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Ref 1/S6 |
Species Action Plan 6 |
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Plan Author: |
RSPB |
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Plan Co-ordinator: |
RSPB |
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Plan Leader |
RSPB |
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31 December 1998 |
Final Draft |
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27 February 2008 |
Revised |
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Bittern Action Plan
New plan available soon. |
National Status
- Population increasing, but still localised and rare in the UK. The UK
population had declined to about 14 booming males in 1997 from a peak of 70
booming males in the late 1960s. However, work completed through two
separate EU LIFE projects has had a dramatic effect on population with 55
booming males recorded in 2004. Numbers are also boosted in winter by
continental immigrants.
- The bittern is listed on Annex I of the EC Birds Directive and Appendix
II of the Berne Convention. It is protected in the UK under Schedule 1 of
the WCA 1981. It is a Red List species, having declined by over 50% in the
last 25 years.
Norfolk Status
- The bittern breeds in north Norfolk and the Norfolk Broads. The bittern
also over-winters on other reedbeds in Norfolk, e.g., along the Wensum and
at Bowthorpe and Guist.
- The population in Norfolk increased from six males in 1995 to 19 in
2004, but has since suffered a marked drop. The number of breeding females,
however, has stayed constant at around seven or eight for the last ten
years.
- Table 1 presents the results of recent counts of booming males and nests
in Norfolk. These can be summarised as follows:
2004: Minimum of 19 and maximum of 26 booming males, with nine nests.
2005: Minimum of 11 and maximum of 11 booming males, with a minimum of seven
and a maximum of eight nests.
2006: Minimum of 13 and a maximum of 16 booming males, with six nests.
2007: Minimum of ten and a maximum of 16 booming males, with a minimum of
four and a maximum of five to six nests.
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Current factors causing loss or decline
The main factors limiting successful breeding of bittern within the Broads
and Norfolk coast are:
- Lack of sufficient food during the breeding season; and
- Inappropriate water level management and control within suitable
breeding sites.
Additional factors which are likely to be leading to loss or decline include:
- Loss of suitable breeding areas in fens and reedbeds through natural
succession and lack of appropriate management (particularly cutting and
water management);
- Degradation of habitat through eutrophication;
- Salt water intrusion into coastal reedbeds and threat of habitat loss
due to sea level rise and isostatic land movements;
- Vulnerability to severe winter weather.
Table 1: Summary of Norfolk counts of booming males and nests, 2004-2007.
| Site |
Year |
| |
2004 |
2005 |
2006 |
2007 |
| BROADS |
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| Upper Ant |
Up to 5 booming males; 5 of 6 nests failed. |
1 booming male; 2 nests. |
2 booming males; 2 nests. |
2 booming males; 1 nest failed. |
| Mid Ant |
1 strong and 1 weak booming male |
2 booming males; 1 nest. |
3 booming males. |
3 booming males. |
| Bure |
2 booming males. |
1 booming male; 1 nest. |
1 booming male. |
2 booming males; 1 successful nest. |
| Thurne |
8 booming males; at least 2 nests. |
3 booming males; 3 nests (2 successful). |
3 booming males; 2 nests. |
5+ booming males. |
| Yare |
1 booming male; 1 nest (failed). |
1 booming male. |
1 booming male. |
2 booming males; 1 nest not confirmed; 1 confirmed. |
| NORTH NORFOLK |
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| North Coast |
3 booming males; 2 successful nests. |
3 booming males; 1 nest. |
3 booming males. |
3 booming males; nests not confirmed. |
Source: RSPB
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Current Action in Norfolk
- All remaining bitterns breed on SSSIs, most of which are managed as
nature reserves. Specific annual management activities carried out include
cutting of reed and sedge, clearance of invading scrub and maintenance of
open ditches and pools. Management of water level control structures is key
to providing seasonally correct water levels.
- During 1995 and 1996, English Nature mechanically removed scrub from
26ha of the 30ha Hoveton marshes (outside but adjacent to Bure Broads &
Marshes SSSI), at a cost of £58,000 and with the help of BA volunteers. In
1997, approximately three kilometres of dykes were mud pumped to improve
water circulation and fish habitat. Since then, bittern have used the site
every winter, but there have been no records of breeding behaviour. However,
the site has been considerably improved as open fen with open water.
- Another project was carried out by English Nature and the Broads
Authority at Bure Marshes NNR in 1999, when 4.7 ha of old reedbed were
lowered by the BA digger. This created a revitalised reedbed with permanent
standing water (with improved connectivity to the River Bure), including 0.6
ha of open water. This has been used since by bitterns for wintering and
feeding during the summer, and was the final increase to the area of
suitable habitat within the middle Bure which is now used by breeding
bittern.
- More recently, management work has been carried out in Norfolk by EN,
RSPB, BA and NWT to benefit bittern as part of two nationally developed EU
LIFE projects. The key aims of the second LIFE project (which ended in 2006)
were to: increase the number of fledged young produced; provide fledglings
with suitable sites to move on to; and provide more suitable sites for
wintering bitterns both from home and abroad.
- Most work on the LIFE projects involved improving water level control,
restoring degraded reedbeds either by cutting or lowering the bed surface,
and creating suitable habitat for fish and other aquatic life that is
likewise accessible for bittern. Key sites included in the LIFE projects
were NWT reserves at Holme, Cley and Hickling, RSPB reserves at Titchwell
and Strumpshaw and BA’s Buttles marsh adjacent to How Hill.
- RSPB continues to carry out detailed ecological studies of bitterns
including annual mapping of booming males and active nest sites to inform
successful breeding.
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