|

In its
first full year of ownership of the Eversley Quarry Complex, CEMEX has
been delighted to support the continuing work of the Moor Green Lakes
Group.
The
publication of this, the Support Group’s 13th Annual
Report, is further evidence of the maturing condition of the Reserve
and of the commitment and enthusiasm of the Group’s ever-increasing
membership.
CEMEX UK Materials Ltd
CEMEX House
Coldharbour Lane
Thorpe, Egham
Surrey
TW2O 8RA
Tel. 01932 583600
August 2006 |
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CHAPTER 1
INTRODUCTION TO THE THIRTEENTH REPORT OF THE
MOOR
GREEN LAKES GROUP
Peter Scott
The various chapters of this report, prepared
by our wildlife recorders, indicate that the reserve is maintaining its
status as an attractive habitat. Naturally some species show declines, but
these are balanced by increases elsewhere. It is a cliché that ‘this is no
time for complacency’, but we can be reasonably pleased with the current
situation.
If this is to continue, it is essential that
we maintain (and possibly enhance) the mix of vegetation. The work parties
play an essential role here, so that only the heaviest jobs have to be
undertaken by outside contractors. In chapter 2, Sue Dent describes the work
done last year. Much was achieved, but there is always more that could be
done. The work programme can only become larger as we begin to tackle jobs
on the adjacent Manor Farm site as restoration proceeds there. The Sunday
work groups, though successful, were somewhat smaller last year than in the
previous couple of years, so more volunteers would be welcome. If you are
able to lend a hand, even if only occasionally, please contact Simon Weeks
so that he can keep you informed of forthcoming tasks.
Many members contribute records of their
wildlife sightings and the recorders give due credit in their reports.
Please keep it up! This information is vital to our assessment of the
effects of our work and to indicate where action may be needed.
Although CEMEX’s management systems still seem
to be a little unsettled, there has been no substantial change to its
commitment to the reserve. One important job that it undertook was
unblocking the outlet pipe in the south-west corner of Colebrook Lake North.
Although the new sluice installed earlier had been expected to solve our
problems in controlling water levels, it soon became a clear that a blockage
was making it ineffective. It turned out that tree roots had grown into the
pipe. These have now been cleared and a manhole installed to make future
maintenance easier.
As
Appendix G shows, there has been just one recent change in committee
membership. Brendan McCartney was unable to continue as membership secretary
and has been replaced by Keith Littler. I am very grateful to them both, and
to all other members, for their efforts.
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CHAPTER 2
SITE
MANAGEMENT REPORT APRIL 2005 TO MARCH 2006
Dr Sue Dent
Countryside & Access Officer
Blackwater Valley Countryside Partnership
General Site Management 2005
The Islands
Long Island has been one of
the management priorities for this year. For several years now it hasn’t
been possible to spend enough time on the island to keep up with the
intended management. As a result large areas have become dominated by dense
bramble which was threatening to swamp the whole island. There are also six
‘scrapes’ around the island, which have become very overgrown, in one case
virtually disappearing completely.
This year we have had the
new pontoon bridge to get to and from the island and this has made a great
difference. Not only is it much quicker to get people to and from the
island, allowing us to tackle the clearance of the scrapes, but we can get
small machinery across and this has allowed us to make real inroads into the
bramble and scrub.
As so much has changed
since the site Management Plan was written, we are carrying out a review of
the management of Long Island which can then be incorporated into the next
revision of the Reserve Management Plan. We plan to make the island a
priority for the next couple of years and hopefully we should be able to
make the most of this, potentially, very useful piece of habitat for the
reserve.
Tern, Plover and Sandpiper
Islands were cleared as usual this year. Clearing the islands is hard work
for the volunteers, but it is manageable and it does seem to create the type
of habitat that many breeding birds, such as the terns, require.
Plantation Viewing Slots
The cutting of viewing
slots along the southern edge of the reserve has continued this year,
continuing the pattern of rotation that has now been in place for three
years. Re-growth of trees that have been coppiced in the last couple of
years has been quite poor, almost certainly because of a combination of deer
and cattle grazing. If the ‘rotation’ is going to be successful it is
important that the trees are able to regenerate quickly and so mesh tree
guards have been put up around many of the trees cut this year, and some of
those still struggling from last year. Hopefully this will give them a
chance to keep ahead of the browsers.
Bramble and Scrub -
as usual
Over the rest of the
reserve the bramble remains a theme. The areas that were cut with a tractor
a couple of years ago have done well and an annual cut is keeping the
re-growth under control. The routine of clearing the lake edges also
continues and seems to be working well.
Cattle
Once again a small group of
cows grazed the site in the autumn. They were a different group this year
and, while they did roam around the boundaries, they didn’t manage to find
the escape routes that the previous group used on several occasions last
year.
'Alien’
species'
Crassula
remains around the site without perhaps getting rapidly worse. It was
noticeable how quickly it spread back across the scrape outside Colebrook
hide, which had been completely cleaned out in spring 2005. We hope to do
some spraying in the autumn to try and keep it in check and the volunteers
have been raking it out of scrapes, which works reasonably well so long as
it isn’t too dense and heavy.
This year for the first
time an attempt was made to tackle Himalayan Balsam, mainly along the
river edge to the south of the reserve. This was part of a wider ‘Pink Peril
Pull’ throughout the Blackwater Valley and we hope to repeat it again this
year.
Conservation Volunteers
As always the management of
the reserve is only possible because of the hard work and support of a
dedicated band of volunteers, both from the Moor Green Lake Group and the
Blackwater Valley Countryside Volunteers. Without their support and
enthusiasm it simply would not be possible to manage the reserve as we do.
The Moor Green
Lakes Group have been
out for 7 Sundays from September to March and this year the group took on
extra work cutting some of the viewing slots and did 4 mid-week tasks.
Overall they have done 87 days of practical work, with an average of 8
people out on the Sunday Tasks. Special thanks go to Peter Scott, Simon
Weeks and Tony Elston who have led the Moor Green Lakes Group tasks. This
has been backed up by the Blackwater Valley Tuesday group who have done 8
tasks and 137 days.
Which all comes to 224 days
of volunteer effort, or over £13 thousand pounds worth of work.
Aggregates Levy
Sustainability Fund grant, an update
It is now over a year since
the work funded by the ALSF grant was completed and it has had a real impact
on the site and its management.
-
The pontoon has been a
great success. It has been regularly used through the winter and is
providing just the improved access that we had hoped for.
-
The new stiles and gates
at the access points are working well and would seem to be keeping motor
bikes off the reserve. One was slightly damaged but was repaired and there
has been no (?) re-occurrence.
-
The new footpath surface
is settling in well.
-
The book on the
Butterflies of the Blackwater Valley, which was funded as part of the
grant, has been produced and is available to buy from BVCP.
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CHAPTER
3
REPORT ON
BIRDS 2005
Recorder: Ian Brown
During the year 132 species were recorded of
which 66 were present in suitable breeding habitat in the summer. One new
species was added to the site list, Whiskered Tern, bringing the total
number of species recorded to 205.
In the early winter period waterfowl numbers
were consistent with those of recent years for most species except Coot,
which were dramatically reduced. Cormorant numbers continued to increase
with a site record count of 98 in January. Up to four Little Egret visited
the site in early year, being firmly established as a regular visitor.
Goosander again used the site regularly for roosting, although daytime
numbers were slightly down. Other records included the now regular wintering
Pintail, occasional Golden Plover, Peregrine and finally, Buzzards were in
evidence in all months for the first time.
Spring arrived in late March with the earliest
ever Common Tern on 24th! Wader passage started mid month with Curlew, a
long staying Oystercatcher (the first of at least eight birds in year),
returning Little Ringed Plovers and Jack Snipe. A Ruddy Duck took up
residence on Grove, remaining for six weeks. During April there were
seemingly interesting sightings each day! The month started with a very
early Reed Warbler (2nd) several Whimbrel, two Mediterranean Gulls
(including a ringed bird, see Appendix B for details), Peregrine, five
Little Gulls in one group, a singing Grasshopper Warbler, and late in the
month two excellent records of Short Eared Owl (same bird?) after a 17 year
absence. Ringed Plover were frequently on the site at this time. May was to
get even better with the undoubted highlight of the year, a fine summer
plumaged Whiskered Tern, that whilst being elusive a times proved very
popular amongst birders, putting in several visits during a six day spell.
Other birds included two Arctic Terns, a Black Tern, more Whimbrel, another
Little Gull, Oystercatchers, Mediterranean Gull, Osprey and a long staying
Snipe in breeding habitat till early June.
It was a relatively poor year for breeding
waders with Little Ringed Plover and Lapwing rearing small numbers of young
together with Redshank falling due to predation. Tufted Duck, Mandarin and
Gadwall all fared much better. Black Headed Gulls continued to expand and
thrive whilst Common Tern numbers remained stable, with at least 25 young
reared. Egyptian Geese also continued to thrive after breeding for the first
time last year, rearing 8 young from two broods. Other species that had a
good breeding season, either on the reserve or nearby, were Little Owl,
Buzzard, Hobby, Kingfisher, Grey Wagtail and Skylark. On the debit side
Great Crested Grebe failed to rear any young and there were no spring
records of Lesser Whitethroat.
Mid summer started with some excellent records
in July (often a less productive month!), a pair of eclipse Garganey and a
remarkable group of 15 Black Tailed Godwits, with further records of two
singletons before the end of the month. A Wood Sandpiper was a short stayer
mid month whilst a long staying Oystercatcher ensured the best year ever for
the species. August’s highlight was a brief staying Arctic Tern whilst
September was brightened by an Osprey and Red Kite. October traditionally
produces some good birds and this year it was the third site record of Black
Necked Grebe. The newly installed Owl boxes were occupied by a Barn Owl
(till year end) and an influx of Bramblings began.
The year ended with a good build up of geese
involving several species, a site record count of 138 Teal, more Pintail, a
Ruddy Duck and a group of 13 Golden Plover with Lapwings.
Last but not least many thanks to the growing
band of observers who submit records especially including those who provide
observers names on the log sheet.
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CHAPTER 4
BOTANICAL SURVEY 2005
Recorder Dr Delphine
Hoyle
In addition to the annual
quantitative survey of wild flowers on the North and West sides of Colebrook
Lake North carried out on 25 May 2005 three further surveys were undertaken.
A survey of grasses (led by
June Chatfield) was conducted on 2 June using approximately the same 1 m
quadrats as for the wild flower survey. A survey of the recently coppiced
woodland next to Colebrook Cut was conducted on 16 August and of the Corner
Wood on 25 August. The results of the woodland surveys are given in Table C
together with the wild flowers found outside the sample squares
The meadow survey followed
the usual method. Ten random samples (1 x 1 m) were surveyed on 25 May 2005,
five on the North side and five on the West side of the Lake. (See map at
Appendix I).
In each of the sample
squares the species present were identified and quantified on the abundance
present
-
| 1. |
<4 % few
individuals |
6. |
26-33 % |
| 2. |
<4 %
several individuals |
7. |
34-50 % |
| 3. |
<4 % many
individuals |
8. |
51-75 % |
| 4. |
4-10% |
9. |
76-90% |
| 5. |
11-25% |
10. |
91-100% |
In addition the frequency of occurrence was
also recorded -
|
I |
1-20 % |
(1 in 5
samples) |
|
II |
21-40% |
(2 in 5
samples) |
|
III |
41-60% |
(3 in 5
samples) |
|
IV |
61-80% |
(4 in 5
samples) |
|
V |
81-100% |
(5 in 5
samples) |
The abundance and frequency
of the wild flowers found in the sample squares are given in Table A.
The survey was carried out
a little earlier this year before the grasses took over making it a. little
easier to identify the plants. Black knapweed, common mouse-ear, ox-eye
daisy, bird’s foot trefoil, ribwort plantain, lesser stitchwort and red and
white clover were all abundant. There was more perforate St John’s wort,
sheep’s sorrel and common vetch on the North side and ragged robin and
common sorrel on the West side
There was little evidence
of tree or shrub invasion on the squares.
Nineteen of the original
sown species were found in the squares and in the surrounding area.
Table A
|
LATIN NAME |
COMMON NAME |
COLEBROOK LAKE NORTH |
|
North |
West |
|
S |
Achillea millefolium |
Yarrow |
I
(1) |
0 |
|
|
Cardamine pratensis |
Cuckooflower |
0 |
I (1) |
|
S |
Centaurea nigra |
Black knapweed |
V (1-5) |
V (3-5) |
|
|
Cerastium fontanum |
Common mouse-ear |
IV (2-4) |
V (1-5) |
|
|
Cirsium |
Thistle |
I (1) |
I (1) |
|
S |
Daucus carota |
Wild carrot |
II
(2-4) |
III (1-4) |
|
S |
Galium verum |
Lady’s bedstraw |
III
(3-6) |
0 |
|
|
Geranium dissectum |
Cut-leaved cranesbill |
III
(2-4) |
II
(2-7) |
|
S |
Hypericum perforatum |
Perforate St.John’s
wort |
IV (1-2) |
I (1) |
|
S |
Hypochoeris radicata |
Common catsear |
I
(1) |
0 |
|
|
Lathyrus pratensis |
Meadow vetchling |
I
(3) |
0 |
|
S |
Leucanthemum vulgare |
Ox-eye daisy |
V (3-6) |
V
(1-8) |
|
S |
Lotus corniculatus |
Bird’s-foot trefoil |
III (1-8) |
IV (1-9) |
|
|
Lychnis flos-cuculi |
Ragged robin |
I (2) |
IV (2-7) |
|
S |
Medicago lupulina |
Black medick |
III (2-7) |
I
(3) |
|
|
Myosotis discolor |
Changing forget-me-not |
II
(1-2) |
I (2) |
|
S |
Plantago lanceolata |
Ribwort plantain |
V
(2-5) |
V
(1-8) |
|
S |
Prunella vulgaris |
Selfheal |
I (4) |
III
(1-3) |
|
S |
Ranunculus acris |
Meadow buttercup |
II (1-4) |
III
(1-4) |
|
|
Ranunculus repens |
Creeping buttercup |
I (1) |
IV
(1-5) |
|
S |
Rumex acetosa |
Common sorrel |
0 |
IV
(1-3) |
|
|
Rumex acetosella |
Sheep’s sorrel |
III (1-3) |
0 |
|
|
Rumex crispus |
Curled dock |
0 |
I (1) |
|
|
Seneciojacobaea |
Ragwort |
II
(1-2) |
II (1) |
|
|
Stellaria graminea |
Lesser stitchwort |
V
(1-4) |
V
(2-4) |
|
|
Taraxacum officinale |
Dandelion |
III
(1-3) |
II
(1) |
|
|
Trifolium pratense |
Red clover |
IV (1-8) |
V (2-8)
|
|
|
Trifolium repens |
White clover |
V (2-5) |
IV
(1-F) |
|
|
Veronica
serpyllifolia |
Thyme-leaved speedwell |
II (1-4) |
I (1) |
|
S |
Vicia sativa |
Common vetch |
IV
(1-4) |
0 |
|
S |
Vicia hirsuta |
Hairy tare |
I (1) |
I
(1) |
Note: S = Sown species
Table B
|
LATIN NAME |
COMMON NAME |
COLEBROOK LAKE NORTH |
|
North Side |
West Side |
|
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
|
Agrostis spp |
Bent grass |
|
|
|
|
|
|
A |
A |
A |
F |
|
Anisantha streilis |
Barren brome |
|
|
|
|
|
|
|
|
|
R |
|
Anthoxanthum odoratum |
Sweet vernal grass |
|
O |
|
C |
|
A |
|
R |
|
|
|
Bromus spp |
Brome |
|
O |
|
|
C |
|
|
|
A |
|
|
Bromus hordeaceus |
Soft brome |
C |
|
|
|
|
|
|
|
|
C |
|
Dactylus glomeratus |
Cock’s foot grass |
|
F |
|
|
|
|
|
|
|
|
|
Holcus lanatus |
Yorkshire fog |
|
O |
|
F |
C |
C |
F |
F |
O |
F |
|
Lolium perenne |
Perennial Rye-grass |
|
O |
|
R |
|
|
|
|
|
|
| Poa
trivialis |
Rough Meadow-grass |
F |
F |
|
F |
C |
C |
|
|
|
|
Key.
A - Abundant C -
Common F - Frequent
O - Occasional R - Rare
Table C
|
|
Plants recorded
at other locations. |
|
|
C1 - Outside
recorded squares |
|
|
C2 - Colebrook Cut
wood |
|
|
C3 - Corner wood |
| |
|
|
LATIN
NAME |
COMMON
NAME |
C1 |
C2 |
C3 |
|
Agrimonia eupatoria |
Agrimony |
X |
|
|
|
Anthriscus sylvestris |
Cow parsley |
X |
|
|
|
Arctium minus agg |
Lesser burdock |
X |
|
|
|
Artemisia vulgaris |
Mugwort |
|
X |
X |
|
Barbarea vulgaris |
Wintercress |
|
X |
|
|
Bellisperennis |
Daisy |
X |
|
|
|
|
Bidens cernua |
Nodding bur marigold |
|
|
X |
|
Centaurium spp. |
Knapweed |
|
X |
|
|
Ceratocapnos claviculata |
Climbing corydalis |
|
X |
|
|
|
Circium palustra |
Marsh thistle |
|
X |
|
|
Conyza canadensis |
Canadian fleabane |
|
X |
|
|
Crepis capillaris |
Smooth hawk’s beard |
|
|
X |
|
Daucus carota |
Wild carrot |
|
X |
X |
|
Digitalis purpurea |
Foxglove |
|
X |
|
|
Epilobium spp |
Willowherb |
X |
X |
X |
|
|
Filipendula ulmaria |
Meadow sweet |
X |
|
|
|
Galeopsis tetrahit |
Common hemp-nettle |
|
X |
X |
|
Galium aparine |
Cleavers |
X |
|
|
|
S |
Geranium pratense |
Meadow cranesbill |
X |
|
|
|
Geranium
robertianum |
Herb Robert |
|
X |
|
|
Heracleum sphondylium |
Hogweed |
|
|
X |
|
|
Hieracium pilosella |
Mouse-ear hawkweed |
X |
|
|
|
|
Impatiens capensis |
Orange balsam |
|
X |
X |
|
S |
Knautia arvensis |
Field scabious |
X |
|
|
|
Lapsana communis |
Nipplewort |
|
X |
X |
|
Linaria vulgaris |
Common toadflax |
|
X |
|
|
|
Lycopus europaeus |
Gjpsywort |
X |
|
|
|
Medicago lupulina |
Black medick |
|
X |
X |
|
Myosoton aguaticum
|
Water chickweed
|
|
X |
|
|
Oenanthe cracata |
Hemlock water dropwort |
X |
|
|
|
Persicaria maculosa |
Redshank |
|
X |
|
|
Plantago lanceolata |
Ribwort plantain |
|
X |
X |
|
Plantago major |
Greater plantain |
|
X |
X |
|
Primula veris |
Cowslip |
X |
|
|
|
|
Pulicaria dysenterica |
Common fleabane |
X |
|
|
|
Ranunculus spp |
Buttercup |
|
X |
|
|
Rubusfruticosus |
Bramble |
X |
X |
|
|
Rumexspp |
Dock |
X |
X |
|
|
Scrophularia auriculata |
Water figwort |
X |
|
|
|
S |
Silene alba |
White campion
|
X |
|
|
|
Sonchus spp |
Sowthistle |
|
X |
X |
|
Stachys officinalis |
Betony |
X |
|
|
|
Stellaria holostea |
Greater stitchwort |
X |
X |
|
|
Taraxacum officinale |
Dandelion |
|
|
X |
|
Torilis japonica |
Upright hedge parsley |
|
X |
X |
|
S |
Tragopogon
pratensis |
Goatsbeard |
X |
|
|
|
Tripleurospermum
inodorum |
Scentless mayweed |
|
X |
|
|
Ulex europaeus |
Gorse |
X |
|
|
|
Urtica dioica |
Nettle |
X |
X |
X |
|
Veronica spp
|
Speedwell
|
X |
|
|
|
Vicia tetrasperma |
Smooth tare |
X |
|
|
S
= Sown Species
Survey of Grasses
June Chatfield
The site was visited on 2
June 2005 by June Chatfield, Delphine Hoyle and Doreen Dye. The general
impression of the meadow area was of patchy vegetation, some lush and tall,
other areas with shorter and more sparse growth. There was some indication
of moisture contours with wetter zones around the lake and sedges. Rushes
and Ragged Robin were present in the damper areas. In many areas herbs,
especially clovers , dominated over grasses. Some grasses were in full
flower while others were just coming into ear. The frequency of these will
change with the season.
|
General Species List |
|
Latin Name |
Common Name |
Notes |
|
Agrostis |
Bent
grass |
Starting to come into ear |
|
Alopecurus geniculatus |
Marsh
Fox-tail |
In full
flower behind rush zone near lake edge. Grey-green and bent at nodes. |
|
Alopecurus pratensis |
Meadow
Fox-tail |
In tall
rank grass along footpath to hide. |
|
Anisantha (=Bromus) streilis |
Barren
brome |
In tall
rank grass along footpath to hide, a few plants in ear in quadrats. |
|
Anthoxanthum odoratum |
Sweet
vernal grass |
A short
early grass at end of flowering in limited area near entrance. |
|
Bromus |
Brome |
This
may be a stunted Soft Brome |
|
Bromus hordeaceus |
Soft brome |
Widespread but varying in height |
|
Carex |
Sedge |
Patches
on lower slopes with rush |
|
Dactylus glomeratus |
Cock’s
foot grass |
A few
young plants, flowering but not tussocks |
|
Holcus lanatus |
Yorkshire fog |
Widespread but only just coming into ear and leaves not extensive yet,
will expand. |
|
Juncus acutiformis/ articulatus |
Rush |
Mostly
in a belt by lake edge. Flowers needed to determine species (late
summer) |
|
Juncus effusus |
Soft
Rush |
Near
lake edge. Flowers just starting to bud. |
|
Lolium perenne |
Perennial Rye-grass |
A few
plants, just coming into ear. |
| Poa
trivialis |
Rough
Meadow-grass |
Mostly
near the entrance - in flower. |
The survey of grasses
included a general listing of the species together with a more quantitative
approach on the ten, 1 metre quadrats, marked out for the wild flower survey
the previous week, The results are given in Table B. The area surveyed was
the grass flanking two sides of Colebrook Lake North. Tall rank grass along
the footpath produced Meadow Fox-tail, Barren Brome, Soft Brome and
Yorkshire Fog, all common species and found in flower.
Dry grass on the slope near
the entrance to the lake included Bent grass (not yet in flower), Sweet
Vernal Grass, Soft Brome, Cock’s-foot, Yorkshire Fog, Perennial Rye-grass
and Rough Meadow-grass. Much of this was in sparse growth and some species
were present in small quantity. The damp areas near the water had Marsh
Fox-tail Grass and a rush with lateral bands of pith which is probably the
Sharp-flowered Rush mentioned in the Tenth Annual Report, but it was not
sufficiently mature to identify. The Soft Rush was also common along with
some sedges that were not identified to species level.
The grass is an interesting
mosaic of thick and thin vegetation with different species areas and this is
determined by the differences in soil moisture and nutrient content by the
path from dog-walking. The most interesting species was the Marsh Fox-tail,
a distinctive grey-green grass bent at the nodes. A further survey would be
useful later in the season to catch the Bent-grasses and sedges in flower
and the rush in fruit. The two most abundant species were Yorkshire Fog that
spreads vegetatively forming a mat and can easily exclude other plants and
Soft Brome.
Acknowledgements
Thanks are due to Irene
Draper, Doreen Dye, and Steve and Sheila Farmer for their help with the wild
flower survey; June Chatfield and Doreen Dye for the grasses survey; Irene
Draper and Peter Scott for the Colebrook Cut woodland survey and Peter Scott
for the Corner Wood survey.
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CHAPTER 5
REPORT
ON BUTTERFLIES FOR 2005
Recorder Sue Proudley
The first butterfly records
for 2005 were: one Brimstone on 17th March, plus 2 Small Tortoiseshell, 3
Comma and 3 Peacock recorded on 19th March.
Brimstones were slightly
down on 2003 peaking at 17 in May before tailing off. The Large White and
Small White numbers were lower than on the 2004 records but Green-veined
Whites remained about the same. 6 Orange-tips were recorded in April rising
to 45 in May.
Small Skipper records
improved with 20 seen in July. Only a few Essex and Large Skippers were
reported.
Speckled Wood butterflies
did well again this year with 50 recorded in July. July was also a good
month for the other summer browns, 300 Gatekeepers, 150 Meadow Browns and 60
Ringlets were recorded.
A single Green Hairstreak
was recorded in both April and May, 5 Purple Hairstreaks in July but
only one Small Copper was found in August. Holly Blue numbers were also
down. 6 Common Blue butterflies were seen in June but none in August.
Small Tortoiseshells were
seen in twos or threes from March until July and Peacocks did little better.
Red Admirals were recorded in low numbers most months until November. Commas
were also less abundant than in 2004.
Two Marbled Whites were
found at the end of June and there was another sighting in July.
One Painted Lady visited in
June and was not recorded again. There were no sightings of Clouded Yellows
or any other unusual visitors.
The last butterflies
recorded were one Speckled Wood and one Red Admiral on 1st November.
The list of
species observed on the reserve in 2005 is as follows:
|
Small Skipper
Essex Skipper
Large Skipper
Brimstone
Large White
Small White
Green-veined White
Orange Tip
Green Hairstreak |
Purple
Hairstreak
Small Copper
Common Blue
Holly Blue
Red Admiral
Painted Lady
Small Tortoiseshell
Peacock
Comma |
Marbled White
Speckled Wood
Gatekeeper
Meadow Brown
Ringlet
Marbled White
|
Number of species 24
I would like to thank all the people who have
taken the trouble to record their observations. Please keep up the good work
and remember to print your name at the bottom of record sheet so that I can
give you the credit.
The following observers contributed to the records in 2005:
|
K & P Crick
C Rose
K B Briggs
D Allott
Walshe
|
M Mitchell
K Carter
E Godden
N Clifford
C Proudley |
J E Warren
R & J W
I H B
BM & RM |
Sue Proudley may be contacted on tel: 01252
875536 or
By e-mail: c.proudley(at)btopenworld.com
|
Recorded numbers Mar -
Oct 2006 |
MAR |
APR |
MAY |
JUN |
JUL |
AUG |
SEPT |
OCT |
NOV |
|
Small Skipper |
(Thymelicus sylvestris) |
|
|
|
|
20 |
|
|
|
|
|
Essex Skipper |
(Thymelicus lineola) |
|
|
|
|
5 |
|
|
|
|
|
Large Skipper |
(Ochiodes venata) |
|
|
|
6 |
2 |
|
|
|
|
|
Clouded Yellow |
(Colias crocea) |
|
|
|
|
|
|
|
|
|
|
Brimstone |
(Gonepteryx rhamni) |
4 |
12 |
17 |
9 |
2 |
1 |
|
1 |
|
|
Large White |
(Pieris brassicae) |
|
|
1 |
1 |
20 |
12 |
3 |
1 |
|
|
Small White |
(Pieris rapae) |
|
5 |
2 |
1 |
6 |
4 |
3 |
|
|
|
Green-veined White |
(Pieris napi) |
|
4 |
16 |
1 |
4 |
4 |
1 |
|
|
|
Orange tip |
(Anthocharis
cardamines) |
|
6 |
45 |
|
|
|
|
|
|
|
Green Hairstreak |
(Callophrys rubi) |
|
1 |
1 |
|
|
|
|
|
|
|
Purple Hairstreak |
(Quercusia guercus) |
|
|
|
|
5 |
|
|
|
|
|
Small Copper |
(Lycaena phlaeas) |
|
|
|
|
|
|
1 |
|
|
|
Common Blue |
(Polyommatus Icarus) |
|
|
|
7 |
|
|
|
|
|
|
Holly Blue |
(Celastrina argiolus) |
|
|
2 |
|
1 |
|
|
|
|
|
Red Admiral |
(Vanessa atalanta) |
|
1 |
1 |
6 |
4 |
|
1 |
4 |
1 |
|
Painted Lady |
(Cynthia cardui) |
|
|
|
1 |
|
|
|
|
|
|
Small Tortoiseshell |
(Aglais urticae) |
2 |
2 |
2 |
3 |
2 |
|
|
|
|
|
Peacock |
(lnachis io) |
3 |
6 |
5 |
2 |
2 |
|
|
1 |
|
|
Comma |
(Polygonia c-album) |
3 |
4 |
1 |
5 |
12 |
1 |
1 |
1 |
|
|
Speckled Wood |
(Pararge aegeria) |
|
13 |
18 |
6 |
50 |
8 |
21 |
3 |
1 |
|
Gatekeeper |
(Pyonia tithonus) |
|
|
|
|
300 |
15 |
|
|
|
|
Meadow Brown |
(Maniola jurtina) |
|
|
|
55 |
150 |
6 |
|
|
|
|
Small Heath |
(Coenonympha pamphilus) |
|
|
|
|
1 |
|
|
|
|
|
Marbled White |
(Melanargia galathea) |
|
|
|
2 |
1 |
|
|
|
|
|
Ringlet |
(Aphantopus hyperantus) |
|
|
|
1 |
60 |
|
|
|
|
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CHAPTER
6
REPORT ON DRAGONFLIES AND DAMSELFLIES FOR 2005
Recorder Ken Crick
2005 marked a significant
change in the method employed for the collection of Odonata data on the Moor
Green Lakes site. The five transects used to-date were abandoned as they are
now so overgrown that the summer leaf-cover provides almost perpetual shade
over much of their length. The resulting data was considered to be no longer
representative of the site as a whole.
A day’s count now includes
Odonata observed from both hides, a visit to three short lengths of the
riverbank where leaf cover remains sparse, and a transect along the northern
shoreline of Colebrook Lake North. The cut, which drains water from Grove
Lake to Colebrook Lake South, was also included from June onwards.
The reserve was surveyed on
20 occasions between the 29th April and 9th October. Generally all
observations were recorded in full sun. Direct comparison with the previous
year’s dragonfly activity is difficult because of the changes referred to
above. Data collected for 2005 indicates the site continues to provide a
viable habitat for 10 species to live out a full life cycle, with 17 species
recorded on the wing.
Five members of the group
recorded their observations on the hide charts, confirming the presence of
many of the species observed during the site survey. In addition Mr. Brendan
McCartney photographed a Broad Bodied Chaser, the only recorded sighting of
this species on the reserve this year.
My thanks go to those
members providing information who were: -
J. Warren, S.
Proudley, R. Eagling, B. J. McCartney, I.H. Brown.
ODONATA CHECKLIST
DAMSELFLIES
Zygoptera
|
Species |
Date of maximum count |
Max count |
Life cycle confirmation Exuvia |
Observed flight period |
|
Large Red
Pyrrhosorna nymphala |
22nd June |
22 |
Yes |
28th April to
22nd June |
|
Azure
Coenagrion puellao |
22nd June |
251 |
Yes |
27th May to
5th July |
|
Common Blue
Enallagama cyathigerum |
15th July |
504 |
Yes |
27th May to
9th October |
|
Banded Demoiselle
Caloperyx splendens |
15th July |
105 |
Yes |
3rd May to
13th Sept. |
|
Blue-tailed
Ischnura elegans |
5th July |
38 |
No * |
27th May to
26th August |
|
Red-eyed
Eiythromma najas |
11th Aug. |
39 |
Yes |
27th May to
26th August |
*There
is little doubt that this species is breeding at Moor Green; I just failed
to pick up any exuviae this year
DRAGONFLIES
Anisoptera
|
Species |
Date of maximum count |
Max count |
Life cycle confirmation Exuvia |
Observed flight period |
|
Downey Emerald
Cordulia aenea |
13th June |
2 |
Yes |
23rd May to
22nd June |
|
Black-tailed Skimmer Orthetrum
cancellatum |
22nd June |
30 |
Yes |
23rd May to
26th August |
|
Four-spotted Chaser
Libellula guadrimaculata |
22nd June |
6 |
Yes |
27th May to
15th July |
|
Emperor
AnaxImperator |
22nd June |
3 |
No |
13 June to
15 July |
|
Golden-ringed
Cordulegaster boltonii |
13th June |
1 |
No |
13th June |
|
Common Darter
Sympetrum striolatum |
7th Sept. |
20 |
Yes |
22nd June to
9th October |
|
Southern Hawker
Aeshna cyanea |
4th Sept. |
1 |
No |
22nd June to
13th September |
|
Brown Hawker
Aeshna grandis |
4th Sept. |
3 |
No |
15th July to
7th September |
|
Migrant Hawker
Aeshna mixta |
4th Sept. |
12 |
Yes |
4th August to
9th October |
|
Ruddy Darter
Sympetrum sanguineum |
13th Sept. |
2 |
No |
26th August to
13th September |
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CHAPTER
7
REPTILE REPORT FOR 2005
Recorder Peter Scott
Reptile recording on site
has two components:
-
regular inspections of
‘basking sheets’ (and their surroundings) in two areas:
a) six sheets within 50
metres of the hibernaculum near Colebrook Lake North. [The five sheets of
corrugated iron originally installed have been supplemented by a wooden
sheet that was constructed by vandals as a jetty from which they could
launch boats. Since being removed and laid among the grass near the
hibernaculum, it has proved at least as attractive to snakes as the iron
sheets, so is best regarded as an extra sheet];
b) three sheets
spread along a 200-metre Section of the north shore of Grove Lake. [Two of
the original five sheets were lost during conservation work in winter
2004/05];
-
casual reports of
sightings anywhere on the reserve.
Regular inspections
Sixteen sheet-inspection
visits were made between April and October. All nine sheets were checked
each time. Nine of the visits produced no sightings, but the remainder made
up for this by often producing two or more snakes. The overall results are
summarised in the following table:
Summary of Surveys of Reptile Basking Tins
|
2002 |
2003 |
2004 |
2005 |
| Site visits
made |
11 |
14 |
15 |
16 |
| Total
tin-inspections |
93 |
140 |
150 |
144 |
| Total grass
snakes (or skins) seen |
6 |
14 |
15 |
13 |
| Total adders
seen |
0 |
0 |
3 |
4 |
| Snake
sightings per tin-inspection |
0.06 |
0.10 |
0.12 |
0.12 |
The overall frequency was
similar to that in the previous two years. Adders, first found at the sheets
in 2004, maintained their presence. As usual, the small scale of the survey
must be borne in mind when interpreting these results, but it seems that
snake numbers are fairly stable. It remains to be seen whether the proximity
of the new barn owl box (which was not installed until autumn 2005) has a
deterrent effect.
Casual reports
Nine reptiles (comprising
seven grass snakes and two adders) were reported, compared with 10 in 2004
and 16 in 2003. The most spectacular find was of an adder inside
Colebrook hide (“gently ejected with a stick” by R. Warden and M. Philpot).
Summary
After four years, we can
have some confidence that snake numbers on the reserve are not changing
greatly. The low frequency (total absence in 2005) of lizard reports is a
little puzzling.
I am grateful to those (B.
Archer, J. Carpenter, K. Crick, M. Philpot and R. Warden) who reported
seeing reptiles. Please take the trouble to note your sightings on the forms
in the hides
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CHAPTER
8
MAMMAL REPORT FOR 2005
Recorder Ian White
Dave Williams of Surrey
Wildlife Trust completed his mammal Survey for Moor Green Lakes in June 2005
with assistance from myself.
A high number of wood mice
Apodemus sylvaticus were trapped, but other species were far less
numerous. Fewer animals than expected were caught and his conclusions were
that it appears that small mammals are more numerous where there is less
disturbance from the general public and grazing animals.
The survey also found
evidence of Roe deer Capreolus capreolus, grey squirrel Sciurus
carolinensis, fox Vulpes vulpes, rabbits Oryctolagus
cunniculus, moles Talpa europaea, brown rat Rattus norvegicus
and badger Meles meles. Most of these species have also been
recorded by members of the group on the mammal recording forms placed in the
hides with the exception of badgers. Perhaps too few members enjoy bird
watching in the dark and so there is limited opportunity to view the elusive
and nocturnal badger. Weasels Mustela nivalis and stoats Mustela
erminea are occasionally recorded by members.
The presence of these
species indicates a good small mammal and rabbit population. Furthermore two
records in 2005 indicated that water vole Arvicola terrestris had
been seen on the site. The presence of these animals (which have the dubious
distinction being Britain’s most rapidly declining mammal) will be further
investigated during 2006.
Ian White may be contacted
at – Ian(at)greenboot.co.uk
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CHAPTER
9
REPORT ON NEST BOXES 2005
Dr. Kevin
Briggs
In early February 2004
another 10 wooden nest boxes were replaced with woodcrete nest boxes to
reduce predation rates. The total number of boxes on site was 45 and
during the breeding season the occupancy rate was 91%.
Great Tit
Egg laying started early
this year with the first egg on 5th April and three more pairs
initiating clutches within the following 4 days. A period of cold weather
then delayed nesting in other pairs for about 10 days. The last clutch was
started on 27th April with another late clutch on 16th May, believed to be a
repeat from a failed pair. The most unusual occurrence was the attempt of a
pair to produce a second brood; this is common on the Continent but not in
Great Britain. The pair from the early 5th April clutch fledged 9 young from
10 eggs and then quickly relined the same nest and produced a second clutch
of 6 eggs from 21st May. Unfortunately, a spell of wet and windy weather
caused the eggs to be deserted on about 3rd June. Of the 13 first clutches
monitored, only one pair failed (deserted). The mean laying date was 14th
April (standard deviation sd 6.5 days) and the mean clutch size 9.2 (sd
2.0). Over 50% of the clutches held 10 or more eggs and one had 13,
which again is quite unusual. Eleven pairs hatched eggs (mean brood size on
hatching 7.4, sd 2.6) and fledged young (mean brood size 7.3, sd 2.6). In
summation it was a good breeding season with 128 eggs producing 88 fledged
young
Blue Tit
Eleven pairs used the nest
boxes with the first egg being laid on 7th April. Most pairs waited until
15th April with one late clutch on 1st May. A nest was obviously being used
by 2 females as it contained one egg on 17th April but 17 eggs on 25th
April. Surprisingly the bird (or birds) hatched 15 eggs and fledged the
whole brood of fifteen. The mean laying date was 17th April (sd 6 days) and
the mean clutch size 11.0 (sd 2.6). The mean brood size on hatching was 10.1
(sd 2.3) and rather strangely the same for fledging. This was a very good
year for this species with 121 eggs producing 112 fledged young. No nests
were predated or deserted.
Stock Dove
Nesting attempts for this
species were followed from the beginning of February in an attempt to find
out how many broods they were producing. Unfortunately, due to an accidental
fall I was only able to collect details to July and so probably missed even
later broods. Seven pairs laid first clutches starting from 18th February to
the end of April. Mean egg-laying date was 16th March (sd 22days) and each
laid a clutch of 2 eggs. One clutch was predated and three broods died in
the nest due to lack of food, but 3 pairs fledged 5 young.
The second broods were
attempted in the same nest boxes but by late April and early May competition
for boxes is high from Grey Squirrels and Mandarins. Six pairs attempted
second broods laying on average from 5th May (sd 13.5 days). One pair
produced a clutch of 3 eggs and successfully fledged all three. The others
were mainly predated or the young died.
The third nesting attempted
(by 4 pairs) had a mean laying date of 4th June (sd 10.7 days) and from 8
eggs produced only 2 fledged young.
|
(number) |
1st brood
7 |
2nd brood
6 |
3rd brood
4 |
|
mean egg date
(sd) |
16 March
27 |
5 May
13.5 |
4 June
10.5 |
|
mean clutch
size
(sd) |
2.0
0 |
2.0
0.6 |
2.0
0 |
|
mean brood size
(sd) |
1.6
0.7 |
1.8
0.9 |
2.0
0 |
|
fledged young
(sd) |
0.7
0.9 |
0.8
1.3 |
0.5
0.5 |
In essence, the second
brood did slightly better but overall it is a poor return; 17 breeding
attempts, 34 eggs, 30 young hatched but only 12 fledged young.
Mandarin
Mandarin occupied eight
nestboxes with the first egg being laid on 5th March. Egg dumping and nest
switching by females is common in this species and does lead to large
clutches and desertion. Then there is the problem of Grey Squirrels usurping
the boxes during laying and incubation.
With ringing it is possible
to check the age of the females and also check their movements from box to
box. The oldest female (FC 77957) is 4 years old and her own clutch
was initiated on 5th March; by 17th March she was incubating as
clutch of 24 (12 of her own and 12 from 2 other females, assessed by egg
size, volume an colour). Being an experienced bird she hatched and fledged
19 of the eggs. Female FC 77988 was usurped by Grey Squirrels 1 May from a
clutch of 9 eggs on Colebrook North and moved 600m to Grove Lake for a
repeat clutch of 7 eggs plus 8 from another female. The bird hatched 13 of
the eggs. Female FC 77987 was lifted from a clutch of 16 eggs on 14th April
and on 24th April and from a clutch of 10 eggs on 24th April in boxes 300m
apart. This bird was egg dumping in the first box and on a clutch of her own
in the second. The second box failed to hatch but her breeding season was
not wasted as 14 of the 16 eggs in the first box hatched, 50% would
have been hers. The normal clutch size of a Mandarin is 7 - 12 eggs and by
egg dumping in another female’s clutch it is possible for the dumping female
to increase her output of young and to do it without any problems of
incubation or duckling rearing.
Overall the mean egg laying
date was 5th April (sd 23 days), mean clutch size 15.25(sd 7.9). The range
was 7 - 30 eggs. From 8 clutches (122 eggs) 4 broods of 63 young hatched
(mean brood size 7.8 sd 7.3). Three clutches were usurped by squirrels and
one clutch of 30 eggs deserted.
No Tawny Owls used the
boxes this year, which is surprising as it was such a good vole year. Birds
were seen at the back of Grove Lake where there are many excellent natural
sites in the old alders. Little Owl, again present on site, did not use the
boxes; this could be that they are all in use by the time they naturally
start to breed. The decline in Little Owl nest box use has been matched by
the increase in Mandarin numbers.
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APPENDIX A
PROFILE
OF THE RESERVE
The Moor Green Lakes Nature Reserve lies
partly within the area administered by Wokingham District Council and partly
within the Borough of Bracknell Forest. The River Blackwater, which forms
the boundary between the counties of Berkshire and Hampshire, runs close to
the southern boundary of the reserve. To the north is Finchampstead Ridges,
an area administered by the National Trust. A map of the reserve appears at
Appendix I.
The reserve covers an area of approximately 36
hectares (90 acres), the majority of which lies within the flood plain of
the River Blackwater. It contains three lakes formed out of flooded gravel
pits which are bordered by areas of grassland, planted coppice and
wildflower meadow. Two of the lakes, Colebrook Lake North and Colebrook Lake
South, are separated by an elongated island through the centre of which runs
the old water course of the Colebrook Cut. The third lake, Grove Lake, lies
immediately to the east separated by a narrow strip of land. Within the
lakes are several gravel-capped islands and gravel beaches.
An important feature of the reserve is the
presence of sluices, at the exit of the Colebrook Cut and from Colebrook
Lake into the River Blackwater, which allow the level of the water in
Colebrook Lakes North and South to be controlled within certain limits. By
this method, muddy margins can be exposed ahead of the main spring and
autumn passage of wading birds.
Overall management of the reserve is under the
control of a Steering Group comprised of representatives of CEMEX Ltd.,
Blackwater Valley Countryside Partnership and the Moor Green Lakes Group.
Practical day-to-day management and the collection, recording, assessment
and dissemination of information about the reserve is undertaken by the Moor
Green Lakes Group, which was established in 1993. The group committee
members are listed in Appendix G. The necessary costs of the Group not
covered by membership subscriptions are met by CEMEX. Membership is open to
all with an interest in the reserve, its wildlife and its management,
Public access to the reserve is restricted to
the viewing hides provided by CEMEX which overlook respectively Colebrook
Lake North and Grove Lake (see map at
Appendix I).
Unfortunately vandalism has meant that the hides cannot be left permanently
open, but members of the public may use the hides whenever they are in use
by members of the group (who have access at any time). The Colebrook Lake
hide incorporates a viewing window for observers in wheelchairs. When the
hides are locked, views over the scrapes adjacent to the hides can be
obtained from the screened viewing points alongside the hides. Views across
the reserve can also be obtained from viewing points along the footpath,
which runs along the western and southern sides of the reserve.
The main access to the reserve is from Lower
Sandhurst Road where a car park has been provided (Ordnance Survey grid
reference SU805 628). The shortest access to the Grove Lake hide is from the
Rambler’s Car Park at the entrance to the Horseshoe Lake Water Sports Centre
off Mill Lane (grid reference SU820620).
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APPENDIX B
EVERSLEY GRAVEL PITS (INC MOOR GREEN LAKES
RESERVE)
ANNUAL BIRD REPORT 2005
LITTLE GREBE
Resident and
winter visitor. During the breeding season seven pairs were present in the
Fox lane area rearing at least one brood. A maxima of 27 were recorded on
Aug.30th.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
2 |
2 |
2 |
1 |
2 |
2 |
2 |
27 |
21 |
5 |
4 |
4 |
GREAT CRESTED GREBE
Common
resident. A maximum of 22 was recorded on March 14th. A total of four pairs
were present during the summer, but breeding was unsuccessful.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
15 |
18 |
22 |
10 |
9 |
8 |
6 |
6 |
6 |
7 |
16 |
17 |
BLACK NECKED GREBE
Rare
visitor. One was present on Oct.7th to 9th on the Hampshire new workings (ML
et al). The third site record the last of which was a long staying bird in
2003.
CORMORANT
Common winter visitor
that oversummers in small numbers. Recorded in all months with a site record
count of 98 on Jan. 7th (BMA).
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
98* |
69 |
40 |
7 |
0 |
2 |
2 |
3 |
12 |
17 |
34 |
71 |
LITTLE EGRET
Regular visitor
with increasing frequency. A substantial increase in records relating to
birds being present in the Blackwater Valley. Recorded in all months except
April, May, August and September. Records on 60 dates relating to 1/3 birds
except four were present Jan.9th and Dec.1st.
GREY HERON
Common resident.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
15 |
5 |
3 |
3 |
4 |
3 |
4 |
6 |
2 |
2 |
3 |
4 |
MUTE SWAN
Common resident and
winter visitor. Three pairs bred rearing six young.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
28 |
29 |
7 |
10 |
22 |
12 |
37 |
32 |
9 |
7 |
8 |
18 |
GREYLAG GOOSE
Common visitor
numbers increasing. A maximum of 74 on Sept.24th (JMC) was a site record
count.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
21 |
13 |
8 |
6 |
5 |
7 |
7 |
0 |
74* |
73 |
12 |
20 |
SNOW GOOSE
Resident with
numbers declining. In the early and late winter periods up to 6 and 5 birds
were present respectively, declining to 4 birds by the year end. Although
birds were present on the site in summer there was no evidence of breeding.
CANADA GOOSE
Abundant
resident.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
180 |
109 |
276 |
- |
- |
98 |
105 |
60 |
- |
110 |
210 |
376 |
BARNACLE GOOSE
Very common
resident. One pair (cf 8 in 2004) reared one young.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
80 |
101 |
- |
6 |
11 |
12 |
2 |
30 |
54 |
61 |
56 |
62 |
EGYPTIAN GOOSE
Resident in
increasing numbers. Two pairs attempted breeding, one successfully rearing
broods of 2 and 6 the latter of which hatched in late October. The second
consecutive year in which breeding has occurred. The count of 66 on Oct.28th
was a site record (BMA).
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
15 |
14 |
21 |
10 |
14 |
19 |
29 |
41 |
50 |
66* |
36 |
43 |
SHELDUCK
Regular visitor.
Recorded as follows: 2, April 5th, 1, April 9th and 1, August 4th.
MANDARIN
Common summer visitor
resident in small numbers. At least four pairs bred successfully including
use of nest boxes. Young were seen on June 3rd.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
18 |
2 |
6 |
4 |
8 |
6 |
2 |
1 |
1 |
2 |
5 |
8 |
WIGEON
Very common winter
visitor. Birds were recorded up to April 7th and from Aug. 11th. Other
records were of singletons on May 5th and July 11th to 12th.The maximum
count was of 432 on Dec.21st.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
398 |
247 |
18 |
12 |
1 |
0 |
1 |
15 |
88 |
284 |
398 |
432 |
GADWALL
Very common winter
visitor that breeds in small numbers. A minimum of 11 males over-summered
with up to three females with breeding successful. At least two broods of
four and ten young were reared. The fourth successive year that breeding has
been confirmed. The maximum count was of 174 on Nov.21st.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
133 |
215 |
26 |
16 |
10 |
12 |
11 |
20 |
44 |
76 |
174 |
84 |
TEAL
Common winter visitor that
occasionally summers. The count of 138 on Dec.31st was a site record (IHB).
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
40 |
22 |
12 |
6 |
0 |
0 |
0 |
15 |
25 |
13 |
91 |
138* |
MALLARD
Common resident and
winter visitor. Numbers are declining.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
117 |
107 |
120 |
15 |
30 |
- |
33 |
30 |
43 |
76 |
86 |
72 |
GARGANEY
Scarce visitor. A pair
in eclipse were present on July 7th (BMA, RMW, IHB). Recorded in three of
the last four years.
PINTAIL
Regular winter visitor.
A good year, recorded as follows: Two males, Jan.1st to 3rd; 1, Jan.19th; 1
male Oct.24th; two, one female, one imm male from Dec.16th to year end.
Records in mid winter are becoming annual.
SHOVELER
Common winter visitor.
Recorded until April 24th and from Aug.6th. The maximum count was of 49 on
Feb.5th
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
48 |
49 |
31 |
7 |
0 |
0 |
0 |
7 |
9 |
20 |
22 | |