Succession and Conservation management - Wicken Fen - case study The way in which conservation management on nature reserves such as Malham Tarn NNR has changed dramatically over time. Initially a lot of reserves were virtual no-go areas for people unless they had special permission to visit the place. Management was often based on the idea that we should just let nature get on with things and see what happened. Neither of these approaches was satisfactory. Can you suggest reasons why not? More recently conservation management became based on a rather better understanding of what would happen if things were left to themselves and this required a thorough understanding of the successional processes within the habitats that people were trying to conserve. Management then became focused on trying to halt succession at an appropriate stage to maximize the conservation value of the habitat being conserved. In many cases (Tarn Moss and Fen areas are good examples) allowing succession through to climax woodland would not be the best way of managing the conservation value of the sites. Recently the recognition of inevitable changes to our wildlife due to climate change has led to a re-appraisal of how we manage nature reserves. There is a feeling that we have to accept that the balance of species on those reserves will change – we may lose some species of concern but others will move in. To allow those changes to take place needs greater connectivity between reserves to allow the movement of species and perhaps also a return to a more naturalistic method of allowing natural processes to determine the outcomes of these changes. The Wicken Fen reserve in East Anglia provides a nice case study of how these thoughts are developing. Wicken Fen (on the outskirts of Cambridge) is a National trust property as is Malham Tarn and similarly has been designated as a: National Nature Reserve Site of Special Scientific Interest under the Wildlife and Countryside Act 1981. Special Area of Conservation under the EU Habitats Directive. Wetland protected under the international Ramsar Convention. The vision statement for the site envisages an extension and rewilding of a wider reserve area: Conservation Management at Wicken Fen The conservation management processes at Wicken Fen are varied, continue throughout the year and fall into two main categories. The first is intensive and arrests or halts the natural succession process at a desired point. The second is extensive. This process is much more flexible, does not prevent succession and in effect has no end point. Intensive Conservation Management This form of management is the one commonly used in conservation in the UK. In essence it follows the traditional methods of land management dating back to the early days of human cultivation. The basic principles are to cut or otherwise "harvest" the vegetation growth and remove that biomass from the area. Formerly, as early as the 15th Century, this process was undertaken at Wicken and the surrounding area in the form of Sedge Harvesting. At that time all the work was carried out by hand and required entire families to gather in the harvest produce. This remained the case until the early-20th Century when low key mechanisation became available. However, it wasn't until the 1960's-70's that this equipment became readily obtainable by conservationists. Latterly, in order to achieve the maximum amount of management in the given period Wicken has adopted a more mechanised process, albeit using the same basic principles as were used by the "harvesters" 600 years ago. Modern day management has several formats at Wicken Fen. Like our predecessors we continue the sedge harvest. This is still a labour intensive activity that is undertaken during the mid-summer period. Following on from the sedge the litter or marsh hay is cut. This is a more mechanised process whereby the vegetation is treated in the same way as hay. This process continues until the end of September when efforts are switched to the fringes of the many droves at Wicken Fen. Although the communities are different the vegetation is treated in much the same way as the litter in that it is cut and cleared using machines. There are of course many other aspects to the management of the Fen. Some are connected to the management of our water courses: brinking and slubbing. These are a means of halting the aquatic succession at an earlier stage than the terrestrial fen habitats, giving a greater diversity to the wildlife found at Wicken Fen Extensive Conservation Management Although this process is quite common in many countries around the world and has been used on large areas in the UK uplands, it is fairly unique to lowland Britain. Whilst 'intensive' management follows the basic principles of traditional 'agriculture', 'extensive' management attempts promote the same basic principle of natural/semi natural processes to drive landscape development. It is a far more hands off approach, requires patience and relies on topography and hydrology to drive landscapes development, whilst the grazing of large herbivores and natural regeneration/colonisation influences the vegetation (and thus the habitats). The exciting aspect of 'extensive' or "naturalistic" management is that the landscape is far more dynamic, being in a constant state of flux. As water levels fluctuate over time so the communities change. As grazing levels of large herbivores change, either through population changes or migration, so the influences on the vegetation change. These changes cause subtle differences in the landscape. The sort of scenario that could be expected is as follows; several seasons of dry weather will concentrate the herbivores in the areas where water can be found and grazing is lush. This concentration will reduce the growth of vegetation in these areas whilst at the same time significantly reducing grazing pressure in the dryer areas. Most aquatic or marginal plants will be suppressed in the wet areas with reed beds giving way to wet grassland. In the dryer areas where grazing is reduced, taller vegetation will ensue, eventually leading to woodland. As the weather follows its cyclical path and seasons become wetter, the reverse will happen. Water will be more readily available across a wider area thus reducing the pressure on the wetter areas. These will experience a prolonged period of water-logging and herbivores will range more widely. The wet grassland areas will once again give way to reed bed. The drier areas that had been abandoned by herbivores will once again be put under grazing pressure. This will break up the established tall vegetation and the area will become more open. Because the former type of management is based on traditional methods its results can be predicted fairly accurately. We therefore know how the habitats will develop. This certainty becomes less clear with the latter form of management. Extensive management is still in its infancy at Wicken Fen and because it is based on natural or semi-natural events, the direction of development can only be assumed. The effects are constantly being monitored and the results will help us and our successors ensure that the landscape and habitat development continues to produce the diversity for which the "ancient" fen has become renowned.
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