appropriate seed sources in the immediate vicinity, i.e. natural or semi-natural 12 grasslands (meadows steppes, closed and open sand steppes) as source and target habitats. 13The age of abandoned fields ranged from 1 to 69 years, but most sites were between 15 and 14 60 years. The cover of vascular plant species (in %) was estimated in 2 m x 2 m plots. 15Relationships between diversity, the progress of succession (similarity to target communities) 16 and the identity of dominants were tested. 17Results: A small portion of successional dominants (eight species) had strong negative 18 impacts on diversity. These species belonged to Poaceae, Asteraceae and Fabaceae families. 19Most of these species were wind pollinated, and capable of lateral vegetative spread. 20 Dominant species varied in size and had, on average, low requirements for nitrogen but a 21 high requirement for light. With one exception, Solidago gigantea, they were native to the 22
BackgroundPrevious studies showed an in-depth ecological understanding by traditional people of managing natural resources. We studied the landscape ethnoecological knowledge (LEEK) of Székelys on the basis of 16-19th century village laws. We analyzed the habitat types, ecosystem services and sustainable management types on which village laws had focused.MethodsSzékelys had self-governed communities formed mostly of “noble peasants”. Land-use was dominated by commons and regulated by village laws framed by the whole community. Seventy-two archival laws from 52 villages, resulting in 898 regulations, were analyzed using the DPSIR framework. Explicit and implicit information about the contemporary ecological knowledge of Székelys was extracted. We distinguished between responses that limited use and supported regeneration and those that protected produced/available ecosystem services and ensured their fair distribution.ResultsMost regulations referred to forests (674), arable lands (562), meadows (448) and pastures (134). Székelys regulated the proportion of arable land, pasture and forest areas consciously in order to maximize long-term exploitation of ecosystem services. The inner territory was protected against overuse by relocating certain uses to the outer territory. Competition for ecosystem services was demonstrated by conflicts of pressure-related (mostly personal) and response-related (mostly communal) driving forces. Felling of trees (oaks), grazing of forests, meadows and fallows, masting, use of wild apple/pear trees and fishing were strictly regulated. Cutting of leaf-fodder, grazing of green crops, burning of forest litter and the polluting of streams were prohibited. Marketing by villagers and inviting outsiders to use the ecosystem services were strictly regulated, and mostly prohibited. Székelys recognized at least 71 folk habitat types, understood ecological regeneration and degradation processes, the history of their landscape and the management possibilities of ecosystem services. Some aspects of LEEK were so well known within Székely communities that they were not made explicit in village laws, others remained implicit because they were not related to regulations.ConclusionsBased on explicit and implicit information, we argue that Székelys possessed detailed knowledge of the local ecological system. Moreover the world’s first known explicit mention of ecosystem services (“Benefits that are provided by Nature for free”) originated from this region from 1786.
Questions: Does succession of rewetted species‐poor fen grasslands display similar trends when different water levels, sites and regions are compared? Will restoration targets as peat growth and waterfowl diversity be reached? Location: Valley fen of the river Peene (NE‐Germany) and the Hanság fen (Lake Neusiedler See, NW‐Hungary). Methods: Analysis of permanent plot data and vegetation maps over a period of up to seven years of rewetting. The general relations between newly adjusted water levels and changes in dominance of helophytic key species during early succession are analysed considering four rewetting intensities (water level classes) and eight vegetation types (Phalaris arundinacea type, Carex type, Glyceria maxima type, Phragmites australis type, Typha type, aquatic vegetation type, open water type and miscellaneous type). Results: The initial period of balancing the site conditions and vegetation is characterised by specific vegetation types and related horizontal vegetation structures. Most vegetation types displayed similar trends within the same water level class when different sites and regions were compared. A significant spread of potentially peat forming vegetation with dominance of Carex spp. or Phragmites as desired goal of restoration was predominantly restricted to long‐term shallow inundated sites (water level median in winter: 0–30 cm above surface). Open water patches as bird habitats persisted mainly at permanent inundated sites (water level median in winter > 60 cm above surface). Conclusions: Site hydrology appeared as a main force of secondary succession. Thus the rewetting intensity and restoration targets have to be balanced adequately.
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