Home About us Contact | |||
Habitats Directive (habitat + directive)
Selected AbstractsInterplay of actors, scales, frameworks and regimes in the governance of biodiversityENVIRONMENTAL POLICY AND GOVERNANCE, Issue 3 2009Jouni Paavola Abstract This article examines the key contributions of the political science and systems theory based literatures on environmental governance, and uses them to analyse the governance of biodiversity in Europe. The article suggests that the key insights of the two bodies of literature are a distinction between governance frameworks and regimes on one hand, and the importance of multifaceted and multiple scales on the other. These key insights draw attention to horizontal and vertical forms of interplay. The article suggests that interplay, both between actors and levels and between frameworks and regimes, is ubiquitous and ambivalent: it can either foster or hinder environmental governance. The article illustrates this discussion in the context of governance of biodiversity in Europe, highlighting how vertical and horizontal interplay between the governance framework for biodiversity and the broader institutional setting or regime have characterized the implementation of the Habitats Directive, both complicating and fostering the governance of biodiversity in Europe. Copyright © 2009 John Wiley & Sons, Ltd and ERP Environment. [source] The Habitats Directive as an instrument to achieve sustainability?ENVIRONMENTAL POLICY AND GOVERNANCE, Issue 3 2006An analysis through the case of the Rotterdam Mainport Development Project Abstract The Habitats Directive is a key document for the protection of critical natural capital in the European Union. In a manner consistent with the understanding of sustainability in the European Commission, even critical natural capital is subject to trade-offs in favour of economic and social development. This is reflected in Articles 6(3) and 6(4) of the directive. This paper analyses the planning process leading to the approval of the expansion of the port of Rotterdam project , which will significantly affect Natura 2000 , against sustainability criteria. Although it shows that the directive is powerful to promote sustainable planning, the success of the case study was due mainly to elements specific to the particular planning process, namely the use of deliberative public participation mechanisms as well as specific assessment tools. Lessons are drawn and recommendations made to strengthen the Habitats Directive and the national planning processes in relation to projects potentially affecting Natura 2000 sites. Copyright © 2006 John Wiley & Sons, Ltd and ERP Environment. [source] ,Sustainable development' as a criterion for the interpretation of Article 6 of the Habitats DirectiveENVIRONMENTAL POLICY AND GOVERNANCE, Issue 2 2006Herwig Unnerstall Abstract Article 6(4) of the Habitats Directive requires a weighing up of environmental and economic interests in order to allow for deviation from valid environmental standards. This provision has to be interpreted in the light of the tasks and aims of the European treaties, especially in the light of sustainable development (SD). It is not only a political aim, but was also introduced in the European treaties in 1997 as both legally binding task and goal. This paper develops a comprehensive interpretative understanding of these provisions and their consequences for the application of European environmental law. SD is usually understood as being one aim amongst others and having three dimensions of SD (ecological, social and economic) of equal weight. This concept of equal weight contradicts the idea of a common but differentiated responsibility (CBDR), which is an essential part of SD. The CBDR requires that ,SD' has de facto different meanings in different member states according to their economic development. Therefore, Article 6 of the Habitats Directive may only be applied in those areas of the Community having a development lag. Copyright © 2006 John Wiley & Sons, Ltd and ERP Environment. [source] The implementation of international nature conservation agreements in Europe: the case of the NetherlandsENVIRONMENTAL POLICY AND GOVERNANCE, Issue 3 2001Graham Bennett Nature conservation policy in European countries is increasingly determined by the requirements of a wide range of international agreements. The most important are two EU directives (the Birds Directive and the Habitats Directive) and four conventions (the Ramsar Convention, the Bern Convention, the Bonn Convention and the UN Convention on Biological Diversity). The main foci of these instruments are habitats and species that are of international importance or require international cooperation to secure their effective conservation. Despite the importance of these habitats and species, implementation of the instruments has been uneven. The Netherlands provides a interesting example of implementation issues. The legislation necessary to enable the government to legally designate areas that have to be protected under the Birds Directive was only adopted in 1998, 17 years after the deadline fixed by the directive. This legislation has enabled the government to nominate areas for designation under the Birds and Habitats Directive. However, not all the sites that fall under the criteria of the Directives have been included in the list, and the legislation does not include the required provision concerning compensation for areas that are protected under the Habitats Directive and then damaged by activities that are authorized in the public interest. In the case of the Ramsar Convention, the government is planning to increase the number of designated sites, but the total number of sites will still represent inadequately the types of wetland of international importance that are found in the Netherlands. Despite this uneven implementation, the instruments , particularly the EU Directives , are having far-reaching effects on nature conservation in Europe. The most important consequences are that ecological considerations are the sole and absolute criteria for determining whether a site should be protected under the EU Directives and that many areas that until now only enjoyed limited protection under the spatial planning system now have to be legally protected from virtually all forms of damage. However, in practice many development plans take only limited account of the biodiversity conservation requirements implied by international conventions. Copyright © 2001 John Wiley & Sons, Ltd. and ERP Environment [source] Fish utilisation of managed realignmentsFISHERIES MANAGEMENT & ECOLOGY, Issue 6 2005S. COLCLOUGH Abstract, One area of ecological benefit not yet fully evaluated in European waters is the utilisation of restored saltmarsh habitats by fish species. This study examines the utilisation of managed realignments and relic saltmarsh by fish species. Factors affecting habitat heterogeneity and fish populations are discussed, and recommendations are made with respect to scheme design and management that will maximise the biological and socio-economic values. Fish populations in the high intertidal areas were assessed using a suite of techniques, including observations on feeding behaviour. Each microhabitat was discussed as a function of the extent of fish colonisation. A positive relationship between the degree of fish utilisation and habitat heterogeneity was ascertained using species richness, abundance and behavioural observations. This study will aid habitat valuation for economic justification of managed realignments, over and above existing drivers, such as compensatory habitat for encroachment, flood defence and the European Union Habitats Directive. The work now forms part of a wider European Interreg IIIb project, COMCOAST. [source] Conservation goals and fisheries management units for Atlantic salmon in the Baltic Sea areaJOURNAL OF FISH BIOLOGY, Issue 2001M-L. Koljonen The effective application of genetic information in fisheries management strategies implies political goal setting taking both conservation and fisheries management into account. The concept of sustainable use as set out by the Convention on Biological Diversity offers a valuable starting point in this respect, since the criterion for it is defined as the maintenance of genetic diversity within each species. However, strategic decisions are also needed on the practical level, where the actual genetic information can be taken into account. Genetic factors, such as glacial differentiation, the postglacial genetic structure of populations, gene flow levels and the probability of the existence of adaptive differences, have an effect on the formation of conservation and management units and on the long-term strategy for the sustainable use of aspecies. The Atlantic salmon (Salmo salar) in the Baltic Sea area is treated here as an example of a complicated management problem with a highly hierarchical genetic structure associated with marked loss of naturally reproductive stocks, extensive hatchery production and an effective international offshore fishery. The implications of genetic factors for the conservation and management strategy of the Baltic salmon is discussed in the light of the goals set by the Convention on Biological Diversity, the Straddling Fish Stocks and Highly Migratory Fish Stocks Agreement, the Habitats Directive of the European Union and the International Baltic Sea Fishery Commission. [source] A macroscale analysis of coastal steepening around the coast of England and WalesTHE GEOGRAPHICAL JOURNAL, Issue 3 2004J A Taylor Coastal steepening potentially presents an array of management issues in the form of financial implications of sea defence degradation, increased risk posed to the hinterland as wave attenuation is reduced, ,coastal squeeze' and statutory requirements in the light of the Habitats Directive. The extent to which coastal steepening has occurred throughout England and Wales has been investigated through use of a GIS and dataset based on historical Ordnance Survey map information. Data were collected along 1084 selected profile lines, positioned so as to be geomorphologically representative of the coast. Features recorded from each map year included the positions of mean high water (MHW) and mean low water (MLW), the relative movements of which infer changing intertidal gradients. The results presented in this paper are on a subject and scale not previously published. It is revealed that 61% of the coastline studied has experienced a tendency towards steepening. Of the remainder, 33% has flattened, and 6% has experienced no rotational movement. This tendency towards steepening has been the dominant movement on each of the west, south, and east coasts. [source] Benchmarking habitat quality: observations using River Habitat Survey on near-natural streams and rivers in northern and western EuropeAQUATIC CONSERVATION: MARINE AND FRESHWATER ECOSYSTEMS, Issue S1 2010Paul J. Raven Abstract 1.Some ecological effects of physically modifying rivers are still unclear, partly due to scale factors, but also because the character of high quality habitat is poorly understood. 2.Surveys at 278 sites on 141 near-natural streams and rivers in northern and western Europe were carried out between 1994 and 2009 to benchmark the habitat quality assessment system used for River Habitat Survey (RHS). 3.The objectives were to establish if RHS was suitable outside the UK, investigate if 500 m was still valid as the survey length, suggest a benchmarking strategy and recommend improvements to habitat quality assessment protocols. 4.Some modifications to RHS are needed to take account of differences in hydrological conditions, land-use and, most importantly, riparian habitat structure found in mainland Europe. 5.On average, 82,87% of channel attributes and 87,98% of channel and bank features were recorded within the first of consecutive RHS sites, confirming that 500 m is an effective sample length for characterizing small rivers. 6.Stream-flow character appeared to influence the distribution of several in-channel features, with greater diversity and between-site variation associated with rivers of mixed flow-types. To account for local variation and for effective use of survey time, it is recommended that two or more consecutive RHS sites are used for benchmarking purposes. 7.A suite of assessment protocols with agreed criteria and analytical rules, linked to specific objectives (e.g. nature conservation, geomorphic condition), is needed to establish the character and habitat quality of rivers in a consistent fashion. 8.A multi-discipline benchmarking programme using hydro-ecological regions in Europe would build on existing knowledge and help to improve both the inter-calibration and local application of quality assessment protocols. Data-sharing by hydrologists, river ecologists and fluvial geomorphologists would improve the basis for managing rivers in support of the European Water Framework Directive and Habitats Directive. Copyright © 2010 John Wiley & Sons, Ltd. [source] Developing standard approaches for recording and assessing river hydromorphology: the role of the European Committee for Standardization (CEN)AQUATIC CONSERVATION: MARINE AND FRESHWATER ECOSYSTEMS, Issue S1 2010Philip J. Boon Abstract 1. Over the last 20 years the concept of ,freshwater quality' has expanded to incorporate a range of physical, chemical, hydromorphological and biological characteristics. In Europe, this process has been given greater impetus by the EC Water Framework Directive (WFD) and the requirement for Member States to assess and monitor a comprehensive suite of freshwater features. 2. Assessments of river hydromorphology are needed not only for implementing the WFD but also for nature conservation purposes, such as monitoring the condition of Special Areas of Conservation under the EC Habitats Directive and helping in the management and restoration of rivers. At present there are few detailed methods available in Europe for assessing river hydromorphology, and standard approaches are urgently required. 3. The European Committee for Standardization (CEN) works to promote voluntary technical harmonization in Europe in conjunction with worldwide bodies and its European partners. The production of a CEN standard for assessing the hydromorphological features of rivers began in September 1999 and culminated in the production of EN 14614 in November 2004. 4. EN 14614 is a ,guidance standard' that provides a framework of general principles and sets out which aspects of river hydromorphology should be assessed, how to plan and conduct field surveys, how results should be interpreted and presented, and ways of applying quality assurance procedures. 5. A second CEN standard on river hydromorphology has recently been published. Using simple scoring systems, this will enable the extent of hydromorphological modification to river channels, banks, riparian zones and floodplains to be recorded and assessed consistently. 6. CEN standards encourage European collaboration and provide a framework which other countries can use to develop their own assessment methods. However, ways need to be found to streamline the process of standardization and to ensure that published standards influence the work of researchers, environmental regulators and policy makers. Copyright © 2010 John Wiley & Sons, Ltd. [source] Distinctiveness of macroinvertebrate communities in turloughs (temporary ponds) and their response to environmental variablesAQUATIC CONSERVATION: MARINE AND FRESHWATER ECOSYSTEMS, Issue 4 2009Gwendolin Porst Abstract 1.Turloughs are a prime example of a water body type that interfaces with both the European Habitats Directive (92/43/EEC) and Water Framework Directive (2000/60/EC) (WFD), highlighting the need for an integrated strategy to protect and manage surface waters and groundwaters. To date, research on turloughs, including their invertebrate communities is limited. 2.Eight turloughs were sampled for their macroinvertebrate communities and water chemistry in April 2007. Faunal samples were collected by means of a simple box sampler. 3.Replicate samples within each turlough clustered together, indicating that a single sample can provide a meaningful description of the turlough invertebrate community. Variation of invertebrate communities within turloughs was nested among turloughs. 4.Hydroperiod influenced mean abundance and taxon richness of macroinvertebrates, but no correlation was found between nutrient status and either mean abundance or taxon richness. 5.Turloughs are priority habitats under the EC Habitats Directive, requiring maintenance of ,favourable conservation status', which needs to be assessed through monitoring, and effected through appropriate management plans. While the distinctiveness of macroinvertebrate communities across turloughs is conducive to simple and cost-effective monitoring, this also challenges the applicability of the concept of type-specific communities across these highly dynamic ecosystems. Copyright © 2009 John Wiley & Sons Ltd. [source] Establishing survey and monitoring protocols for the assessment of conservation status of fish populations in river Special Areas of Conservation in the UKAQUATIC CONSERVATION: MARINE AND FRESHWATER ECOSYSTEMS, Issue 1 2009I.G. Cowx Abstract 1.Under the EC Habitats Directive (92/43/EEC), several rivers in the UK have been designated Special Areas of Conservation (SACs) because they support important populations of fish species. Several factors need to be considered when establishing survey protocols to assess the conservation status of fish species in these rivers. 2.It is important to understand the biology and habitat requirements of fish species and to design appropriate monitoring surveys that adequately assess the status of the fish populations. This information can, in turn, provide the basis for establishing sustainable conservation targets for specific stocks, a process known as condition assessment. 3.Favourable condition of fish species in SAC rivers is assessed using three criteria. The first relates to density of fish in various life stages against pre-set targets, assuming that an appropriate number of sites is surveyed to account for natural spatial and temporal variations in fish populations. The second is evaluation of the demographic structure to demonstrate continued recruitment success. Third, by mapping the distribution of the target species in individual rivers and where favourable condition is only achieved where there has been no reduction in the distribution range river between surveys. 4.The framework described was developed from limited survey data. As more monitoring and assessment data become available, the threshold criteria for favourable condition for each species should be improved, and uncertainty in the procedures reduced. Copyright © 2008 John Wiley & Sons, Ltd. [source] Vegetation communities of British lakes: a revised classification scheme for conservationAQUATIC CONSERVATION: MARINE AND FRESHWATER ECOSYSTEMS, Issue 2 2007Catherine Duigan Abstract 1.A revised classification scheme is described for standing waters in Britain, based on the TWINSPAN analysis of a dataset of aquatic plant records from 3447 lakes in England, Wales and Scotland, which is held by the Joint Nature Conservation Committee. 2.Separate ecological descriptions of 11 distinct lake groups (A,J) are presented with summary environmental data, macrophyte constancy tables and maps showing their distribution. These lake groups include small dystrophic waters dominated by Sphagnum spp.; large, acid, upland lakes supporting a diversity of plant species, including Juncus bulbosus, Littorella uniflora, Lobelia dortmanna and Myriophyllum alterniflorum; low-altitude, above-neutral lakes with a high diversity of plant species, characterized by the presence of Potamogeton spp., Chara spp. or water-lilies and other floating-leaved vegetation; and coastal, brackish lakes, with macroalgae. 3.The Plant Lake Ecotype Index (PLEX) is presented as an indicator of changing lake environments. PLEX scores reflecting the new classification scheme have been developed for individual plant species and lakes. Applications of the index are demonstrated. 4.There is discussion of possible applications of the data collected and the resultant classification, in the context of the Habitats Directive, the Water Framework Directive and other conservation requirements. © Crown copyright 2006. Reproduced with the permission of Her Majesty's Stationery Office. Published by John Wiley & Sons, Ltd. [source] Directionality of pre- and post-breeding migrations of a marbled newt population (Triturus marmoratus): implications for buffer zone managementAQUATIC CONSERVATION: MARINE AND FRESHWATER ECOSYSTEMS, Issue 3 2005P. Marty Abstract 1.The marbled newt, Triturus marmoratus, is a vulnerable urodele species (listed on Annex IV of the European Habitats Directive). However, biological information about their migration and the terrestrial habitats they use is relatively scarce. In order to investigate the influence of the surrounding habitats of a local pond on the directions of pre- and post-breeding migrations, adult newts were monitored over two successive years (from February 2000 to June 2001) at a permanent pond in south-western France using a drift fence and pitfall traps. 2.In both sexes the entry and exit directions were non-randomly distributed. Furthermore, males and females generally followed similar directions facing an oak forest and avoiding barren areas. However, the directions followed by postbreeding migrants leaving the pond differed from those they followed when coming to the pond. 3.The distribution of captures around the pond was related to environmental factors, and more precisely to vegetation within the immediate surroundings of the pond. 4.The environmental conditions occurring at the end of the spring postbreeding migration differed greatly from those occurring during the winter prebreeding migration. Thus, vegetation does not exert similar attraction during the two migration periods. 5.This raises the importance of microhabitat diversity in the vicinity of the breeding pond, which provides a wide range of suitable shelters in different migration periods. Conservation planning must take into account the ecological requirements of this endangered species in managing buffer zones around the breeding sites. Copyright © 2005 John Wiley & Sons, Ltd. [source] Lake habitat suitability for the rare European macrophyte Najas flexilis (Willd.) Rostk.AQUATIC CONSERVATION: MARINE AND FRESHWATER ECOSYSTEMS, Issue 3 2005& Schmidt Abstract 1.Najas flexilis (Willd.) Rostk. & Schmidt is a submerged annual macrophyte, rare in Europe, which is protected under the EC Habitats Directive. 2.N. flexilis grows in deep, often coloured or turbid water in mesotrophic lakes. Because of this habitat preference it is difficult to locate and assess the ecological state of populations of the species for conservation monitoring purposes. 3.A method is described based on plant community information that can be used to determine the baseline probability that conditions in a lake are suitable for supporting N. flexilis growth. This can be applied to conservation management decisions, such as whether a detailed underwater survey is justified for monitoring the integrity of existing populations of N. flexilis, or whether the lake may be a suitable site for introduction, or reintroduction, of populations of the plant. 4.Two methods of plant community description are compared: a quantitative micro-habitat scale approach and a whole-lake-scale qualitative approach. Plant community data collected using each method were grouped using TWINSPAN, and environmental descriptors of the sites comprising each plant community group were compared statistically. 5.Micro-habitat-scale community groups differed significantly only in the light extinction coefficient, indicating the zone within the lake in which N. flexilis occurred. 6.The whole-lake-scale community groups differed in a number of environmental variables indicative of eutrophication and acidification, two major environmental threats to N. flexilis survival. 7.This study suggests that a lake-scale qualitative plant community description would be a better indicator of site suitability for N. flexilis growth than a quantitative micro-habitat plant community description. This is because the whole-lake-scale approach could detect a difference in the environmental factors that affect N. flexilis growth, which the micro-habitat scale approach could not. Copyright © 2005 John Wiley & Sons, Ltd. [source] Using aerial photography for identification of marine and coastal habitats under the EU's Habitats DirectiveAQUATIC CONSERVATION: MARINE AND FRESHWATER ECOSYSTEMS, Issue 4 2003Jan Ekebom Abstract 1.Implementation of the E.U. Habitats Directive requires information on the distribution, abundance and area covered by the habitats listed in Annex I of the Directive. 2.In Finland, 21 of these habitats occur in marine and coastal areas. The demand for spatial information of these habitats is increasing, so rapid and relatively inexpensive mapping methods are needed. 3.This study examines the identification of 15 habitats using high altitude black and white aerial photographs. Our goal was to find out how well these habitats could be identified using these types of photographs. We used a test group of 34 persons who were given only brief instructions on how to identify the habitats prior to the test. Their results were compared to a set of field data from an archipelago area at the entrance of the Gulf of Finland, in August 1999 and autumn 2000. 4.The test group identified sandy beaches, lagoons, submerged sandbanks and cliffs with an accuracy of 82%, 71%, 66% and 65%, respectively. The main reasons for these high accuracy percentages were apparently the high contrast and/or easy delineation of the habitat from the surrounding areas. 5.Reefs, wooded dunes and submerged reefs were identified with an accuracy of 39%, 44% and 45%, respectively. The remaining habitats were less precisely identified, apparently due to their small size or poor contrast to the surrounding areas. 6.High altitude aerial photographs are shown to be a useful tool for identifying several of these habitats and can be used as a complement to field mapping methods, GIS methods and other remote sensing techniques. The use of high altitude photographs for monitoring change is discussed. Copyright © 2002 John Wiley & Sons, Ltd. [source] Acidification of sandy grasslands , consequences for plant diversityAPPLIED VEGETATION SCIENCE, Issue 3 2009Pål Axel Olsson Abstract Questions: (1) Does soil acidification in calcareous sandy grasslands lead to loss of plant diversity? (2) What is the relationship between the soil content of lime and the plant availability of mineral nitrogen (N) and phosphorus (P) in sandy grasslands? Location: Sandy glaciofluvial deposits in south-eastern Sweden covered by xeric sand calcareous grasslands (EU habitat directive 6120). Methods: Soil and vegetation were investigated in most of the xeric sand calcareous grasslands in the Scania region (136 sample plots distributed over four or five major areas and about 25 different sites). Environmental variables were recorded at each plot, and soil samples were analysed for exchangeable P and N, as well as limestone content and pH. Data were analysed with regression analysis and canonical correspondence analysis. Results: Plant species richness was highest on weakly acid to slightly alkaline soil; a number of nationally red-listed species showed a similar pattern. Plant species diversity and number of red-listed species increased with slope. Where the topsoil had been acidified, limestone was rarely present above a depth of 30 cm. The presence of limestone restricts the availability of soil P, placing a major constraint on primary productivity in sandy soils. Conclusions: Acidification of sandy grasslands leads to reduced abundance of desirable species, although the overall effect is rather weak between pH 5 and pH 9. Slopes are important for high diversity in sandy grasslands. Calcareous soils cannot be restored through shallow ploughing, but deep perturbation could increase the limestone content of the topsoil and favour of target species. [source] |