Nicola Arndt und Matthias Pohl - Neobiota
Nicola Arndt und Matthias Pohl - Neobiota Nicola Arndt und Matthias Pohl - Neobiota
1 Background 1.1 Increasing interest in landscape assessment tools Over the last five years, European landscapes have received increasing attention from policy makers and researchers at both the national and international level. Growing demand for landscape expertise can be recognised on the side of political institutions such as the European Commission, the Council of Europe, the Organisation for Economic Co-operation and Development (OECD) and UNESCO as well as on the side of NGOs. These interests appear to reflect a newly and more widely experienced awareness regarding landscape functions and values as essential components of both human welfare and ecology. Rooted in culture, tradition, aesthetics, identification and in the environment, landscape concepts offer new tools for sustainable land management through the integration of sectoral activities and through participatory processes involving a wide range of stakeholders. The launch of the European Landscape Convention (Council of Europe), the development of various national landscape assessment programmes and the emerging role of indicator-based monitoring and reporting in support of – e.g. agri-environmental – policies have underlined the need for a scientifically reliable foundation of the landscape concept. One of the pressing needs in the field of landscape ecological tools at the European level is the development of a scientifically sound landscape classification and its cartographic representation in a format that meets the interests of both the research community as well as the decision-makers at the national and international level. When taking a closer look at other, similar attempts of international cooperation in the field of environmental mapping, it becomes evident that these efforts were facing a number of – partly severe – technical and procedural difficulties, such as conflicting schools of thinking, different socio-political perceptions, high demands on time and funds as well as inconsistent data-supplies. Examples are the development of the European Map of Natural Vegetation (1976 - 2003), the establishment of a habitat classification in the framework of CORINE (1989-1999) or the creation of a Digital Map of European Ecological Regions as part of the work programme of the European Environment Agency (1994-2000). One of the lessons learned from these relatively recent experiences is that key methodological principles need to be well researched and communicated in order to prepare a stable ground for launching targeted activities that require the commitment of many international experts and institutions. The development of a European classification for landscapes is – compared to works on species, habitats, vegetation and biogeographic regions – at a relatively early stage. Though almost a decade has passed since the development of a first policy-oriented map of European landscapes (MEEUS 1993) in contribution to the EEA’s Dobríš Assessment (STANNERS & BOURDEAU 1995), wider international cooperation in the field of landscape mapping has been rather limited. Two subsequent projects, namely the work undertaken for a Technical Report by the EEA (WASCHER & JONGMAN 2002) and the development of a ‘Physical Map of Europe’ did not only rely on centrally managed data sources (top-down approaches), they were also falling short of seeking European-wide recognition and of reaching the goal to address the cultural aspects of European landscapes – one of the essential challenges that have been identified in the policy world. 82
With the establishment of a network initiative under the name of Landscape Europe (PEDROLI et al. 2001), a new international approach towards institutional cooperation on the development of an agreed-upon European landscape classification and map is just beginning to take shape. A first international workshop had been organised by Landscape Europe in Wageningen (August 2001). One of the central questions of this workshop was indeed the identification of the principal data sources when building a European landscape classification and the role of natural vegetation data has been discussed. Before entering methodological considerations regarding the role of vegetation data, it deems necessary to define the meaning and policy dimension of landscape in its environmental and political dimension. 1.2 Definition of landscape European landscapes are based on natural features that are evolutionary and abiotic as well as on human intervention through agriculture, forestry and other cultural forces. The following definition has lately been proposed to be considered as a European-wide approach: “Landscapes are the concrete and characteristic products of the interaction between human societies and culture with the natural environment. As such, landscapes can be identified as spatial units where region-specific elements and processes reflect natural and cultural goods or history in a visible, spiritual and partly measurable way. Because the underlying human and natural processes are subject to change and evolution, landscapes are dynamic systems.” (WASCHER et al. 1998) This is also echoed by KLIJN & VOS (2000) who state that the ‘cultural landscape is the visible result of all agro-ecological and socio-economic forces operating at any given time, and is, therefore, constantly changing.’ In the European context it is possible to identify three broad categories of landscape that mark the extent and diversity of human intervention: 1. Relatively untouched areas that are situated in the most inhospitable regions, e.g. geographically remote areas such as mountain tops or areas of extreme climate and longitude, e.g. the Arctic tundra where permafrost and the short growing seasons inhibits the growth of most types of vegetation. 2. A decreasing proportion of traditionally managed land that have been transformed decades or centuries ago and have been maintained by traditional management practices (e.g. bocage in France or kampen in Flanders and Brabant) 3. Major parts of the landscape have been subject to a succession of different land uses and fairly intensive management practices. Climate, geo-morphology and both natural as well as anthropogenic vegetation dominates the coarse division of European landscapes as well as the major division in European biodiversity. 1.3 Policy objectives for mapping European landscapes In order to adequately manage and protect Europe’s landscapes, various efforts have been made to identify the relevant landscape characteristics at the regional, national and the international level. 83
- Seite 33 und 34: Over this distance matrix several m
- Seite 35 und 36: Figure 8 (Left): The Highlands beca
- Seite 37 und 38: - boundaries between ecological reg
- Seite 39 und 40: Anwendung und Auswertung der Karte
- Seite 41 und 42: SCHMIDT 2000, 2001). Die in diesem
- Seite 43 und 44: Diese „landschaftsökologische Ve
- Seite 45 und 46: Tabelle 2 entsprechende Qualitätsa
- Seite 47 und 48: Abb. 2: Analogie Kugelbeispiel / Ra
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- Seite 51 und 52: Abb. 5: Karte der landschaftsökolo
- Seite 53 und 54: Die Analyse der geostatistischen Re
- Seite 55 und 56: DINTER, W. (1999): Naturräumliche
- Seite 57 und 58: Application and Analysis of the Map
- Seite 59 und 60: 2 FAO Requirements Many environment
- Seite 61 und 62: In practical terms, delineation of
- Seite 63 und 64: 3.3 FAO Global Ecological Zone clas
- Seite 65 und 66: Table 2: LUT for Europe, showing th
- Seite 67 und 68: forests (F), 7 subgroups (F1- F7) h
- Seite 69 und 70: Figure 2: Map of Global Ecological
- Seite 71: Annex Table 4: Source maps used for
- Seite 74 und 75: DMEER-Projekt (Digitale Karte der
- Seite 76 und 77: Figure 1: The ecoregions are catego
- Seite 78 und 79: An example of the relationship betw
- Seite 80 und 81: DASMANN, R.F. (1973): A system for
- Seite 82 und 83: THACKWAY, R. & CRESSWELL, I.D. (eds
- Seite 86 und 87: While regional and national activit
- Seite 88 und 89: forest systems are supposed to reac
- Seite 90 und 91: According to SCHLÜTER (1991), hete
- Seite 92 und 93: derived from an analysis of soils a
- Seite 94 und 95: Map 1: Landscape Character Areas of
- Seite 96 und 97: in terms of successions and replace
- Seite 98 und 99: Map 5: Landscape map of Europe by M
- Seite 100 und 101: Russia. Information on rural land u
- Seite 102 und 103: 100 Map 7: European Landscape Typol
- Seite 104 und 105: G.3.1/37 F.1.1/7 & F 1 2/15 F.1.1/8
- Seite 106 und 107: Map 10: Comparison of the vegetatio
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- Seite 110 und 111: � Natural vegetation data will al
- Seite 112 und 113: LUC (1999): Glasgow and the Clyde V
- Seite 115 und 116: Application and Analysis of the Map
- Seite 117 und 118: characterized by zonal vegetation i
- Seite 119 und 120: Table 1: FAO Global Ecological Zoni
- Seite 121 und 122: The name of each type includes the
- Seite 123: References LAVRENKO E.M. (1964): Al
- Seite 126 und 127: 1 Introduction A dominant feature i
- Seite 128 und 129: 10° 65° 70° SBZ 75° MBZ 42 20°
- Seite 130 und 131: As shown in Table 2 there is a good
- Seite 132 und 133: What is interesting is that the tem
With the establishment of a network initiative <strong>und</strong>er the name of Landscape Europe (PEDROLI et al.<br />
2001), a new international approach towards institutional cooperation on the development of an<br />
agreed-upon European landscape classification and map is just beginning to take shape. A first<br />
international workshop had been organised by Landscape Europe in Wageningen (August 2001). One<br />
of the central questions of this workshop was indeed the identification of the principal data sources<br />
when building a European landscape classification and the role of natural vegetation data has been<br />
discussed. Before entering methodological considerations regarding the role of vegetation data, it<br />
deems necessary to define the meaning and policy dimension of landscape in its environmental and<br />
political dimension.<br />
1.2 Definition of landscape<br />
European landscapes are based on natural features that are evolutionary and abiotic as well as on<br />
human intervention through agriculture, forestry and other cultural forces. The following definition<br />
has lately been proposed to be considered as a European-wide approach:<br />
“Landscapes are the concrete and characteristic products of the interaction between<br />
human societies and culture with the natural environment. As such, landscapes can<br />
be identified as spatial units where region-specific elements and processes reflect<br />
natural and cultural goods or history in a visible, spiritual and partly measurable<br />
way. Because the <strong>und</strong>erlying human and natural processes are subject to change and<br />
evolution, landscapes are dynamic systems.” (WASCHER et al. 1998)<br />
This is also echoed by KLIJN & VOS (2000) who state that the ‘cultural landscape is the visible result<br />
of all agro-ecological and socio-economic forces operating at any given time, and is, therefore,<br />
constantly changing.’<br />
In the European context it is possible to identify three broad categories of landscape that mark the<br />
extent and diversity of human intervention:<br />
1. Relatively untouched areas that are situated in the most inhospitable regions, e.g. geographically<br />
remote areas such as mountain tops or areas of extreme climate and longitude, e.g. the Arctic<br />
t<strong>und</strong>ra where permafrost and the short growing seasons inhibits the growth of most types of<br />
vegetation.<br />
2. A decreasing proportion of traditionally managed land that have been transformed decades or<br />
centuries ago and have been maintained by traditional management practices (e.g. bocage in<br />
France or kampen in Flanders and Brabant)<br />
3. Major parts of the landscape have been subject to a succession of different land uses and fairly<br />
intensive management practices.<br />
Climate, geo-morphology and both natural as well as anthropogenic vegetation dominates the coarse<br />
division of European landscapes as well as the major division in European biodiversity.<br />
1.3 Policy objectives for mapping European landscapes<br />
In order to adequately manage and protect Europe’s landscapes, various efforts have been made to<br />
identify the relevant landscape characteristics at the regional, national and the international level.<br />
83