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The
Vegetation of Turlough Basins
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Turloughs are generally
surrounded by open limestone pavement, scrub woodland or pastureland.
| The extent of the
flood level is often marked by the presence of the black turlough moss
- Cinclidotus fontinaloides, which covers walls, rocks or
tree branches. |
|
|
Fontinalis antipyretica
is
a moss that is more tolerant of submergence and replaces the black turlough
moss further into the turlough basin. |
The vegetation within
the basin is usually comprised of a herbaceous sward. The vegetation
communities of turlough basins form identifiable zones which are largely
dependent on the following factors and also on a combination of all three:
-
Depth and duration of
inundation
-
Soil composition
-
Grazing intensity
The depth and duration
of flooding delimit plants that are intolerant of regular submergence.
In deeper zones the soil is bare following subsidence and is subsequently
colonised by ephemerals such as Rorippa islandica and Limosella
aquatica. In turloughs where the soil is freely draining the
vegetation is dominated by ruderals such as Plantago lanceolata and
Rumex
spp.
Where drainage is impeded by the clogging of swallow holes or by the deposition
of marl, peat build-up is encouraged and the vegetation is dominated by
sedges and rushes. Heavy grazing results in the removal of flood
tolerant scrub such as Salix spp. These influences result
in a mosaic of vegetation zones that are not necessarily at similar levels
in different basins.
Many plants that are
not aquatic in nature survive several months complete submergence e.g.
Lotus
corniculatus, Agrostis stolonifera and Ranunculus repens
although
in some species such as Potentilla anserina above ground parts
die-back during the inundated period.
A
List of Recognisable Vegetation Types (after Goodwillie,
1998)
The following list
of turlough plant communities is derived from probably the most comprehensive
survey of turlough vegetation to date. Increasing numbers relate
broadly to increasing depth of inundation. The sequence of letters
relate to community development on differing substrate or communities subjected
to differing grazing intensities as indicated in the text.
| 1A. Dry woodland:
Fraxinus
excelsior, Euonymus europaeus, Quercus rober, Glechoma hederacea, Festuca
gigantea, Moehringia trinervia. Not flooded in every year or
for only a few weeks. |
|
| 2A. Turlough
scrub: flooded woodland of Rhamnus cathartica, Prunus spinosa, Crataegus
monogyna, Virburnum opulus, Solanum dulcamara, Rubus caesius.
Litter of dead plant material enriches the soil. |
|
|
2B. Flooded
pavement: exposed rock often with Frangula alnus, Rhamnus cathartica,
Potentilla fruticosa, Sedum acre, Cladium mariscus and Schoenus
nigricans locally. |
| 2C. Limestone
grassland: Dryish sites with Festuca rubra, Achillea millefolium
, Galium verum, Prunella vulgaris, Filipendula vulgaris. |
|
| 2D. Lolium
grassland: Lolium perenne, Poa trivialis, Bellis perrenis, Leontodon
autumnalis, Cirsium arvense. Includes intensive fields of pasture and
sometimes much Rumex spp. |
|
| 2E. Damp
grassland: Grazed fields with low nutrient input. Phleum pratense,
Carex hirta, C. distcha, Festuca pratensis, Elytrigia repens, Rumex acetosa,
Cardamine pratensis. |
3A. Sedge
heath: Closely grazed nutrient-poor sites with good drainage and sometimes
some seepage. Danthonia decumbens, Molinia caerulea, Potentilla erecta,
Nardus stricta, Festuca arundinacea, Deschampsia cespitosa. |
| 3B. Carex
hostiana / Molinia: Nutrient-poor fen, often on skeletal limestone.
Carex
panicea, C. hostiana, C. flacca, Molinia caerulea, Succisa pratensis, Cirsium
dissectum. |
 |
3C. Tall
herb: Ungrazed, nutrient-rich sites. Carex disticha, C.hirta, Phalaris
arundinacea, Filipenda ulmaria, Lysimachia vulgaris, Rorippa palustris,
Polygonum hydropiper, Vicia cracca. |
| 4A. Potentilla
reptans / Viola canina: Species-rich, grazed community with Potentilla
reptans, Filipendula ulmaria, Galium boreale, Viola canina, Salix repens,
Lotus corniculatus, Ophioglossum vulgatum. |
| 4B. Potentilla
reptans / Carex nigra: species-poor, Potentilla reptans, P. anserina,
Mentha aquatica, Carex nigra, Ranunculus repens, Litorella iniflora, Viola
persicifolia. |
|
| 4C. Dry Carex
nigra: Carex nigra, Phalaris arundinacea, Pontentilla anserina,
Plantago lanceolata, Ranunculus repens, Rumex crispus. Relatively
firm in summer. |
4D. Wet Carex
nigra: peaty substrate, slow to dry out with Carex nigra, Eleocharis
palustris, Juncus articulatus, Caltha palustris, Senecio aquaticus. |
|
5A. Floodgrass:
long-lasting pools that eventually dry out. Glyceria fluitans, Eleocharis
palustris, Veronica catenata, Ranunculus trichophyllus, Rorippa amphibia,
Apium inundatum. |
| 5B. Polygonum
amphibium: Nutrient-rich sites with Polygonum amphibium, P. hydropiper,
Carex vesicaria, Lythrum salicaria, Alopecurus geniculatus. |
| 6A. Baldellia
/ Littorella: on marl or peat. Baldellia ranunculoides, Scorpidium
scorpioides, Potamogeton gramineus, Eleocharis multicaulis, Eleogiton fluitans,
Littorella uniflora. |
|
|
6B. Eleocharis
acicularis / Limosella: transitory vegetation on mud. Eleocharis
acicularis, Limosella aquatica, Lythrum portula, Rorippa islandica, Polygonum
minus, Chenopodium rubrum. |
7A. Peaty
Carex nigra: Carex nigra, Menyanthes trifoliata, Equisetum fluviatile,
Juncus articulatus, Lythrum salicaria.
Close to summer water
table. |
7B. Schoenus
/ Cirsium dissectum: fen peat layer with Schoenus nigricans, Cirsium
dissectum, Molinia caerulea, Achillea ptarmica, Parnassia palustris. |
| 8A. Oenanthe
aquatica / Hippuris: in ponds, springs and ditches within turloughs,
Apium
nodiflorum, Nasturtium officinale, Rorippa amphibia, Hippuris vulgaris,
Oenanthe aquatica, Sparganium spp., Nymphaea alba. |
|
|
8B. Potamogeton
/ Elodea: shallow semi-permanent water with Potamogeton crispus,
P. berchtoldii, P. pectinatus, Elodea canadensis, Myriophyllum spicatum,
Ceratophyllum demersum. |
| 8C. Schoenoplectus
/ Phragmites: In water, Schoenoplectus lacustris, Phragmites australis,
Equisetum fluviatile, Ranunculus lingua, Carex rostrata. |
|
8D. Magnocaricion:
ungrazed sites, damp in summer. Carex elata, C. rostrata, C. vesicaria,
some
Phalaris
arundinacea or Phragmites australis. Mesotrophic. |
| 8E. Cladium
mariscus: Species-poor stands of Cladium with scattered Phragmites
australis, Carex lasiocarpa, Potamogeton coloratus. Nutrient-poor. |
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