Fen Management Handbook - Scottish Natural Heritage
Fen Management Handbook - Scottish Natural Heritage
Fen Management Handbook - Scottish Natural Heritage
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Appendix VI – <strong>Fen</strong> management for bryophytes<br />
In general, favourable management of fens should deliver favourable conditions for fen bryophytes,<br />
although there are obvious exceptions when succession has modified the bryophyte flora of a fen<br />
and management then impacts on the resulting flora. Ecological change and loss of management<br />
appear to be the main causes of the loss of populations of Red Data Book (Church et al, 2001)<br />
and UKBAP species from lowland mires in recent years, especially in East Anglia, although wholescale<br />
habitat destruction through drainage is thought to have caused the extinction of three rich-fen<br />
mosses including Paludella squarrosa in northern England in the late 19th century, and Meesia<br />
triquetra in Ireland as recently as the 1960s.<br />
Key environmental and management factors for mosses and liverworts<br />
Water chemistry<br />
Bryophytes are highly sensitive to changes in water chemistry. The majority of fen bryophytes require<br />
low macro-nutrient (i.e. N, P & K) levels and are intolerant of nutrient enrichment. They vary more in<br />
terms of base tolerance, from low base status (poor-fen) species, through neutral water specialists<br />
to obligate rich-fen species. It is critical that site managers understand the natural water chemistry of<br />
a site and ensure irrigation with nutrient-poor water of suitable base-status.<br />
Kooijman & Bakker (1995) carried out cultivation experiments that showed Sphagnum squarrosum<br />
responding to nutrient enrichment more than S. subnitens, and Scorpidium scorpioides being more<br />
tolerant of mineral-rich groundwater than the two sphagna. The common generalist Calliergonella<br />
cuspidata replaced the fen specialist S. scorpioides as nutrient levels rose, and the base-intolerant<br />
Sphagnum squarrosum replaced Calliergonella when inputs of groundwater declined. Such<br />
transitions can be observed in situ and may be rapid; sometimes resulting in substantial change in<br />
the character of fen features. For example, blocking ditches feeding mineral-rich water into a wetland<br />
can lead to the formation of poor-fen (van Wirdum, 1995). Complete competitive exclusions are<br />
probably rare (Malson & Rydin, 2009), at least among rich-fen bryophytes, but declines in abundance<br />
and vigour can lead to the loss of species to other environmental changes.<br />
Even traditionally managed fens can lose specialist bryophytes because of changes in surrounding<br />
land use or atmospheric N deposition (Bergamini et al., 2009): surveys in 1995 and 2006 of 36<br />
traditionally managed fens in Switzerland showed significant losses in fen specialist bryophytes and<br />
Red-list plants, and a significant increase in vascular plant biomass. N deposition is implicated in<br />
an increase in Sphagnum fallax on bogs (Limpens et al., 2003) and clearly has an impact on fens<br />
as well. Most of lowland Britain is above the critical threshold for N enrichment of fens (www.apis.<br />
ac.uk), making management even more challenging and emphasising the need for restriction of<br />
nutrient inputs within the entire catchment of a fen. Grazing or mowing may be needed to remove<br />
the competitive vascular plants that develop in response to enrichment. The effects of atmospheric<br />
enrichment are often exacerbated by water abstraction (see Case Study 10) and enrichment, as<br />
demonstrated by the loss of the UKBAP liverwort Leiocolea rutheana from four of its five sites in<br />
Norfolk and its decline at the fifth (Church et al., 2001; Swann, 1982).<br />
Hydrology<br />
Changes in hydrological regime can produce unsuitable conditions for key rich-fen mosses. Many<br />
experience fluctuating water levels and periodic inundation in the winter, but a rapid or sustained<br />
increase in water levels can lead to the loss of species such as Calliergon giganteum, which is<br />
replaced in deeper, more nutrient-rich water by C. cordifolium. Buoyant fen rafts may be more<br />
resilient than non-buoyant surfaces, but any rapid change in water levels should be avoided in<br />
favour of a gradual rise. Ditch blocking to raise water levels in one part of a fen may divert enriched<br />
or chemically unsuitable water on to another part and can have unforeseen consequences on the<br />
bryophyte flora.<br />
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