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| Redgrave and Lopham Fen |
Pevensey Levels |
South Wales |
UK conservation status |
Discovery of the UK populations
Dolomedes plantarius was not discovered in the UK until 1956 when eminent arachnologist Eric Duffey found it around at the margins of peat pools at Redgrave and Lopham Fen, at the source of the River Waveney on the Norfolk/Suffolk border (Duffey 1958). A second UK population was discovered, 180 km away, when Peter Kirby identified D. plantarius from grazing marsh ditches on the Pevensey Levels in East Sussex in 1988 (Kirby 1990). This population had been known to biologists for several years but it was assumed to be D. fimbriatus. It had been known to local people for much longer and, in the 1950s, was reported to be common in the areas in which it is most still abundant.
In 2003, a third UK population was discovered on a disused canal near Swansea, South Wales, by local naturalist Mike Clarke (CCW Press release). Immature Dolomedes found on near-by Crymlyn Bog were subsequently also identified as D. plantarius. Although Dolomedes fimbriatus was reported from this site by Jonathan Lees in the 1970s, the record was never verified.
The lack of any reliable historical record for this species in Britain makes it impossible either to assess the extent of its decline or to account for its present highly disjunct distribution. Its extreme rarity must result from the loss and degradation of wetlands in general, and of both lowland fens, and ditch systems in lowland grazing marsh, in particular.
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History
Four years after the discovery of D. plantarius, an artesian borehole was sunk close to the edge of the Fen. Removal of 3,500 tonnes of water a day from the underlying chalk over the following four decades, exacerbated by droughts in the 1970s, '80s and '90s, progressively dried out and degraded the fen. A hydrological regime controlled by rainfall patterns and inflow of eutrophic water from a catchment dominated by intensive pig farming, replaced the fen's formerly copious supply of base-rich, nutrient-poor artesian groundwater. This rose from marginal springs and seepage lines. Internationally rare plant assemblages were degraded or lost, together with many rare species of plants and invertebrates (Redgrave and Lopham Fen History).
Habitat
Raft spiders are restricted to areas of the fen dominated by Cladium mariscus (Great Fen Sedge). They occur around the margins of pools that were created both by traditional peat digging for fuel peat and, more recently, by mechanical excavation to increase the availability of water to the spiders in dry summers(Duffey 1977, Smith 2000).
D. plantarius is one of very few of the fen's national rarities to survive this period. It is almost certainly the depth of the fen's peat pools, enabling them to hold water even in dry summers, which enabled to spider to survive as the fen began to dry out.
Conservation
Despite the excavation of additional, deep pools to provide standing water for the spiders in the 1970s and 1980s, the droughts of the late 1980s left very little standing water on the fen and D. plantarius became confined to two, small, isolated areas representing a reduction of over of over 80% in its likely former range (Smith 2000).
In 1991 a Species Recovery Programme project was initiated by English Nature with the aim of preventing extinction of the residual population: significant expansion was not a realistic objective while the fen remained dry. Systematic monitoring and positive habitat management measures were established. The latter included re-instating cutting of C. mariscus on a traditional rotation, scrub removal, excavation of additional pools and deepening of existing ones and, most radically, the introduction of an irrigation supply, piped from the borehole to the core of the spider population (Smith 2000).
Population Trends
The borehole closed in July 1999, at the end of a 5-year EU-funded programme to restore the fen by a combination of extensive removal of scrub, stripping of oxidized surface peat and grazing. A run of wet seasons resulted in rapid hydrological recovery of the Fen. Despite this, and despite the very high potential fecundity of the spiders (Biology), neither of the residual populations have shown any evidence of recovery in population size or in range. Population trends over the sixteen years of systematic monitoring under the Species Programme show that there is significant variation between years and between two residual populations, but no evidence of any long-term trend or of recovery:
Annual population indices for the two residual sub-populations of D. plantariuson Redgrave and Lopham Fen NNR, in July 1991-2007. Data generated by a log-linear Poisson regression model plotted on a linear scale. 2SEs shown as postitive bars for the sub-population on Middle Fen and negative bars for that on Little Fen.
The Future
The reasons for the failure of the spider population to recover since 1999 are unclear. Factors that might underlie this include:
- A reduction in area of suitable habitat. Phragmites australis, which is avoided by the spiders, has colonised both the margins of the flooded scrapes created by peat stripping and invaded areas of Cladium mariscus. However, the areas of suitable habitat that remain have very low densities of spiders or remain uncolonised.
- Deep innundation of the core spider areas with stagnant water throughout the year as a result of impeded drainage following the restoration operation.
- Eutrophication of the water supply to the fen. The relative contributions from the surrounding arable catchment and from nutrient release from the degraded surface peat are not known.
- Genetic problems resulting from tight bottlenecks in the size of the spider population.
The problems of the Redgrave and Lopham Fen population are currently being addressed by the Species Recovery Programme through targeted autecological research, ongoing efforts to understand and improve control of the complex hydrology of the fen, and vegetation management designed to increase the area of internationally rare fenland associations. This includes the Cladium mariscus swamp favoured by the spiders. Studentships at the University of East Anglia are investigating both the genetics of the spiders and aspects of their autecology.
To download the 2006 summary report on the status of Dolomedes plantarius at Redgrave and Lopham Fen click here
(764 KB).
Earlier reports on the status of D. plantarius at Redgrave and Lopham Fen NNR are published as English Nature Research Reports and can be obtained from Natural England (Northminster House, Peterborough PE1 1UA, UK)
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Habitat
The Pevensey Levels comprise one of the largest continuous lowland wet grazing systems in south-east England. Although over 500ha have been converted to arable, 3500ha of low-lying grazing meadow remain, intersected by a complex network of ditches. The aquatic communities supported by the ditches include 68% of British aquatic plant species and many nationally rare invertebrates. The national and international importance of the area is reflected in its designation as an SSSI and RAMSAR site. Some of the best habitat (181.6 ha) is protected as a National Nature Reserve (NNR), 130.2 ha of which is managed by the Sussex Wildlife Trust (SWT).
Although the Pevensey habitat is very different from that at Redgrave and Lopham Fen they share characteristics common to western European D. plantarius sites. Both are lowland wetlands fed by neutral to alkaline, base-rich water: the structure of the vegetation is more important than its species composition (Smith 2000). The requirement for stiff-leaved, emergent vegetation to support the nursery webs (Biology), which is met primarily by Cladium mariscus at Redgrave and Lopham Fen, is met by a range of emergent marginal species, such as Carex pseudocyperus, as well as by the stiff leaves of the floating rosettes of Stratiotes aloides on the Pevensey Levels.
Conservation
Following the discovery of D. plantarius in 1988, English Nature commissioned a large-scale survey of its range and abundance in 1990 (Jones 1992). This survey, of ca 90km of ditches throughout the SSSI and in adjacent areas, revealed a very extensive population. In the areas of best habitat, primarily on gravity-drained marshes, densities were often very high: nursery web densities averaged one per 2m of bank. Away from this core area, however, the pump-drained marshes supported a much lower population density and the population appeared to be very fragmented. On the basis of nursery web counts, the total adult female population was estimated to be in the order of 3000 at a time when the Redgrave and Lopham Fen population was thought to have, at best, only tens of adult females.
Although the Pevensey population was much larger than that at Redgrave and Lopham Fen on 1990, it is widely considered that habitat quality on the Levels has declined during the last fifty years. Drainage schemes, implemented in the 1960s and 1970s substatially reduced water levels and some of the main channels have become eutrophic. Dramatic increase in the populations of alien water plants, including Azolla filiculoides, Crassula helmsii and, most recently, Hydrocotyle ranunculoides, pose a further threat to the rich species assemblages of the ditches.
Over the last decade, efforts by the Environment Agency, EN, the Sussex Wildlife Trust and local landowners, have resulted in measures to address these problems. These have resulted in major changes in water level and land management on the Levels. A Wildlife Enhancement Scheme (WES) on the SSSI now provides landowners with tiered financial incentives for environmentally sensitive practices, including water level and ditch management, reduced stocking rates and restrictions on agrochemical use. Improved water level management has been made possible by the modification of existing sluices and construction new ones.
The Future
To assess the response of D. plantarius to the changes in management on the Pevensey Levels, and to monitor changes in the extent and status of the population, EN are currently developing a long-term population monitoring programme for the area. The genetic and autecological studies at the University of East Anglia will also focus on the Pevensey population.
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In May 2003 D. plantarius was discovered along a short section of the bank of the disused Tennant Canal where it flows through Pant-y-Sais NNR, east of Swansea. In common with the English sites, this a lowland waterbody fed by neutral to alkaline, base-rich water. Open, stiff-leaved tussocks of Carex paniculata (tussock sedge) provide the main structure for nursery-web construction although webs were also found in Glyceria maxima. Survey work in 2003 suggested that the population may be confined to this small area: it was not found in what appeared to be very suitable fen vegetation in the immediately adjacent Pant-y-Sais Reserve. However, further survey work is required to verify the extent of this population and inform management decisions.
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In May 2003 D. plantarius was discovered along a short section of the bank of the disused Tennant Canal where it flows through Pant-y-Sais NNR, east of Swansea. In common with the English sites, this a lowland waterbody fed by neutral to alkaline, base-rich water. Open, stiff-leaved tussocks of Carex paniculata (tussock sedge) provide the main structure for nursery-web construction although webs were also found in Glyceria maxima. Survey work in 2003 suggested that the population may be confined to this small area: it was not found in what appeared to be very suitable fen vegetation in the immediately adjacent Pant-y-Sais Reserve. However, further survey work is required to verify the extent of this population and inform management decisions.
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As a result of its extreme vulnerability in the UK, D. plantarius is classified as Endangered (Merrett and Bratton, 1991), is fully protected under Schedule 5 of the Wildlife and Countryside Act 1981 and is the subject of a Species Action Plan (UK Biodiversity Steering Group, 1999). Click here to view the Action Plan and here to view the revisions that followed the 2005 BAP review.
PLEASE NOTE that a licence is required under the Wildlife and Countryside Act 1981 for any activity that is likely to cause disturbance to this species.
For information on licencing click here.
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HOMEPAGE
This site is maintained by Helen Smith
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