Fen Management Handbook - Scottish Natural Heritage
Fen Management Handbook - Scottish Natural Heritage
Fen Management Handbook - Scottish Natural Heritage
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establish. The use of nurse crops is fraught with problems as plants suited to initial<br />
establishment tend to persist as strong components of the vegetation. Examples<br />
are reed canary grass and reedmace which will colonise silty nutritious substrates,<br />
but continue to dominate for many years if nutrients are available. An alternative is<br />
to use non-wetland plants, but this requires ability to control water levels precisely,<br />
gradually flooding the area once stabilised.<br />
210<br />
On cut-over fen peatlands in Minnesota it was found that a cover crop<br />
made up of a mixture of oat (40%), winter wheat (40%) and annual<br />
ryegrass (20%) increased the rate of establishment of fen plants<br />
significantly on bare peat (Johnson & Valppu 2003).<br />
9.10.5 Weed competition<br />
Where previous land use was agricultural, short-term colonisation by weedy<br />
species may have to be accepted as a phase which the fen will go through. Given<br />
time, the excess nutrients will usually be mopped up by the vegetation and soil, and<br />
a more stable fen community will develop. On newly created fen sites where arable<br />
weeds threaten to outcompete desirable fen species, herbicide such as glyphosate<br />
may be required. Approval is needed prior to herbicide use in or near water.<br />
Disturbing the soil surface before seeding can stimulate the germination of arable<br />
weeds. This can significantly reduce the growth of competing species but there is<br />
no guarantee that the same species will not subsequently germinate later if the soil<br />
is disturbed.<br />
9.11 Post establishment management<br />
<strong>Management</strong> is not usually required in the first year after establishment, but<br />
thereafter most vegetation will require some management to avoid accumulation<br />
of dead leaf litter which will reduce opportunities for colonisation by smaller fen<br />
species. Plans should be put in place before the fen is created for the introduction<br />
of appropriate grazing and cutting regimes, for scrub control (see Section 6: <strong>Fen</strong><br />
Vegetation <strong>Management</strong>) and for control of water levels (see Section 7: <strong>Fen</strong> Water<br />
<strong>Management</strong>). Replacement of sown or planted target species may be necessary<br />
where there has been excessive loss due to intensive grazing by livestock, birds or<br />
other wild animals.<br />
9.12 References<br />
Amon, J.P., Jacobson, C.S. & Shelley, M.L. 2005. Construction of fens with and<br />
without hydric soils. Ecological Engineering 24, 341-357.<br />
Galatowitsch, S., Budelsky, R.& Yetka, L. 1999. Revegetation strategies for<br />
northern temperate glacial marshes and meadows. In: W. Streever (ed.) An<br />
International Perspective on Wetland Rehabilitation, pp. 225-241. Kluwer<br />
Academic Publishers.<br />
Garbisch, E.W. 2005. Hableton Island restoration: Environmental Concern’s first<br />
wetland creation project. Ecological Engineering 24, 289-307.<br />
Johnson, K.W. & Valppu, S.H. 2003. <strong>Fen</strong> restoration final project report. <strong>Natural</strong><br />
Resources Research Institute, University of Minnesota, Duluth.