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  • landscape view with reedbeds in the foreground and buildings on the horizon
  • A bittern standing in shallow water in from of reeds
  • A common frog
  • A water vole peeping out from between reed stalks

Reedbeds

A fen community dominated by reeds occurring in waterlogged areas, which are mostly freshwater, but can also be brackish or tidal.
 

Made up of reedbed, fen, eutrophic open water, ditches and wet woodland, they may also include small areas of wet grassland and carr woodland.

Most of the UK’s reedbeds are in East Anglia, with the three largest being on the Suffolk coast. They contain over fifty-six species of conservation concern.

Importance for wildlife

Reedbeds provide breeding habitats for rare and migratory birds and important wintering habitats. They make excellent habitats for otters, water voles, water shrews and harvest mice. Variations in reedbeds such as shallow areas, well-vegetated ditches, open areas of water and gentle bank gradients help to support a broad range of amphibians and reptiles. They are also an extremely important habitat for invertebrates with fifty-four notable invertebrates associated with Suffolk’s reedbeds.


Important associated species

Birds
Starling, Grasshopper Warbler, Savi's Warbler, Cuckoo, Reed Bunting, Bittern, Marsh Harrier, Cetti's Warbler, Reed Warbler, Sedge Warbler, Crane, Bearded Tit

Mammals
Harvest Mouse, Water Shrew*, Common Pipistrelle*

Flies
Broads Long-legged Fly, Black Fungus Gnat

Amphibians
Common Frog, Smooth Newt, Great Crested Newt, Common Toad, Grass Snake

Molluscs
Depressed River Mussel, Desmoulin's Whorl Snail, Swollen Spire Snail, Narrow-mouth Whorl Snail

Moths
White-mantled Wainscot, Fenn's Wainscot, Concolorous, Large Wainscot**

*Suffolk Priority species
**Priority - Research Only. Common and widespread, but rapidly declining

Notable Invertebrates

Species and Designation
Snails and slugs (Mollusca)
  • Vertigo moulinsiana, BAP Priority RDB3
  • Oxyloma sarsi, RDB1
  • Mercuria confusa, probably in Suffolk. Recorded under the older name ‘Pseudamnicola confusa’ at Barsham Marshes 2006, several sites in the 1980s and Carlton Marshes 1992, RDB2
Spiders and allies (Arachnida: Araneae and Pseudoscorpiones)
  • Clubiona juvenis, Redgrave & Lopham 2009-10, RDB2
  • Donacochara speciosa, Na
  • Entelecara omissa, Na
  • Gongylidiellum murcidum, Redgrave & Lopham 1984, Nb
  • Hypomma fulvum, Na
  • Marpissa radiata, Na
  • Tetragnatha striata, Nb
Woodlice (Isopoda)

Trichoniscoides albidus, Nb

True Bugs (Hemiptera)

Heteroptera

  • Microvelia pygmaea, Nb
  • Gerris lateralis, Local

Leafhoppers, planthoppers, froghoppers, treehoppers & cicadas (Auchenorrhyncha)

  • Chloriona dorsata (feeds exclusively on Phragmites), Nb
  • Oliarus leporinus (feeds exclusively on Phragmites), Nb
  • Paralimnus phragmitis (feeds exclusively on Phragmites), Nb
Flies (Diptera)

Snail-killing flies, picture-wing flies, grass flies and allies (Acalyptrata)

  • Lipara similis (Chloropidae), Redgrave & Lopham 2000, RDB2
  • Elachiptera austriaca (Chloropidae), N
  • Eribolus slesvicensis (Chloropidae), N
  • Lipara rufitarsis (Chloropidae), N
  • Anagnota bicolor (Anthomyzidae), N

Craneflies (Tipulidae)

  • Tipula marginella, RDB3
  • Dicranomyia complicata, RDB2
  • Erioptera bivittata, RDB2
  • Dicranomyia danica, RDB3
  • Thaumastoptera calceata, N
  • Molophilus pleuralis
Beetles (Coleoptera)

Ground beetles

  • Demetrias imperialis, Nb
  • Odacantha melanura, Nb

Leaf beetles (Chrysomelidae)

  • Donacia aquatica, BAP Priority Rare

Rove beetles and allies (Staphylinidae/Scydmaenidae/Silphidae)

  • Stenus butrintensis, Redgrave & Lopham 2009-10, N
  • Rugilus fragilis, Hopton Fen 2004, N
  • Dacrila fallax (characteristic of reedbeds, but also found elsewhere), N
  • Aloconota languida, Thelnetham 2004 (characteristic of reedbeds, but also found elsewhere), N
  • Stenus binotatus, Local
  • Stenus solutus, Local
  • Paederus riparius, Local
  • Erichsonius cinerascens, Local
  • Tachyporus pallidus, Local
  • Myllaena infuscata, Local
  • Myllaena intermedia, Local
  • Myllaena minuta, Local
  • Hygronoma dimidiata, Local
  • Alianta incana, Local
  • Pachnida nigella, Local
  • Ocyusa picina, Local
Caddis flies (Trichoptera)
  • Phacopteryx brevipennis 1 undated record from Redgrave & Lopham, N
  • Agrypnia pagetana, Local
  • Limnephilus binotatus, Local & Regionally Notable
  • Trichostegia minor, Regionally Notable
Ants, bees and wasps (Hymenoptera: Aculeata)
  • Odynerus simillimus, RDB1
  • Passaloecus clypealis, RDB2, RDB3, Rare
  • Hylaeus pectoralis, Rare
  • Macropis europaea, RDB3, Na, Scarce
Definitions of Designations
RDB3 – Red Data Book category 3

RARE: Species which occur in small populations and, although not currently either Endangered or Vulnerable, are at risk. Rare species exist in 15 or fewer 10km squares, or are more widespread than this but dependent on small areas of especially vulnerable habitat.

RDB2 - Red Data Book Category 2

VULNERABLE: A taxon is Vulnerable when it is not Critically Endangered or Endangered but is facing a high risk of extinction in the wild in the medium-term future. Rare species exist in 15 or fewer 10km squares, or are more widespread than this but dependent on small areas of especially vulnerable habitat.

Nb – Nationally Scarce Category B

Species which do not fall within Red Data Book categories but which are nonetheless uncommon in Great Britain and thought to occur in between 31 and 100 10km squares of the National Grid, or for less well recorded groups, between eight and twenty vice-counties.

Na – Nationally Scarce Category A

Species which do not fall within Red Data Book categories but which are nonetheless uncommon in Great Britain and thought to occur in 30 or fewer (typically between 16 and 30) 10km squares of the National Grid, or for less well recorded groups, in seven or fewer vice-counties.

RDBK

Species appear in the Red Data Book but the status is unknown, although they are thought to be rare.

Local

Found in restricted habitats.

Notable A

Taxa which do not fall within RDB categories but which are none-the-less uncommon in Great Britain and thought to occur in 30 or fewer 10km squares of the National Grid or, for less well-recorded groups, within seven or fewer vice-counties. The same as ‘Nationally Scarce’.

Notable B

Taxa which do not fall within RDB categories but which are none-the-less uncommon in Great Britain and thought to occur in between 31 and 100 10km squares of the National Grid or, for less-well recorded groups between eight and twenty vice-counties. Superseded by Nationally Scarce, and therefore no longer in use.

N – Nationally Scarce

Species which do not fall within Red Data Book categories but which are nonetheless uncommon in Great Britain. This status category has been used where information has not been sufficient to allocate a species to either Na or Nb. These species are thought to occur in between 16 and 100 10km squares of the National Grid.

BAP Priority Species

Listed under Sec 41 of the Natural Environment and Rural Communities Act 2006 as priorities for conservation action.


Factors affecting habitat in Suffolk

  • Coastal erosion and saline incursion have already led to a substantial reduction in the size and quality of the reedbed. Shingle banks protecting them are being eroded or overtopped by the sea. These reedbeds are expected to be lost as inundation by seawater increases in frequency.
  • Conversion to intensive agriculture, water abstraction and land drainage.
  • Inappropriate management leading to dehydration, scrub encroachment and loss of open water. Wetter parts of reedbeds are quickly lost if not managed resulting in woodland forming.
  • Inappropriate water level management, impacts from water abstraction and fluvial flooding threaten key species through direct losses (desiccation and drowning) or by impairing management.

Habitat management advice

  • Maintain water levels at a sufficiently high level and ensure that areas of litter do not dry out. Ensure continuity of level as rising water levels can be damaging for many invertebrates.
  • Maintain all stages of succession from young reed in shallow water to old reed and invasion of scrub on virtually dry ground over dense litter.
  • Maintain existing stands of Phragmites, tussocky grasses, sallow carr and sedges to ensure habitat diversity.
  • Retain scrub in small areas to increase habitat diversity. Remove any unwanted scrub by pulling out bushes, leaving small pools of water.
  • Consider grazing to maintain floral and invertebrate diversity. Trampling and poaching can create valuable patches of bare soil and create high-quality berms at ditch margins
  • Encourage flower-rich areas at the reedbed margins to provide pollen and nectar sources for adult insects.
  • Create a gently sloping profile at the fen edge to allow for seasonal water level variations.
  • Non-commercial cutting of reeds should take place on a 4 year+ rotation to allow time for invertebrates to reproduce successfully.
  • On a commercially cut reedbed, only part of the site should be managed intensively, leaving other areas available as longer-term invertebrate habitat. Only a small amount of the reedbed should be burned at any one time.

Vision for Suffolk

  1. Improve knowledge of extent and quality of reedbeds.
  2. Maintain the existing extent of reedbeds to ensure no net loss.
  3. Re-create reedbeds as opportunities arise.
  4. Encourage the restoration and improvement of degraded reedbeds.

Where to find further information

* all the links marked (pdf) have been gathered into an Issuu stack


Images: 

  • North Warren, Thorpeness by Emma Aldous
  • Bittern by John Evans (Flickr)
  • Common Frog by Paul Kitchener (Flickr)
  • Water Vole by Margaret Holland (Flickr)