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CEMEX remains committed to
the future of the Moor Green Lakes Nature Reserve and is greatly
appreciative of the work undertaken by the Group in its continuing role in
managing the land. This annual report, which marks the 15th anniversary of
the publication, is testament to the enthusiasm and commitment of the Group
and we are delighted to continue in its support.
CEMEX UK Materials Ltd
CEMEX House
Coldharbour Lane
Thorpe, Egham
Surrey TW20 8TD
August 2008
CEMEX UK Operations
Limited
CEMEX
House, Coldharbour Lane, Thorpe, Egham, Surrey TW20 8TD, United Kingdom.
Phone:
+44 (0) 1932 568833 Fax: +44 (0) 1932 568933
www.cemex.co.uk
Registered
in England and Wales: Company Number 658390 Registered Office: CEMEX
House, as above.
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CHAPTER 1
INTRODUCTION TO THE FIFTEENTH REPORT OF THE
MOOR GREEN LAKES GROUP
Peter Scott
Welcome to our annual report on the wildlife
found on the reserve and the maintenance work carried out there during the
last year. Again the numbers of species seen was generally good: even
reptiles returned to their usual numbers after the disappointing picture in
2006. The main exception was dragonflies, for which the poor summer weather
was a factor in their reduced numbers.
For the first time since 1995, moths have been surveyed. As Colin Proudley
reports in chapter 11, the numbers found are very encouraging. Colin intends
to continue his observations and we are grateful to him for joining our team
of recorders to fill an important gap in our knowledge.
Another new contribution is a chapter on the ringing of birds on Tern
Island by Tim Ball, Paul James and Karen Tucker of the Reading and
Basingstoke Ringing Group. Their efforts in doing this and in producing this
report are greatly appreciated, as are those of Bruce Archer in arranging
the work.
Having contributed an initial set of bumblebee data last year, Steve Farmer
has repeated the exercise in 2007, as reported in chapter 10. He and his
wife Shelia have also supplied a report on flowers found along the riverside
footpath beside Manor Farm, included here as an addition to the chapter on
botanical surveying. As the restoration of Manor Farm continues, we may wish
to extend most of our surveys to cover it, though this would be a
considerable increase in workload in some cases. Ian Brown's bird reports
have always included it, of course, and several of the nest boxes examined
regularly by Bruce Archer are located on Manor Farm.
On the administrative front, two members of our committee resigned their
posts at our AGM in February 2007. Robert Godden relinquished the role of
committee secretary and Keith Littler withdrew from that of membership
secretary. They have been replaced by Roger Murfitt and David Bishop
respectively. We are very grateful to Robert and Keith for their past
services and to Roger and Dave for stepping into the vacancies.
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CHAPTER 2
SITE MANAGEMENT REPORT
APRIL 2007 TO MARCH 2008
Dr
Sue Dent
Countryside & Access Officer
Blackwater Valley
Countryside Partnership
General Site
Management 2007/8
Islands
and scrapes
Long Island
is beginning to show real signs of improvement now that the pontoon is
available to get volunteers and equipment across to the island. The
increased management is gradually reducing the cover of scrub and bramble
and encouraging a shorter grass sward.
On Tern Island the
control of bramble and perennial vegetation has gradually become more
difficult over the years. As an experiment the island was sprayed this
summer with a general herbicide and this certainly made it much easier to
clear the island in the winter work programme. The impact on the re-growth
next summer will be monitored to see how well it works. The fenced enclosure
on Tern Island is beginning to deteriorate and was reinforced with sand bags
to stop predators getting underneath. Some shelters for the terns to nest
under were also put out over the winter and these will hopefully give them
some protection from the gulls.
Plover and Sandpiper
Islands were also cleared of vegetation. If
the spraying of Tern Island is successful it may be extended to Plover next
year.
Grassland
Controlling scrub on the
grassland is an on-going commitment and is mostly done by volunteers both by
hand and with the help of some machines. As usual the meadows have been
grazed this year. We have changed to a grazier who can provide native
breeds of cattle, which should be more suitable to the type of poor grazing
we have at Moor Green and may be more likely to graze the scrub and
bramble. This year we have had Irish Moiles and a group of Belted Galloways
which seem to have settled in well and we hope to use them again next year.
The FMD outbreak meant that grazing started later than planned, but we were
very lucky to be able to go ahead at all.
Plantations to southern
edge of Reserve.
The rotational cutting of
the plantation has continued, as well as thinning of some blocks that are to
remain as wooded areas. It is hoped that this will encourage a diverse
ground flora to develop.
Other reserve matters
Path to Colebrook Hide.
MGLG successfully applied for a grant to
resurface the path to Colebrook Hide from SC Johnson and the Blackwater
Valley Countryside Trust.
The path from Lower
Sandhurst Road car park was repaired after it was damaged in the
storms last summer which turned it briefly into a stream and left some large
gullies in the surface.
A new Map Board has
been installed close to the bridge across the River Blackwater in
collaboration with BVCP and Bracknell Forest BC. It shows the main circular
walks around the area, including Horseshoe Lakes.
Conservation
Volunteers
Conservation volunteers
make an enormous contribution to the management of the reserve. The tasks
are made up of Sundays by the MGLG and a regular monthly Tuesday from the
BVCP volunteers.
The Moor
Green Lakes Group have been out for 7 Sundays from September to March
and several extra tasks to pick up special jobs such as transporting
sandbags to Tern Island. Overall they have done over 80 days of practical
work, with an average of 11 people out on the Sunday Tasks. Special thanks
to Peter Scott, Simon Weeks, Tony Elston and Tim Mockridge who have led the
Moor Green Lakes Group tasks this year. There have also been two special
tasks, including a BBQ, aimed at encouraging newcomers and in total 13 new
volunteers came along this season.
This has been backed up by
the Blackwater Valley Tuesday group who have done 9 tasks and 178
days, with an average of 19 volunteers per task. This has included two days
working on the new Manor Farm workings. Altogether this adds up to a minimum
of 256 volunteer days or over £14 thousand pounds worth of work.
Extra thanks to Peter Scott
who plans the practical work and makes sure that the volunteer teams know
what needs doing each month and to Simon Weeks, the Site Liaison Officer,
who keeps an eye on the site on a day-to-day basis and checks on cattle
while they are on site.
Manor Farm
The BVCP Tuesday group has
started to carry out work on the new Manor Farm site. This year they have
carried out more trial planting for the new reedbed. The results from the
planting done last year have been mixed, but the most successful method
seems to be simple root/rhizome cuttings. To date there have been
sufficient reeds on Moor Green to provide material for transplanting.
The Tuesday volunteers and
a BTCV-run group have also been thinning the established plantations
adjacent to Lower Sandhurst Road and managing some newer planting.
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CHAPTER
3
REPORT
ON BIRDS 2007
Recorder: Ian
Brown
During the year 136 species were recorded of
which 67 were present in suitable breeding habitat in the summer. The latter
maintains last years equal highest annual recorded total. Barn Owl was
gained as a breeding species but Barnacle Goose lost. The number of species
recorded was boosted by an exceptional year (the best on record; see article
by Bruce Archer in newsletter) for waders, with 24 species recorded (cf
previous high, 21 in 2006). These figures overall partly reflect habitat
improvement and increased habitat diversity but especially the fact that
large areas of the Manor farm workings were maintained in drained state for
most of the year. One new species was added to the site list, Mealy Redpoll,
bringing the total number of species recorded to 209.
In the early winter period waterfowl numbers
were generally good despite relatively mild weather. Wigeon numbers continue
to increase year on year and 2007 was no exception with a site record count
of 597 in January. A male Peregrine remained faithful to the pylon by Mill
lane and two male Ruddy Ducks graced Horseshoe lake for several weeks.
Little Egret’s were again regular visitors and a handful of Golden Plover
were recorded. Dunlin and Oystercatcher were particularly noteworthy in
February.
Returning waders began to appear in mid March
with Ringed Plover, Redshank and Little Ringed Plover recorded before the
months end. Also in March were Barn Owls taking up residence in the west owl
box. Arrivals of passerines was much later this year with for example House
and Sand Martins not being recorded until the latter half of April.
Nevertheless there were plenty other birds in the early part of April with
another Oystercatcher, a good passage of Yellow Wagtails, five Little Gulls,
two Greenshank, only the second site record of Avocet and Spotted Redshank.
This however only proved to be the appetizer for May that proved to be an
outstanding month especially for waders. It began on 1st with a Little
Stint, 2 Wood Sandpipers together and a Whimbrel! These were followed mid
month by a party of 11 Dunlin, another Spotted Redshank, good numbers of
Ringed Plover, Oystercatcher, the third site record of Knot and a party of 7
Sanderling, comfortably the largest group of this species recorded. These
birds were interspersed with an Arctic Tern, the first site record of Syke’s
Wagtail (race of Yellow) and of course all the returning breeding birds.
Overall it was another successful breeding
season. Waders fared with mixed success with Redshank and Lapwing
successfully fledging young but Little Ringed Plovers had a poor year
despite good numbers of birds present only one young was definitely reared.
Amongst waterfowl Tufted Duck and Mandarin did moderately well as did both
species of breeding grebe and Gadwall successfully reared two broods, now a
firmly established breeding species. Egyptian Geese go from strength to
strength and despite early broods in January not surviving, still reared at
least one brood. Black Headed Gull and Common Tern largely failed for the
second year in succession with Tern Island again being abandoned
prematurely, Mink? The major successes were the first confirmed breeding in
the recording area of Greylag Goose and of course successful occupancy of
the west owl box by Barn Owls rearing four young and providing good viewing
opportunities for all as the adults feverishly hunted for prey. Other
species that had a good breeding season either on the reserve or nearby were
Little Owl, Hobby, Kingfisher, Grey Wagtail and Skylark. Breeding may have
been attempted by Grey Heron for only the second time.
The flow of notable wader records continued in
July (which can often be a quieter month) with three records of Black Tailed
Godwit, up to three Turnstone, four Whimbrel, a Curlew and another
Oystercatcher. August continued in the same vein with five Greenshank, a
party of eight Black Tailed Godwits, plus a Little Stint and a Ruff both of
which lingered for several days. Other records during the month included a
Garganey on three dates, Red Kite (scarcer this year) and Peregrine.
September began with probably the highlight of the year which unfortunately
was only witnessed by one lucky observer who saw a single group of 28 Black
Tailed Godwits on the Manor Farm site. This will be a county record if
accepted by Berkshire! However for those who missed out there was plenty of
additional fare with another long staying Ruff, three Curlew Sandpipers,
another Little Stint, a Grasshopper Warbler, more Curlew, Whinchat and a
Rock Pipit. Wader species number 24 occurred in late October with a Jack
Snipe. Other notable autumn records included the customary good geese counts
with site records for Greylag (103) and Egyptian Geese (108) at roost.
The year ended with another site record, a
remarkable influx of Golden Plover to the Lapwing flock on the works. Good
numbers were seen over a period of several days finally peaking at 630,
approximately 15 times higher than the previous best! The year ended with
returning Little Egrets, Goosander, a Caspian Gull, Brent Goose and
Peregrine. Finally, but not least the only addition to the site list during
the year was Mealy Redpoll, when one of this former subspecies was sharply
detected in the alders near Longwater sewage works.
Again my thanks go to the growing band of
observers who submit records especially including those who provide
observers names on the log sheet (it is helpful if there is a need to follow
up on any record). In particular I would thank again the small band of
stalwarts covering the site on a daily basis irrespective of weather!
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CHAPTER 4
Moor Green Lakes Ringing
Project, 2007 Report
Tim Ball, Paul James, Karen Tucker
(Reading and Basingstoke Ringing Group)
1 Black-headed
Gull
Black-headed Gulls have
been nesting at Moor Green Lakes since 2003. All the chicks which fledged in
the first year were ringed by Kevin Briggs. In 2007 the Moor Green Lakes
Group asked us to ring the Gulls and any Terns that nested on Tern Island on
Colbrook Lake North. No Terns nested this year and only Gulls were ringed.
In the last couple of years
most of the Gulls have nested inside the fenced area of the island and only
a few have nested on the unprotected areas. Since birds first bred here in
2003 the colony has grown significantly - however productivity has dropped:
-
2003 - 8 pairs raised 21 young
-
2004 - Approx 80 pairs reared in excess of 130 young
-
2005 - Approx 122 pairs reared in excess of 125 young
-
2006 - Approx 180 pairs reared only about 100 young - a
predator of some kind got inside the fence and killed a lot of young
The first ringing trip in
2007 was carried out on 4 June and 52 chicks were ringed. There were a large
number of nests with eggs still being incubated and about 20 or 30 young
that were too young to ring. Unfortunately it was also clear that the very
wet weather at the end of May had taken a significant toll and there were
between 20 and 30 dead small young present. A complete nest count located
124 nests.
A second trip on 15 June
proved how disastrous the bad weather over the Bank Holiday weekend had been
- it was clear that all the un-hatched eggs have failed, although some
adults were still attempting to incubate the dead eggs. No new young had
hatched since the first trip and we ringed all the remaining young - there
were another 27 making 79 ringed in all. But the continuing unsettled
weather had led to more young dying - including 4 of those ringed on 4 June.
A further dead bird was found during maintenance work on 30 August – this
had probably died at around the time it would have fledged. The final
productivity of 74 birds from 124 nests is well below normal Black-headed
Gull productivity.
There have been no
subsequent recoveries of the ringed birds.
2 Little Ringed
Plover
Little Ringed Plovers at
Moor Green were monitored with assistance from Chris Gent and Bruce Archer
as part of a wider project across a number of sites in Berkshire and
Hampshire. All approaches to nests and breeding birds were carried out by
Tim Ball under the appropriate Schedule 1 license. The results were
submitted to the BTO’s Little Ringed & Ringed Plover Breeding Survey.
Colbrook Lake
One
pair apparently attempted
to breed but probably failed before any young hatched.
New Workings
Three pairs bred with a
fourth possibly present
Pair A: Pair seen changing
over on a nest on 9 May. 1 young was first seen on 29 May and was still
present on 15 June when it was very well grown and may have already fledged.
Generally occupying the northern central part of the New Workings.
Pair B: 4 young first seen
on 5 June, only 3 young were seen on 8 June and were still present on 15
June when 2 were ringed and had primary feathers sprouting about 3 or 4 mm
out of the pin so were 10 to 14 days old. Generally occupying the western
part of the New Workings.
Pair C: 3 young first seen
on 9 June, reduced to 2 young on 10, 12 & 14 June. The parents were behaving
as if they still had young on 15 June. Generally occupying the north eastern
part of the New Workings.
One adult seen occasionally
at the extreme west end of the New Workings may represent an extra pair.
Adults seen occasionally on
the restored part of the New Workings were thought to be birds from the main
New Workings pit.
There were very few records
of young after 16 June and it is thought unlikely that more than 2 fledged
successfully – one from pair A and one from pair B or C.
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CHAPTER 5
BOTANICAL SURVEY 2007
Peter Scott
Quantitative surveys of the
meadow areas on the north and west sides of Colebrook Lake North have been
undertaken since 1997. The method used is based on the National Vegetation
Classification. Ten one-metre-square quadrats are identified, five on each
side of the lake. In 2007 two visits were made, in May and July. All ten
quadrats were surveyed each time.
In each of the sample
squares the species present were identified and quantified by the area of
the quadrat they covered -
| 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) |
Table A gives the frequency
and abundance of the forty-five species other than grasses (which were not
surveyed) found in the quadrats. This is more than in any previous year.
However, previously each quadrat has been surveyed once only, so the
increase is probably a result of more intensive surveying and is therefore
more apparent than real.
Table B lists, in column
B1, other species noted in the immediately surrounding areas. Two other
sites were also surveyed. These were the Colebrook Cut Wood and the Corner
Wood (near the river). The additional species found at these two sites are
given in columns B2 and B3. Species listed in Table A are repeated in Table
B only if they were found in one or both of the two woods.
The most frequent and/or
abundant species were mostly the same as in 2006: Black Knapweed, Lady’s
Bedstraw, Cut-leaved Crane’s-bill, Oxeye Daisy, Lesser Stitchwort, Ribwort
Plantain, Clover (both Red and White) and Smooth Tare. The north side of
the lake seems to have a more diverse flora than the west side. The north
bank, of course, receives more direct sunshine and this, together with the
steeper slope to the lake and the fact that the soil is rather thin in
places, creates rather dry conditions. This makes it more difficult for
species which become dominant in ‘richer’, damper soils to thrive.
When the reserve was
created, the meadow area was planted with a wild-flower mix of 24 species. In 2007 seventeen of the original sown species were found in the quadrats
and a further three were noticed nearby.
This indicates that the botanical
diversity of the reserve is being maintained. However, a full list of
species present on the reserve, for comparison with the surveys carried out
up to 1994, is overdue and will be attempted in the next couple of years.
I am grateful to Pauline
Crick, Irene Draper, Doreen Dye, Steve and Sheila Farmer and Delphine Hoyle
for their help with the survey.
Table A. Quadrat Surveys
|
Species |
Common name |
Shore |
|
|
North |
West |
|
S |
Achillea millefolium |
Yarrow |
I (3) |
0 |
|
|
Agrimonia eupatoria |
Agrimony |
IV
(1-2) |
0 |
|
|
Bellis perennis |
Daisy |
I (1) |
0 |
|
S |
Centaurea nigra |
Black Knapweed |
IV
(4-7) |
V
(4-5) |
|
|
Centaurium erythraea |
Common Centaury |
I (1) |
0 |
|
|
Cerastium fontanum |
Common Mouse-ear
|
II
(1) |
III
(1-3) |
|
|
Cirsium arvense |
Creeping Thistle |
I (1) |
0 |
|
|
Crepis capillaris |
Smooth Hawk’s-beard |
III
(1-4) |
0 |
|
|
Crepis versicaria |
Beaked Hawk’s-beard |
I (1) |
0 |
|
S |
Daucus carota |
Wild Carrot |
IV
(1) |
0 |
|
|
Galium aparine |
Cleavers |
I (2) |
I (1) |
|
|
Galium sp. |
Bedstraw (unidentified) |
0 |
I (1) |
|
S |
Galium verum |
Lady’s Bedstraw |
V
(1-8) |
III
(2-6) |
|
|
Geranium dissectum |
Cut-leaved Crane’s-bill |
IV
(1-4) |
V
(1-7) |
|
S |
Geranium pratense |
Meadow Crane’s-bill |
II
(1-6) |
0 |
|
S |
Hypericum perforatum |
Perforate St.John’s-wort |
IV
(2-4) |
0 |
|
S |
Hypochaeris radicata |
Cat’s-ear |
III
(1) |
0 |
|
|
Lathyrus pratensis |
Meadow Vetchling |
III
(1-4) |
III
(2-6) |
|
S |
Leucanthemum vulgare |
Oxeye Daisy |
V
(1-8) |
IV
(1-3) |
|
S |
Lotus corniculatus |
Common Bird’s-foot-trefoil |
III
(2-7) |
III
(1-8) |
|
|
Lychnis flos-cuculi |
Ragged-Robin |
I (1) |
0 |
|
S |
Medicago lupulina |
Black Medick |
I (1) |
I (1) |
|
|
Myosotis discolor |
Changing Forget-me-not |
I (1) |
0 |
|
S |
Plantago lanceolata |
Ribwort Plantain |
V
(4-7) |
V
(3-8) |
|
S |
Prunella vulgaris |
Selfheal |
III
(1-4) |
I (1) |
|
|
Quercus robur |
Pedunculate Oak |
III
(1) |
0 |
|
S |
Ranunculus acris |
Meadow Buttercup |
I (2) |
V
(1-2) |
|
|
Ranunculus repens
|
Creeping Buttercup |
II
(1-8) |
IV
(4-5) |
|
|
Rubus fruticosus |
Bramble |
I (2) |
0 |
|
S |
Rumex acetosa |
Common Sorrel |
III
(1-2) |
V
(1-3) |
|
|
Rumex acetosella |
Sheep's Sorrel |
III
(1-3) |
0 |
|
|
Rumex sp. |
Dock (unidentified) |
0 |
I (1) |
|
|
Senecio jacobaea |
Ragwort |
III
(1) |
0 |
|
|
Stellaria graminea |
Lesser Stitchwort |
IV
(1-5) |
IV
(1-5) |
|
S |
Taraxacum officinale |
Dandelion |
III
(1-2) |
II
(1) |
|
|
Trifolium arvense |
Hare’s-foot Clover |
I (4) |
0 |
|
|
Trifolium dubium |
Lesser Trefoil |
V
(1-3) |
0 |
|
|
Trifolium pratense |
Red Clover |
III
(3-5) |
V
(4-8) |
|
|
Trifolium repens |
White Clover |
IV
(1-5) |
III
(1-4) |
|
|
Urtica dioica |
Stinging Nettle |
I (1) |
0 |
|
|
Veronica hederifolia |
Ivy-leaved Speedwell |
I (1) |
0 |
|
|
Veronica serpyllifolia |
Thyme-leaved Speedwell |
I (1) |
0 |
|
S |
Vicia sativa
|
Common Vetch |
II
(1-2) |
I (1) |
|
|
Vicia sp. |
Vetch (unidentified) |
III
(1) |
IV
(1-2) |
|
S |
Vicia tetrasperma |
Smooth Tare |
IV
(1-5) |
V
(1-3) |
Note: S = Sown species
Table B. Plants Recorded in other locations
|
B1 - Outside
recorded squares |
|
B2 - Colebrook
Cut wood |
|
B3 - Corner wood |
| |
|
Species |
Common name |
B1 |
B2 |
B3 |
|
Anthriscus sylvestris |
Cow Parsley |
|
X |
X |
|
Arctium minus |
Lesser Burdock |
X |
|
|
|
Artemisia vulgaris |
Mugwort |
X |
|
|
|
Bryonia dioica |
White Bryony |
X |
|
|
|
Cardamine pratensis |
Cuckooflower |
X |
|
|
|
Cirsium palustre |
Marsh Thistle |
|
X |
X |
|
Cirsium vulgare |
Spear Thistle |
X |
X |
|
|
Clinopodium vulgare |
Wild Basil |
|
X |
|
|
Conyza canadensis |
Canadian Fleabane |
|
X |
|
|
Daucus carota |
Wild Carrot |
|
X |
|
|
Digitalis purpurea |
Foxglove |
|
X |
X |
|
Epilobium parviflorum |
Hoary Willowherb |
|
|
X |
|
Filago vulgaris |
Common Cudweed |
X |
|
|
|
Galium aparine |
Cleavers |
X |
X |
X |
|
Geum urbanum |
Wood Avens |
|
X |
|
|
Heracleum sphondylium |
Hogweed |
X |
|
X |
|
Humulus lupulus |
Hop |
X |
|
|
|
Hypericum perforatum |
Perforate St.John’s-wort |
X |
X |
X |
|
Iris pseudacorus |
Yellow Iris |
X |
|
|
|
Knautia arvensis |
Field Scabious |
X |
|
|
|
Lactuca serriola |
Prickly Lettuce |
X |
|
|
|
Lapsana communis |
Nipplewort |
X |
X |
X |
|
Leucanthemum vulgare |
Oxeye Daisy |
|
X |
|
|
Lychnis flos-cuculi |
Ragged-Robin |
X |
X |
|
|
Lycopus europaeus |
Gipsywort |
X |
|
X |
|
Lysimachia vulgaris |
Yellow Loosestrife |
X |
|
|
|
Mentha aquatica |
Water Mint |
|
|
X |
|
Myosoton aquaticum |
Water Chickweed |
|
X |
|
|
Oenanthe crocata |
Hemlock Water-dropwort |
X |
|
X |
|
Polygonum aviculare |
Knotgrass |
X |
|
|
|
Primula veris |
Cowslip |
X |
|
|
|
Pulicaria dysenterica |
Common Fleabane |
X |
|
|
|
Ranunculus acris |
Meadow Buttercup |
X |
X |
|
|
Ranunculus repens |
Creeping Buttercup |
X |
|
X |
|
Rubus fruticosus |
Bramble |
X |
X |
X |
|
Rumex crispus |
Curled Dock |
X |
|
|
|
Rumex obtusifolius |
Broad-leaved Dock |
X |
X |
|
|
Rumex sanguineus |
Wood Dock |
|
|
X |
|
Scrophularia nodosa |
Common Figwort |
X |
|
|
|
Senecio jacobea |
Ragwort |
X |
X |
X |
|
Silene latifolia |
White Campion |
X |
|
|
|
Sonchus asper |
Prickly Sow-thistle |
X |
|
|
|
Stachys officinalis |
Betony |
X |
|
|
|
Stachys sylvatica |
Hedge Woundwort |
|
X |
X |
|
Taraxacum officinale |
Dandelion |
X |
|
X |
|
Torilis japonica |
Upright Hedge-parsley |
|
X |
X |
|
Ulex europaeus |
Gorse |
X |
|
|
|
Urtica dioica |
Stinging Nettle |
|
X |
X |
|
Veronica chamaedrys |
Germander Speedwell |
X |
X |
|
|
Veronica montana |
Wood Speedwell |
|
|
X |
Manor
Farm Riverside Path Botanical Survey
Steve and Sheila Farmer
A botanical survey was
conducted on 12 June 2007 along the public footpath on the southern boundary
of the Manor Farm Gravel Quarry. This part of the Blackwater Valley path was
established about 7 years ago along the edge of fields that existed at that
time on the northern bank of the River Blackwater. It stretches from the
small footbridge at the south west corner of Colebrook South Lake (SU805621)
to Longwater Road just north of the Sewage Farm near Finchampstead Bridge
(SU795624). The total length is approximately 1300 metres. Plants growing
on either side of the path were recorded, but not those on the river bank.
The path was surveyed for
flowering plants including all annuals and herbaceous perennials. Woody
shrubs and climbers were included, but saplings and trees were excluded. Two
non-flowering plants, namely horsetail and bracken, were also included as
these formed a significant part of the vegetation along the sides of the
path in some places.
The path was divided into
five sections of approximately 250 metres each and then the results were
combined to give an overall frequency of occurrence of each species. The
frequency was assessed according to the following table.
|
Number of
individual plants |
Percentage
of path length along which plant occurs. |
Frequency
class |
|
few plants (1-5) |
|
1 |
|
several plants (6-10) |
|
2 |
|
many plants (11-20) |
|
3 |
|
|
<1% |
4 |
|
|
1-2% |
5 |
|
|
3-5% |
6 |
|
|
6-10% |
7 |
|
|
11-20% |
8 |
|
|
21-40% |
9 |
|
|
41-100% |
10 |
The overall frequency of
each species is given in Table A.
This initial survey
revealed the surprisingly high number (74) of different kinds of flowering
plants. This may reflect the variety of habitat along the path. Some parts
have become rather overgrown with trees and saplings during the last 7
years, while others remain fairly open. Coarse vegetation such as Bramble,
Broom, Stinging Nettle, Mugwort and Hogweed were dominant along some
stretches. However, other parts had much lower-growing subjects such as
Greater and Lesser Stitchwort. An area of disturbed ground near the
abstraction sump, which was installed by Cemex during the winter 2006/7, had
several low-growing subjects such as Corn Spurrey, Field Pansy and
Shepherd’s-purse. These are often found as weeds of cultivation on arable
land. Sand Spurrey was found among the gravel of the path at several places
towards the western end of the path. Dog-rose, Honeysuckle and Hop were
also found mostly along this section of the path.
TABLE A
|
SPECIES |
COMMON NAME |
FREQUENCY |
CLASS |
|
Achillea millefolium |
Yarrow |
5% |
6 |
|
Alliaria petiolata |
Garlic
Mustard |
few |
1 |
|
Artemisia vulgaris |
Mugwort |
5% |
6 |
|
Bellis perennis |
Daisy |
few |
1 |
|
Calystegia sepium |
Hedge
Bindweed |
<1% |
4 |
|
Capsella bursa-pastoris |
Shepherd's-purse |
few |
1 |
|
Centaurea nigra |
Black
Knapweed |
few |
1 |
|
Cerastium fontanum |
Common
Mouse-ear |
<1% |
4 |
|
Chaerophyllum temulum |
Rough
Chervil |
5% |
6 |
|
Chenopodium album |
Fat-hen |
few |
1 |
|
Cirisium arvense |
Creeping Thistle |
<1% |
4 |
|
Cirisium spp |
Thistle
(species) |
few |
1 |
|
Crepis capillaris |
Smooth
Hawk’s-beard |
1% |
5 |
|
Crepis vesicaria |
Beaked
Hawk’s-beard |
several |
2 |
|
Cytisus scoparius |
Broom |
15% |
8 |
|
Digitalis purpurea |
Foxglove |
several |
2 |
|
Epilobium hirsutum |
Great
Willowherb |
several |
2 |
|
Epilobium montanum |
Broad-leaved Willowherb |
few |
1 |
|
Galium aparine |
Cleavers |
5% |
6 |
|
Geranium dissectum |
Cut-leaved Crane’s-bill |
1% |
5 |
|
Geranium molle |
Dove’s-foot Crane’s-bill |
many |
3 |
|
Glechoma hederacea |
Ground-ivy |
1% |
5 |
|
Heracleum sphondylium |
Hogweed |
10% |
7 |
|
Humulus lupulus |
Hop |
1% |
5 |
|
Hypericum perforatum |
Perforate St.John’s-wort |
several |
2 |
|
Hypochaeris radicata |
Common
Cat’s-ear |
2% |
5 |
|
Impatiens glandulifera |
Indian
Balsam |
<1% |
4 |
|
Lamium album |
White
Dead-nettle |
many |
3 |
|
Lapsana communis |
Nipplewort |
many |
3 |
|
Leucanthemum vulgare |
Oxeye
Daisy |
several |
2 |
|
Linaria vulgaris |
Common
Toadflax |
many |
3 |
|
Lonicera periclymenum |
Honeysuckle |
several |
2 |
|
Lotus corniculatus |
Common
Bird’s-foot-trefoil |
few |
1 |
|
Matricaria discoidea |
Pineappleweed |
many |
3 |
|
Myosotis arvensis |
Field
Forget-me-not |
few |
1 |
|
Oenanthe cracata |
Hemlock
Water-dropwort |
<1% |
4 |
|
Oenothera glazioviana |
Large-flowered Evening-primrose |
few |
1 |
|
Plantago lanceolata |
Ribwort
Plantain |
2% |
5 |
|
Plantago major |
Greater
Plantain |
1% |
5 |
|
Polygonum aviculare |
Knotgrass |
few |
1 |
|
Prunella vulgaris |
Selfheal |
few |
1 |
|
Ranunculus acris |
Meadow
Buttercup |
<1% |
4 |
|
Ranunculus repens |
Creeping Buttercup |
<1% |
4 |
|
Rosa
canina |
Dog-rose |
several |
2 |
|
Rubus caesius |
Dewberry |
5% |
6 |
|
Rubus fruticosus |
Bramble |
25% |
9 |
|
Rumex acetosella |
Sheep's
Sorrel |
<1% |
4 |
|
Rumex obtusifolius |
Broad-leaved Dock |
1% |
5 |
|
Senecio jacobaea |
Ragwort |
many |
3 |
|
Senecio vulgaris |
Groundsel |
few |
1 |
|
Sisymbrium officinale |
Hedge
Mustard |
several |
2 |
|
Solanum dulcamara |
Bittersweet |
few |
1 |
|
Sonchus asper |
Prickly
Sow-thistle |
many |
3 |
|
Sonchus oleraceus |
Smooth
Sow-thistle |
many |
3 |
|
Spergula arvensis |
Corn
Spurrey |
many |
3 |
|
Spergularia rubra |
Sand
Spurrey |
1% |
5 |
|
Stellaria graminea |
Lesser
Stitchwort |
1% |
5 |
|
Stellaria holostea |
Greater
Stitchwort |
1% |
5 |
|
Stellaria media |
Common
Chickweed |
many |
3 |
|
Stellaria nemorum |
Wood
Stitchwort |
many |
3 |
|
Taraxacum officinale |
Dandelion |
many |
3 |
|
Trifolium dubium |
Lesser
Trefoil |
<1% |
4 |
|
Trifolium pratense |
Red
Clover |
many |
3 |
|
Trifolium repens |
White
Clover |
many |
3 |
|
Tripleurospermum inodorum |
Scentless Mayweed |
few |
1 |
|
Tussilago farfara |
Colt’s-foot |
few |
1 |
|
Ulex
europaeus |
Gorse |
several |
2 |
|
Urtica dioica |
Stinging Nettle |
20% |
8 |
|
Veronica chamaedrys |
Germander Speedwell |
few |
1 |
|
Veronica serpyllifolia |
Thyme-leaved Speedwell |
few |
1 |
|
Vicia cracca |
Tufted
Vetch |
2% |
5 |
|
Vicia hirsuta |
Hairy
Tare |
few |
1 |
|
Vicia sativa |
Common
Vetch |
<1% |
4 |
|
Viola arvensis |
Field
Pansy |
several |
2 |
|
|
|
|
|
|
NON-FLOWERING PLANTS |
|
|
|
|
Equisetum arvense |
Field
Horsetail |
<1% |
4 |
|
Pteridium aquilinum |
Bracken |
1% |
5 |
|
|
|
|
|
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CHAPTER
6
REPORT ON BUTTERFLIES FOR 2007
Recorder Sue Proudley
Although no butterflies
were recorded at Moor Green during February 2007 the warm spring brought out
several butterflies in March and April. The first butterflies to be recorded
were 6 Brimstones, 4 Peacocks, a Small Tortoiseshell, Red Admiral and
Comma on 8th March.
In April Brimstone numbers
swelled to 23, 20 Orange Tips, 16 Peacocks, 10 Speckled Woods, 7 Commas, 6
Red Admirals as well as 2 Holly Blues and a Green Hairstreak promised a
better butterfly year.
In May 19 Brimstones were
recorded but other butterfly sightings were disappointing. There were 6
Peacocks and Commas, 4 Whites and a single Holly Blue and Green
Hairstreak.
The summer months showed a
sharp decline in the normally common grassland butterflies. Meadow Brown
numbers recorded only 30, Gatekeepers 32 and Ringlets 9. Speckled Woods
fared better with 25 recorded in July, 28 in August, 18 in September and 16
in October.
A few Small, Essex and
Large Skippers were recorded in June, July and August.
2 Common Blues were seen in
June but no Small Coppers or Small Heaths were sighted.
Red Admirals and Commas
were seen throughout the season
3 Marbled Whites were found
in July and a single Grayling in September.
One Painted Lady visited in
July and was not recorded again. There were no sightings of Clouded Yellows
or any other unusual visitors.
The last butterfly recorded
was a Red Admiral on 23rd October.
The list of species
observed on the reserve in 2007 is as follows:
|
Small Skipper |
Large White |
Green Hairstreak |
Red Admiral |
Comma |
Gatekeeper |
|
Essex Skipper |
Small White |
Purple Hairstreak |
Painted Lady |
Marbled White |
Meadow Brown |
|
Large Skipper |
Green-veined White |
Common Blue |
Small Tortoiseshell |
Grayling |
Ringlet |
|
Brimstone |
Orange Tip |
Holly Blue |
Peacock |
Speckled Wood |
|
Number
of Species 23
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 2007:
|
K and P Crick
R Horland
B and R McCartney
A B |
A Moreton
M Mitchell
M N C
J G and D B |
J E Warren
C Wolfe
J and R Westmacott
D J B |
S A and S F Farmer
I H Brown
C Rose |
Sue Proudley may be contacted on tel: 01252
875536 or
By e-mail: c.proudley(at)btopenworld.com
| |
 |
MOOR GREEN BUTTERFLIES |
 |
|
|
Recorded numbers Mar -
Oct 2007 |
MAR |
APR |
MAY |
JUN |
JUL |
AUG |
SEPT |
OCT |
|
Small Skipper |
(Thymelicus sylvestris) |
|
|
|
7 |
3 |
1 |
|
|
|
Essex Skipper |
(Thymelicus lineola) |
|
|
|
5 |
3 |
3 |
|
|
|
Large Skipper |
(Ochiodes venata) |
|
|
|
1 |
4 |
|
|
|
|
Clouded Yellow |
(Colias crocea) |
|
|
|
|
|
|
|
|
|
Brimstone |
(Gonepteryx rhamni) |
6 |
23 |
19 |
1 |
1 |
1 |
|
2 |
|
Large White |
(Pieris brassicae) |
|
1 |
1 |
5 |
9 |
|
2 |
1 |
|
Small White |
(Pieris rapae) |
|
2 |
2 |
|
5 |
1 |
2 |
|
|
Green-veined White |
(Pieris napi) |
|
|
1 |
|
4 |
4 |
2 |
|
|
Orange tip |
(Anthocharis
cardamines) |
|
20 |
|
|
|
|
|
|
|
Green Hairstreak |
(Callophrys rubi) |
|
1 |
1 |
|
|
|
|
|
|
Purple Hairstreak |
(Quercusia guercus) |
|
|
|
|
2 |
|
|
|
|
Small Copper |
(Lycaena phlaeas) |
|
|
|
|
|
|
|
|
|
Common Blue |
(Polyommatus Icarus) |
|
|
|
2 |
|
|
|
|
|
Holly Blue |
(Celastrina argiolus) |
|
2 |
1 |
|
2 |
2 |
|
|
|
Red Admiral |
(Vanessa atalanta) |
1 |
6 |
|
10 |
14 |
1 |
2 |
1 |
|
Painted Lady |
(Cynthia cardui) |
|
|
|
|
1 |
|
|
|
|
Small Tortoiseshell |
(Aglais urticae) |
1 |
1 |
|
|
2 |
|
|
|
|
Peacock |
(lnachis io) |
4 |
16 |
6 |
|
2 |
|
1 |
|
|
Comma |
(Polygonia c-album) |
1 |
7 |
|
3 |
10 |
1 |
1 |
|
|
Speckled Wood |
(Pararge aegeria) |
|
10 |
6 |
2 |
25 |
28 |
18 |
16 |
|
Grayling |
(Hipparchia semele) |
|
|
|
|
|
|
1 |
|
|
Gatekeeper |
(Pyonia tithonus) |
|
|
|
|
32 |
15 |
|
|
|
Meadow Brown |
(Maniola jurtina) |
|
|
|
30 |
10 |
4 |
2 |
|
|
Small Heath |
(Coenonympha pamphilus) |
|
|
|
|
|
|
|
|
|
Marbled White |
(Melanargia galathea) |
|
|
|
|
3 |
|
|
|
|
Ringlet |
(Aphantopus hyperantus) |
|
|
|
3 |
9 |
|
|
|
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CHAPTER
7
REPORT ON DRAGONFLIES AND DAMSELFLIES FOR 2007
Ken
Crick
The data collection
protocol employed over the last two years was adhered to for the 2007
season. The winter was mild and the spring season started early. The first
species to show was the Large Red Damselfly about 1.5 miles from the reserve
on the 15th April. I found one exuvia for this species on the
reserve on the 18th April and by the 28th copulating
pairs was observed over Colebrook Lake North. The same day produced 38
Common Blue Damselflies, 15 Blue-tailed Damselflies and 88 Banded
Demoiselles, with the exuvia of three Red – eyed Damselflies found in the
emergent vegetation of the northern corner of Colebrook Lake North.
The unsettled conditions
of May and June, with some local flooding in June, made the collection of
exuvia extremely problematic. Numbers on the wing were low across all the
species of both Dragonfly and Damselfly. Weather conditions were generally
poor for observing Odonata and exuvia numbers were also low.
The absence of any shallow
open water in the scrapes, in front of Grove hide, now completely covered by
dense vegetation, undoubtedly contributed to the failure of last years new
arrivals Keeled Skimmer & Black Darter to show.
Data for this year was
collected over 15 site visits resulting in records for only 14 species.
Two of these records were from the sighting of single
individuals; a further record resulted from only two sightings. Despite the
poor showing on the wing and overall numbers of exuvia being down, 9 species
of exuvia were recovered from a very limited area of marginal vegetation,
one more species than last year.
I was grateful for the
digital image sent in by Christine Wolfe of a Brown Hawker with only three
wings, seen by her at Colebrook Lake North on the 19 June. A digital image
always adds credence to unusual observations.
ODONATA CHECKLIST
2007
DAMSELFLIES Zygoptera
|
Species |
Date of
maximum count |
Max count |
Life cycle
confirmation Exuvia |
Observed Flight period |
|
Large Red
Pyrrhosorna nymphala |
28 April & 22 May |
12 |
Yes |
18 April
to
20 June |
|
Azure
Coenagrion puellao |
22 May |
18 |
Yes |
22 May
to
19 July |
|
Common Blue
Enallagama cyathigerum |
1 June |
815 |
Yes |
28 April
to
23 October |
|
Banded Demoiselle
Caloperyx splendens |
22 May |
119 |
No* |
28 April
to
13 September |
|
Blue-tailed
Ischnura elegans |
19 July |
59 |
Yes |
28 April
to
17 August |
|
Red-eyed
Erythromma najas |
8 August |
39 |
Yes |
28 April
to
13 September |
*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 |
22 May |
1 |
No |
22 May |
|
Black-tailed Skimmer Ortheirum
cancellatum |
22 May |
39 |
Yes |
3 June
to
10 Sept. |
|
Four-spotted Chaser Libellula
guadrimaculata |
22 May |
5 |
Yes |
13 May
to
19 July |
|
Emperor
Anax Imperator |
22 May & 20 June |
2 |
No |
13 June
to
15 July |
|
Golden-ringed
Cordulegaster boltonii |
Not observed this year |
|
|
|
|
Common Darter
Sympetrum striolatum |
13 September |
30 |
Yes |
19 July
to
10 Sept. |
|
Southern Hawker
Aeshna cyanea |
Not observed this year |
|
|
|
|
Brown Hawker
Aeshna grandis |
19 July & 8 August |
14 |
No |
19 July |
|
Migrant Hawker
Aeshna mixta |
13 September |
23 |
Yes |
19 July.
to
10 Sept. |
|
Ruddy Darter
Sympetrum sanguineum |
4 July |
3 |
No |
8 Aug.
to
10 Sept. |
|
Keeled Skimmer
Orthetrum coerulescens |
Not observed this year |
|
|
|
|
Black Darter
Sympetrum danae |
Not observed this year |
|
|
|
|
Broad-bodied Chaser
Libellula Depressa |
Not observed this year |
|
|
|
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CHAPTER
8
REPTILE REPORT FOR 2007
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;
b) one sheet on the north shore of Grove Lake (two sheets having been lost
since the previous year);
• casual reports of
sightings anywhere on the reserve.
Regular inspections
Twelve sheet-inspection
visits were made between April and September. All seven sheets were checked
each time. Once again, the majority of the visits produced no sightings.
The remainder found individual snakes under various tins. The results are
summarised in the following table:
Summary of Surveys of Reptile Basking Tins
|
2002 |
2003 |
2004 |
2005 |
2006 |
2007 |
| Site visits
made |
11 |
14 |
15 |
16 |
14 |
12 |
| Total
tin-inspections |
93 |
140 |
150 |
144 |
126 |
84 |
| Total grass
snakes (or skins) seen |
6 |
14 |
15 |
13 |
7 |
7 |
| Total adders
seen |
0 |
0 |
3 |
4 |
0 |
3 |
| Snake
sightings per tin-inspection |
0.06 |
0.10 |
0.12 |
0.12 |
0.06 |
0.12 |
The overall ‘sighting rate’
is back to the level typical of 2003-2005, an increase from the poor showing
of 2006. However, the loss of two sheets on the north shore of Grove Lake
means that the year-to-year comparison is not on a strictly ‘like-for-like’
basis. The missing sheets rarely had snakes anyway, so their loss decreases
the denominator of the ‘sighting rate’ while having a smaller effect on the
numerator. Nevertheless, it is pleasing to see adders again after the zero
count in 2006. These were all seen very close to the hibernaculum (as,
indeed, were most of the grass snakes). This indicates that the barn owl
box was probably not responsible for the low number of sightings in 2006, as
had been feared.
Casual reports
Only five reptiles (all
grass snakes) were reported, similar to the four reported in 2006.
Summary
The number of reptiles seen
in 2007 indicates a partial recovery from the very low 2006 figure. In 2008
more sheets will be installed, to make up for those lost over the past
couple of years.
I am grateful
to those (Bruce Archer, Ken Crick and MLP) who reported seeing reptiles.
Please take the trouble to note your sightings on the forms in the hides.
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CHAPTER
9
REPORT ON NESTBOXES 2007
Bruce
Archer
Forty-eight
nest boxes were monitored between 13th March and 23rd
May this year; 6 of these are on the Manor Farm site (new workings), the
remaining 42 being on the Reserve and along the bridleway. 31 are woodcrete
tit boxes, of which 29 were occupied, 15 are large wooden boxes, of which 9
were used by nesting birds – Grey Squirrels occupy some of these, and 2 are
open-fronted boxes neither of which were used this year. The attached table
shows data for each nest and the statically analysis of the results with the
survival rates for each species.
The mild
April, followed by cooler and wet whether from May had an impact on the
survival of young, so overall it was not a particularly good year. A total
of 308 eggs were laid in the boxes being monitored and 213 birds left the
nests.
Blue Tit
The mild and
dry April meant that Tits got off to a good start. Eleven boxes were
occupied by Blue Tits: first egg date was between 3rd and 23rd
of April. The clutch sizes were between 3 and 11 eggs - a total of 98 in
all. 77 young hatched, with one clutch being predated during laying,
probably by Grey Squirrels. 10 broods of between 5 and 9 young were
successfully hatched. Food supplies must have been good, because 100% of
young appear to have fledged this year. First fledging was on 16th
May with 5 of the 11 nests fledging on 22nd May. The productivity
was 6.9 young per nest, with 78% of eggs laid surviving to fledged young.
One Blue Tit laid an egg in a Great Tit nest which was fostered and fledged
successfully – it was seen in the nest with 8 young Great Tits a few days
before fledging. Another box that seemed to have been initially occupied by
Blue Tits was taken over by Great Tits suggesting that there was competition
for nest boxes. Blue Tits also occupied at least 2 bat boxes and built a
nest in one of the lifebelt stands around Horseshoe Lake.
Great Tit
Seventeen
boxes were used by Great Tits, the first egg date was between the 4th
and 19th April, with a total of 155 eggs being laid with clutch
sizes between 4 and 13. Two clutches failed: one of 4 eggs appeared to have
been predated by Squirrels during laying and a clutch of 11 eggs was
deserted during incubation – probably because of death of the parent. 110
young hatched between 27th April and 6th May, of these
97 fledged; one clutch of 8 was deserted. All fledging was during an 8 day
period between 15th and 22nd May. One pair of Great
Tits chose to nest and raise young in the leaflet holder on Grove Hide!
Mandarin
Duck
Five of the
large wooden boxes were used by Mandarin Ducks this year to lay 41 eggs and
produced 36 young. Because, like all ducks, Mandarin young leave the nest
upon hatching, there is no means of knowing how many survive to fledge.
First egg dates were between 19th March and 22nd
April. Hatching of 36 young was confirmed from 4 boxes between 24th
April and 24th May; one was probably taken over by Squirrels.
Many of the large boxes not used by birds showed signs of Squirrel
occupation. One box was contested by Stock Doves; the initial Stock Dove
clutch of 2 eggs disappeared, probably taken by Squirrels. Mandarin then
started to lay; Stock Doves then laid another 2 eggs with the Mandarin eggs,
but these eggs disappeared and the Mandarin hatched 9 eggs. There is an
additional large wooden box on one of the five Oaks on the spit in the new
lake on the Manor Farm site which was not monitored, but a late brood of 7
young Mandarin were seen in that area with a female on 30th July.
The number of Mandarin eggs recorded this year is considerably lower than in
previous years, but the total count of young is not too different.
Stock Dove
Stock Doves
lay only two eggs in a nest, but can nest from February until October; so
the monitoring through spring was inevitably incomplete. Seven nesting
attempts in 6 different boxes were monitored. The laying date was between
26thFeberuary and 18th April for the 5 nests where a
date could be determined. Seven of the 14 eggs laid hatched and just 3 young
fledged – all on 22nd May. Four eggs were lost because of
competition with Mandarins, and 3 were taken, probably by Squirrels. Four
young were deserted and found dead in the nest, 2 being half grown. A pair
of Stock Doves nested in the Barn Owl box north of Colebrook Lake – 2 eggs
were present on 6th June.
Barn Owl
The Barn Owl
boxes were checked on 6th June by a licensed inspector. The box
by Colebrook Lake was in use by Stock Doves with 2 eggs. The Manor Farm (new
workings) box was occupied by a pair of Barn Owls with 4 young. A visit to
ring the young in early July found only 3 well grown young. Because it was a
“vole year” with plentiful food supplies, many cases of second broods later
in the summer occurred, but a check of the boxes in September confirmed that
there were no second broods at Moor Green Lakes. This is the first breeding
on the site since 1997.
Kestrel
Kestrels
attempted to breed in the top section of the Barn Owl box on the Manor Farm
site. One deserted egg was found on the 6th June visit, and the
remains of two more eggs under the box.
|
|
|
Eggs |
Hatched |
Fledged |
|
Box No. |
Species |
First |
Max |
First |
Max |
First |
Max |
|
|
|
|
|
|
|
|
|
|
02 |
Blue Tit |
03-Apr-07 |
9 |
27-Apr-07 |
9 |
16-May-07 |
9 |
|
03 |
Blue Tit |
08-Apr-07 |
11 |
02-May-07 |
8 |
21-May-07 |
8 |
|
05 |
Blue Tit |
14-Apr-07 |
10 |
07-May-07 |
9 |
22-May-07 |
9 |
|
06 |
Blue Tit |
18-Apr-07 |
9 |
05-May-07 |
8 |
23-May-07 |
8 |
|
12 |
Blue Tit |
13-Apr-07 |
8 |
02-May-07 |
5 |
21-May-07 |
5 |
|
34 |
Blue Tit |
12-Apr-07 |
10 |
08-May-07 |
7 |
22-May-07 |
7 |
|
38 |
Blue Tit |
23-Apr-07 |
3 |
|
|
|
|
|
43 |
Blue Tit |
05-Apr-07 |
9 |
27-Apr-07 |
5 |
16-May-07 |
5 |
|
45 |
Blue Tit |
19-Apr-07 |
9 |
07-May-07 |
9 |
22-May-07 |
9 |
|
46 |
Blue Tit |
16-Apr-07 |
8 |
07-May-07 |
8 |
22-May-07 |
8 |
|
47 |
Blue Tit |
10-Apr-07 |
11 |
03-May-07 |
8 |
22-May-07 |
8 |
|
26* |
Blue Tit |
|
1 |
06-May-07 |
1 |
22-May-07 |
1 |
|
|
|
|
|
|
|
|
|
|
Blue Tit |
Average |
12-Apr-07 |
8.8 |
03-May-07 |
7.6 |
20-May-07 |
7.6 |
|
|
Standard Deviation |
5.8 |
2.1 |
3.9 |
1.4 |
2.4 |
1.4 |
|
11 |
Total |
|
98 |
|
77 |
|
77 |
|
|
Survival |
Egg/Pulli |
78.6% |
Pulli/Fledge |
100.0% |
Egg/Fledge |
78.6% |
|
|
|
|
|
|
|
|
|
|
01 |
Great Tit |
13-Apr-07 |
8 |
01-May-07 |
8 |
|
|
|
04 |
Great Tit |
16-Apr-07 |
13 |
06-May-07 |
8 |
22-May-07 |
8 |
|
07 |
Great Tit |
12-Apr-07 |
11 |
01-May-07 |
8 |
18-May-07 |
8 |
|
08 |
Great Tit |
15-Apr-07 |
4 |
|
|
|
|
|
09 |
Great Tit |
14-Apr-07 |
7 |
01-May-07 |
6 |
19-May-07 |
6 |
|
10 |
Great Tit |
09-Apr-07 |
10 |
01-May-07 |
8 |
19-May-07 |
8 |
|
13 |
Great Tit |
15-Apr-07 |
8 |
01-May-07 |
8 |
19-May-07 |
8 |
|
16 |
Great Tit |
07-Apr-07 |
7 |
27-Apr-07 |
7 |
15-May-07 |
7 |
|
24 |
Great Tit |
17-Apr-07 |
10 |
06-May-07 |
7 |
22-May-07 |
7 |
|
25 |
Great Tit |
11-Apr-07 |
7 |
01-May-07 |
5 |
19-May-07 |
5 |
|
26 |
Great Tit |
11-Apr-07 |
9 |
06-May-07 |
8 |
22-May-07 |
8 |
|
27 |
Great Tit |
13-Apr-07 |
12 |
06-May-07 |
9 |
22-May-07 |
9 |
|
29 |
Great Tit |
19-Apr-07 |
8 |
06-May-07 |
3 |
22-May-07 |
3 |
|
31 |
Great Tit |
16-Apr-07 |
12 |
06-May-07 |
9 |
22-May-07 |
4 |
|
33 |
Great Tit |
14-Apr-07 |
9 |
03-May-07 |
9 |
21-May-07 |
9 |
|
36 |
Great Tit |
11-Apr-07 |
9 |
03-May-07 |
7 |
21-May-07 |
7 |
|
40 |
Great Tit |
04-Apr-07 |
11 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Great Tit |
Average |
12-Apr-07 |
9.1 |
03-May-07 |
7.3 |
20-May-07 |
6.9 |
|
|
Standard Deviation |
3.6 |
2.2 |
2.8 |
1.6 |
2.0 |
1.8 |
|
17 |
Total |
|
155 |
|
110 |
|
97 |
|
|
Survival |
Egg/Pulli |
71.0% |
Pulli/Fledge |
88.2% |
Egg/Fledge |
62.6% |
|
|
|
|
|
|
|
|
|
|
15 |
Mandarin Duck |
26-Mar-07 |
9 |
24-Apr-07 |
7 |
|
|
|
17 |
Mandarin Duck |
20-Mar-07 |
2 |
|
|
|
|
|
20 |
Mandarin Duck |
22-Apr-07 |
9 |
24-May-07 |
9 |
|
|
|
21 |
Mandarin Duck |
19-Mar-07 |
11 |
05-May-07 |
11 |
|
|
|
39 |
Mandarin Duck |
22-Mar-07 |
10 |
09-May-07 |
9 |
|
|
|
|
|
|
|
|
|
|
|
|
Mandarin Duck |
Average |
28-Mar-07 |
8.2 |
08-May-07 |
9.0 |
|
|
|
|
Standard Deviation |
12.7 |
3.2 |
10.7 |
1.4 |
|
|
|
5 |
Total |
|
41 |
|
36 |
|
|
|
|
Survival |
Egg/Pulli |
87.8% |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
11 |
Stock Dove |
06-Apr-07 |
2 |
28-Apr-07 |
1 |
22-May-07 |
1 |
|
20 |
Stock Dove |
07-Apr-07 |
2 |
|
|
|
|
|
20 |
Stock Dove |
|
2 |
|
|
|
|
|
23 |
Stock Dove |
26-Feb-07 |
2 |
20-Mar-07 |
2 |
|
|
|
23 |
Stock Dove |
16-Apr-07 |
2 |
10-May-07 |
2 |
22-May-07 |
2 |
|
48 |
Stock Dove |
|
2 |
|
|
|
|
|
50 |
Stock Dove |
12-Apr-07 |
2 |
04-May-07 |
2 |
|
|
|
|
|
|
|
|
|
|
|
|
Stock Dove |
Average |
01-Apr-07 |
2.0 |
22-Apr-07 |
1.8 |
22-May-07 |
1.5 |
|
|
Standard Deviation |
17.7 |
0.0 |
19.9 |
0.4 |
0.0 |
0.5 |
|
7 |
Total |
|
14 |
|
7 |
|
3 |
|
|
Survival |
Egg/Pulli |
50.0% |
Pulli/Fledge |
42.9% |
Egg/Fledge |
21.4% |
|
|
|
|
|
|
|
|
|
|
40 |
Totals |
|
308 |
|
230 |
|
177 |
|
|
Survival |
Egg/Pulli |
74.7% |
Pulli/Fledge |
77.0% |
Egg/Fledge |
57.5% |
|
* This egg was laid in a Great Tit
nest and fostered - while it is counted in the totals, it is not
included in the statistical analysis. |
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CHAPTER 10
BUMBLEBEE SURVEYS DURING 2007
Steve
Farmer
Surveys of bumblebees were
conducted on Manor Farm, Moor Green Lakes and Horseshoe Lake during 2007.
These were designed to establish the species present on these sites and
their relative importance for foraging bumblebees.
The sites surveyed were (a)
the Manor Farm river path from Longwater Road eastwards; the wildflower
meadows on (b) the west side and (c) the north side of Colebrook Lake North;
the small wildflower meadow on (d) the north west side of Grove Lake near
Grove Island and (e) the north east corner of Grove Lake; (f) the west side,
(g) the north side and (h) the east side of Horseshoe Lake.
TABLE A.
Number of bumblebees
seen during the surveys
|
Date
2007 |
Site |
Bombus pascuorum |
Bombus lapidarius |
Bombus
pratorum |
Bombus terrestris |
Bombus
lucorum |
Bombus hortorum |
Bombus vestalis |
Total |
|
20/05 |
Manor Farm |
6 |
|
6 |
2 |
4 |
|
|
18 |
|
07/06 |
Manor Farm |
6 |
|
3 |
11 |
18 |
4 |
|
42 |
|
04/07 |
Manor Farm |
|
|
|
|
11 |
2 |
|
13 |
|
18/07 |
Manor Farm |
1 |
|
|
3 |
9 |
|
|
13 |
|
01/08 |
Manor Farm |
9 |
|
|
|
2 |
1 |
|
12 |
|
07/08 |
CLN (West) |
45 |
|
|
1 |
|
1 |
|
47 |
|
07/08 |
CLN (North) |
30 |
14 |
|
4 |
|
1 |
|
49 |
|
07/08 |
Grove (NW) |
28 |
|
|
|
1 |
1 |
|
30 |
|
07/08 |
Grove (NE) |
16 |
|
|
1 |
|
1 |
|
18 |
|
19/07 |
Horseshoe (W) |
18 |
|
|
|
|
|
|
18 |
|
19/07 |
Horseshoe (N) |
4 |
|
|
|
1 |
|
|
5 |
|
19/07 |
Horseshoe (E) |
39 |
3 |
|
2 |
1 |
1 |
|
46 |
|
05/08 |
Horseshoe (W) |
40 |
|
|
2 |
|
|
|
42 |
|
05/08 |
Horseshoe (N) |
5 |
|
|
|
|
|
|
5 |
|
05/08 |
Horseshoe (E) |
28 |
1 |
|
2 |
3 |
1 |
|
35 |
|
Totals for 20 May to
7 August 2007. |
275 |
18 |
9 |
28 |
49 |
14 |
0 |
393 |
The main surveys were
conducted between 1 and 7 August, which was towards the end of the nesting
season. Some partial surveys were carried out on earlier dates. The results
of most of these surveys are given in Table A. There were some additional
casual observations on other dates.
Bumblebees had rather mixed
fortunes during 2007. Most queens emerged from hibernation early and
successfully established nests in response to a fine, dry, warm April.
However wet and cool weather during the early summer resulted in some of
these nests being flooded out and many foraging workers being killed in
heavy rain. Continued cool and damp conditions caused many of the remaining
nests to finish early. There was a rapid decline in the number of workers
by mid August.
A short summary follows for
each of the 7 species of bumblebee recorded during the surveys.
Bombus
pascuorum. (Common
carder bumblebee).
B.pascuorum has a long
nesting cycle and the number of workers only builds up slowly. It was by far
the most common bumblebee seen during these surveys and was still present in
good numbers in early August.
Bombus
lapidarius. (Red-tailed
bumblebee).
Fourteen males were seen on
CLN (north) on 7 August all feeding on black knapweed. There was probably a
mature nest in the vicinity.
Bombus pratorum. (Early-nesting
bumblebee).
This species builds its
nest early and has a short nesting cycle. Two males were seen on Manor Farm
on 20 May and a new queen on 7 June. However two workers were seen feeding
on white bryony on CLN (west) 18 July and two more on 19 August. These were
probably from a second generation nest.
Bombus
terrestris. (Buff-tailed
bumblebee).
This species was one of the
first to emerge from hibernation. One queen was seen near Colebrook Hide and
another near Grove Hide on 11 March. It usually has a long period of
activity, even having a second complete nesting cycle in some summers.
However it was seen in only fairly small numbers from July onwards. A new
queen was seen on Grove (NE) on 7 August.
Bombus lucorum.
(White-tailed bumblebee).
This species emerges from
hibernation early and the number of workers normally builds up throughout
June and July until a large colony has been produced. The observations
showed good numbers of workers on Manor Farm till mid-July but only small
numbers thereafter
Bombus hortorum.
(Garden bumblebee).
This species has a short
nesting cycle and the size of nest is usually small. This year it was only
seen in small numbers. A few workers were seen in August.
Bombus vestalis.
(formerly known
as Psithyrus vestalis). (No
common name).
This is a "cuckoo"
bumblebee that is parasitic in the nests of B.terrestris. One queen was
seen on Manor Farm on 14 April. Others were seen in the local area during
the spring.
Bumblebee preferences
for wildflowers.
The results of the surveys
were analysed to establish which of the flowers growing on the Reserve were
the most important for the bumblebees. Table B shows the number of each
species of bumblebee seen foraging on different types of wildflower. These
are the results for all surveys combined. The bumblebees were recorded on
17 kinds of wildflower, but most were observed on just 8 species which were
available between May and early August.
TABLE B.
Number of each species
of bumblebee seen foraging on different types of wildflower.
|
Flower |
Bombus pascuorum |
Bombus lapidarius |
Bombus
pratorum |
Bombus terrestris |
Bombus
lucorum |
Bombus hortorum |
Bombus vestalis |
Total |
|
birdsfoot trefoil |
47 |
3 |
|
1 |
|
|
|
51 |
|
black knapweed |
31 |
15 |
|
3 |
1 |
1 |
|
51 |
|
bramble |
15 |
|
9 |
12 |
31 |
6 |
|
73 |
|
common hempnettle |
8 |
|
|
|
|
1 |
|
9 |
|
Himalayan balsam |
2 |
|
|
3 |
9 |
1 |
|
15 |
|
meadow vetchling |
9 |
|
|
|
|
|
|
9 |
|
red clover |
8 |
|
|
|
|
1 |
|
9 |
|
tufted vetch |
143 |
|
|
5 |
4 |
1 |
|
153 |
|
other * |
12 |
|
|
4 |
4 |
3 |
|
23 |
|
Total |
275 |
18 |
9 |
28 |
49 |
14 |
0 |
393 |
*Other
includes:- betony, broom, creeping thistle, hairy tare, meadow cranesbill,
spear thistle, St John’s wort, toadflax, and white clover.
B. pascuorum was found
mainly on birdsfoot trefoil, black knapweed and especially tufted vetch. B.lapidarius
was found mainly on black knapweed. The few B.pratorum were found on bramble
early in the season. B.terrestris and B.lucorum were also found mainly on
bramble but also on Himalayan balsam. The few B.hortorum were found on
bramble mainly. The most interesting change from the previous year was the
large number of B.pascuorum found on tufted vetch, which was abundant this
year. Himalayan balsam, which did not feature in the previous survey, proved
to be a fairly important flower for bumblebees to forage on.
Additional reading:-
Benton, T. (2000). The
Bumblebees of Essex. Lopinga Books.
Benton, T. (2006). Bumblebees. Collins.
Edwards, M. and Jenner, M.
(2005). Field Guide to the Bumblebees of Great Britain & Ireland. Ocelli.
Prys-Jones, O. and Corbet,
S. (1987). Bumblebees. Naturalists' Handbook 6, Richmond Publishing
Co. Ltd.
Societies:-
Bees, Wasps and Ants
Recording Society. (BWARS).
http://www.bwars.com
Bumblebee Conservation
Trust. (BBCT).
http://www.bumblebeeconservationtrust.co.uk
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CHAPTER 11
REPORT ON MOTHS FOR 2007
Recorder Colin Proudley
The first moth recording took place at Moor
Green Lakes in 1995. Des Sussex ran a single trap on two evenings, once in
June and again in July. The total species caught was 62. The trap was
located on the North West corner of the reserve.
In 2007, after a gap of twelve years, I ran two Skinner traps, the first in
March with Steve Bailey, and again in April, May, July and October, this
time with Richard Eagling, a fellow moth enthusiast. Once again the location
was on the North West corner of the reserve. One trap was located under the
Oaks that border Moor Green Farm boundary fence at Colebrook North. The
second trap was located on the perimeter path at the entrance gate to
Colebrook North. I had intended to do more, but Richard and I were defeated
by the atrocious summer weather.
The total moth species count for 2007 was 78, comprising 62 Macro moths plus
16 Micro moths. The total moth species identified at Moor Green Lakes
reserve to date is 119. Of this total there were no rare or Red Data Book
species but there are 13 species which qualify as Local. (This means moths
only recorded from 101- 300 10km squares in Great Britain since 1st January
1960.)
The complete list of moths follows this report.
The number in the first column is the one allocated by Bradley (2000). The
Check List of Lepidoptera Recorded from the British Isles. The third column
shows rarity Status again as allocated by Bradley.
Richard and I intend to continue trapping in 2008 and onwards. This will
enable us to get a true picture of the moths at Moor Green Lakes.
All moths caught were released after being identified. Anyone interested in
joining us, please contact Colin Proudley. Tel: 01252 875536. You will be
most welcome, I am sure you will find it very interesting.
Moor Green Moths
|
Ref. No. |
Species |
Status |
1995 |
2007 |
2008 |
|
14 |
Ghost
Moth |
|
X |
|
|
|
17 |
Common
Swift |
|
|
X |
|
|
937 |
Agapeta hamana |
|
|
X |
|
|
998 |
Epiphyas postvittana |
|
|
X |
|
|
1033 |
Green
Oak Tortrix |
|
|
X |
|
|
1113 |
Eudemis profundana |
|
|
X |
|
|
1174 |
Epiblema cynosbatella |
|
|
X |
|
|
1205 |
Spilonata ocellana |
|
|
X |
|
|
1260 |
Cydia
splendana |
|
|
X |
|
|
1293 |
Chrysoteuchia culmella |
|
|
X |
|
|
1334 |
Scoparia ambigualis |
|
|
X |
|
|
1348 |
Ringed
China Mark |
|
|
X |
|
|
1376 |
Small
Magpie |
|
|
X |
|
|
1392 |
Udea
olivalis |
|
|
X |
|
|
1405 |
Mother
of Pearl |
|
X |
X |
|
|
1413 |
Gold
Triangle |
|
|
X |
|
|
1424 |
Endotricha flammealis |
|
|
X |
|
|
1452 |
Phycita roborella |
|
|
X |
|
|
1513 |
Pterophorus pentadactyla |
|
|
X |
|
|
1640 |
Drinker |
|
X |
X |
|
|
1646 |
Oak
Hook Tip |
|
X |
|
|
|
1653 |
Buff
Arches |
|
X |
|
|
|
1654 |
Figure
of Eighty |
|
X |
|
|
|
1666 |
Large
Emerald |
|
X |
|
|
|
1667 |
Blotched Emerald |
Local |
X |
|
|
|
1690 |
Small
Blood Vein |
|
X |
|
|
|
1711 |
Treble
Brown Spot |
Local |
X |
|
|
|
1713 |
Riband
Wave |
|
|
|
|
|
1732 |
Shaded
Broad Bar |
|
X |
|
|
|
1738 |
Common
Carpet |
|
X |
|
|
|
1742 |
Yellow
Shell |
|
X |
|
|
|
1745 |
Mallow |
|
|
|
|
|
1754 |
Phoenix |
|
X |
|
|
|
1758 |
Barred
Straw |
|
|
|
|
|
1760 |
Red
Green Carpet |
|
|
|
|
|
1764 |
Common
Marbled Carpet |
|
|
|
|
|
1768 |
Grey
Pine Carpet |
|
|
|
|
|
1776 |
Green
Carpet |
|
|
|
|
|
1794 |
Sharp
Angled Carpet |
Local |
X |
|
|
|
1853 |
Oak
Tree Pug |
|
|
|
|
|
1862 |
Double
Striped Pug |
|
|
|
|
|
1882 |
Small
Seraphim |
Local |
|
|
|
|
1887 |
Clouded Border |
|
X |
|
|
|
1904 |
Scorched Wing |
Local |
|
|
|
|
1906 |
Brimstone Moth |
|
X |
|
|
|
1907 |
Bordered Beauty |
|
|
|
|
|
1915 |
September Thorn |
|
|
|
|
|
1917 |
Early
Thorn |
|
|
|
|
|
1922 |
Swallowtail Moth |
|
X |
|
|
|
1931 |
Peppered Moth |
|
|
|
|
|
1937 |
Willow
Beauty |
|
X |
|
|
|
1941 |
Mottled Beauty |
|
X |
|
|
|
1956 |
Common
Wave |
|
X |
X |
|
|
1961 |
Light
Emerald |
|
X |
X |
|
|
1979 |
Lime
Hawkmoth |
|
X |
|
|
|
1981 |
Poplar
Hawkmoth |
|
X |
X |
|
|
1991 |
Elephant Hawkmoth |
|
X |
X |
|
|
1992 |
Small
Elephant Hawkmoth |
Local |
|
X |
|
|
1994 |
Bug
Tip |
|
X |
|
|
|
1997 |
Sallow
Kitten |
|
X |
|
|
|
2009 |
Maple
Prominent |
Local |
|
X |
|
|
2011 |
Pale
Prominent |
|
|
X |
|
|
2014 |
Marbled Brown |
Local |
X |
X |
|
|
2015 |
Lunar
Marbled Brown |
|
|
X |
|
|
2028 |
Pale
Tussock |
|
|
X |
|
|
2030 |
Yellow
Tail |
|
X |
|
|
|
2037 |
Rosy
Footman |
Local |
X |
|
|
|
2043 |
Orange
Footman |
Local |
|
X |
|
|
2047 |
Scarce
Footman |
Local |
|
X |
|
|
2050 |
Common
Footman |
|
X |
X |
|
|
2061 |
Buff
Ermine |
|
X |
|
|
|
2064 |
Ruby
Tiger |
|
X |
X |
|
|
2087 |
Turnip
Moth |
|
|
X |
|
|
2088 |
Heart
and Club |
|
X |
|
|
|
2089 |
Heart
and Dart |
|
X |
|
|
|
2098 |
The
Flame |
|
X |
X |
|
|
2102 |
Flame
Shoulder |
|
X |
X |
|
|
2107 |
Large
Yellow Underwing |
|
X |
X |
|
|
2109 |
Lesser
Yellow Underwing |
|
|
X |
|
|
2110 |
Broad
Bordered Yellow Underwing |
|
X |
X |
|
|
2118 |
True
Lovers Knot |
|
|
|
|
|
2126 |
Setaceous Hebrew Character |
|
X |
X |
|
|
2128 |
Double
Square Spot |
|
|
|
|
|
2134 |
Square
Spot Rustic |
|
|
X |
|
|
2155 |
Dot
Moth |
|
X |
|
|
|
2157 |
Light
Brocade |
Local |
|
X |
|
|
2182 |
Small
Quaker |
|
|
X |
|
|
2190. |
Hebrew
Character |
|
|
X |
|
|
2193 |
The
Clay |
|
X |
|
|
|
2198 |
Smokey
Wainscot |
|
X |
|
|
|
2199 |
Common
Wainscot |
|
|
X |
|
|
2231 |
Deep
Brown Dart |
|
|
X |
|
|
2232 |
Black
Rustic |
|
|
X |
|
|
2247 |
Merveille Du Jour |
|
|
X |
|
|
2248 |
Brindled Green |
|
|
X |
|
|
2258 |
Chestnut |
|
|
X |
|
|
2259 |
Dark
Chestnut |
|
|
X |
|
|
2270 |
Lunar
Underwing |
|
|
|
|
|
2272 |
Barred
Sallow |
|
|
X |
|
|
2279 |
Sycamore |
Local |
X |
X |
|
|
2284 |
Grey
Dagger |
|
X |
|
|
|
2305 |
Small
Angle Shades |
|
X |
|
|
|
2306 |
Angle
Shades |
|
X |
|
|
|
2318 |
Dunbar |
|
X |
|
|
|
2321 |
Dark
Arches |
|
X |
X |
|
|
2322 |
Light
Arches |
|
X |
|
|
|
2335 |
Slender Brindle |
|
X |
|
|
|
2339 |
Tawny
Marbled Minor |
|
|
X |
|
|
2340 |
Middle
Barred Minor |
|
X |
|
|
|
2343 |
Common
Rustic |
|
|
X |
|
|
2360 |
Ear
Moth |
|
X |
|
|
|
2380 |
Treble
Lines |
|
|
X |
|
|
2381 |
The
Uncertain |
|
X |
|
|
|
2410 |
Marbled White Spot |
|
|
X |
|
|
2442 |
Beautiful Golden Y |
|
X |
|
|
|
2443 |
Plain
Golden Y |
|
X |
|
|
|
2474 |
Straw
Dot |
|
|
X |
|
|
2477 |
The
Snout |
|
X |
X |
|
|
2489 |
Fan
Foot |
|
X |
|
|
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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 2007
LITTLE GREBE
Resident and winter visitor. During the
breeding season four pairs were present rearing at least four young.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
2 |
2 |
1 |
4 |
3 |
2 |
2 |
5 |
8 |
4 |
4 |
3 |
GREAT CRESTED GREBE
Common resident. A maxima of 17 were recorded
on Feb.18th. A total of four pairs were present during the summer and
successfully reared three young (two broods).
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
13 |
17 |
8 |
8 |
8 |
8 |
9 |
14 |
12 |
9 |
15 |
12 |
CORMORANT
Common winter visitor that over-summers in
small numbers. Small numbers roosted on Grove Island during the winter
period.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
43 |
7 |
15 |
6 |
3 |
3 |
0 |
2 |
8 |
19 |
25 |
35 |
LITTLE EGRET
Frequent visitor with increasing frequency. In
the early year 1/3 birds were recorded on 28 dates until Mar.31st. Summer
records were 1, May 13th and 1, Jun.28th (first site records for these
months). From Nov.8th till the year end 1/3 birds were recorded on 24 dates.
GREY HERON
Common resident. A report of a bird on a nest
on the ground in the Grove area was received but breeding could not be
confirmed.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
4 |
2 |
3 |
3 |
3 |
5 |
3 |
3 |
3 |
2 |
2 |
3 |
MUTE SWAN
Common resident and winter visitor. One pair
bred rearing four young.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
40 |
43 |
24 |
- |
14 |
22 |
26 |
14 |
17 |
12 |
30 |
22 |
GREYLAG GOOSE
Common visitor numbers increasing, new
breeder. A maximum of 103 roosted on Sept.16th (JMC) a site record count*
for the second successive year. One pair bred with one young seen in June
(IHB), final success unknown. The first confirmed breeding within the
recording boundary.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
20 |
12 |
6 |
6 |
5 |
5 |
9 |
4 |
103* |
4 |
23 |
24 |
SNOW GOOSE
Resident with numbers sharply declining.
Present in all months but there was no evidence of breeding. In the early
year four birds were present but this declined to three in the late winter
period. How many more years will they grace the site?
CANADA GOOSE
Abundant resident.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
158 |
189 |
156 |
39 |
63 |
72 |
- |
320 |
560 |
97 |
227 |
300 |
BARNACLE GOOSE
Common resident. Breeding was not attempted
for the first time since at least 1989.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
52 |
24 |
2 |
2 |
2 |
0 |
0 |
34 |
39 |
0 |
37 |
37 |
BRENT GOOSE
Scarce visitor. One was briefly on Grove on
Dec.15th (IHB). The fourth site record.
EGYPTIAN GOOSE
Resident in increasing numbers. Four pairs
attempted breeding. First brood seen on Jan.6th. One brood of five
definitely survived. Roosting on the new workings area occurred in the
winter and a maximum count of 108 was recorded on Oct.13th (JMC). A new site
record for the third successive year.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
36 |
9 |
27 |
20 |
8 |
20 |
31 |
70 |
85 |
108* |
103 |
107 |
SHELDUCK
Regular visitor. 1/2 birds were recorded on
five dates between Apr.7th and May 1st. Other records were of 2, May 26th
and Jun.1st and 3 immatures, Aug.25th.
MANDARIN
Common summer visitor. Resident in small
numbers. At least six pairs bred successfully including use of nest boxes
(four broods totalling 36 from five boxes). Young were seen from Jul.30th.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
5 |
8 |
7 |
5 |
9 |
3 |
8 |
12 |
15 |
1 |
4 |
0 |
WIGEON
Very common winter visitor. Birds were
recorded up to Apr.1st and from Sept.7th. One was present on Jun.18th. The
maximum count was of 597 on Jan.20th (JMC) a site record.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
597* |
303 |
224 |
3 |
0 |
1 |
0 |
0 |
35 |
201 |
264 |
478 |
GADWALL
Very common winter visitor that breeds in
small numbers. A minimum of eight males oversummered with up to three
females, with breeding successful. Three birds were successfully fledged
from a brood of eight, a second brood was seen but success was unknown.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
184 |
183 |
80 |
11 |
8 |
9 |
8 |
13 |
20 |
23 |
38 |
148 |
TEAL
Common winter visitor that occasionally
summers. Breeding was not suspected. The maximum count was of 80 on
Jan.20th.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
80 |
32 |
15 |
10 |
0 |
0 |
3 |
22 |
25 |
18 |
70 |
60 |
MALLARD
Common resident and winter visitor. Numbers
are declining.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
86 |
66 |
19 |
- |
30 |
54 |
- |
60 |
35 |
48 |
36 |
46 |
GARGANEY
Infrequent visitor. One female was present on
Aug.11th and 16th (ML, IHB, BMA et al). The recent trend of increased
records is maintained. The ninth and tenth records.
PINTAIL
Regular winter visitor. A good year, recorded
as follows: 1/2 birds generally recorded on 18 dates between Jan.1st and
Feb.25th involving up to 2m and 1f.
SHOVELER
Common winter visitor. Recorded until April
19th and from Jul.17th. The maximum count was 81 on Jan.27th .
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
81 |
12 |
68 |
32 |
0 |
0 |
8 |
4 |
22 |
12 |
21 |
48 |
POCHARD
Common winter visitor, occasional in summer.
Recorded until Apr.5th and from Jun.27th. The maximum was 176 on Sept.16th.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
57 |
41 |
29 |
3 |
0 |
1 |
4 |
4 |
176 |
63 |
52 |
91 |
TUFTED DUCK
Abundant resident and winter visitor. During
the summer a minimum of eight broods totalling a minimum of 26 young were
raised. Another successful breeding season and continues an upward trend.
The maximum count was of 216 on Dec.14th.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
210 |
160 |
190 |
88 |
28 |
26 |
55 |
185 |
176 |
117 |
109 |
216 |
GOLDENEYE
Winter visitor in increasing numbers. In the
early year birds were recorded until Apr.5th First returns were from
Nov.7th.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
5 |
6 |
4 |
2 |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
3 |
GOOSANDER
Common winter visitor. Birds continued to
roost on the site. The last early year record was on Apr.17th. First returns
were from the relatively early date of Oct.29th.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
30 |
24 |
22 |
4 |
0 |
0 |
0 |
0 |
0 |
7 |
15 |
43 |
RUDDY DUCK
Occasional visitor of annual occurrence. A
good year. Two males (one adult, one imm) were present on Horseshoe lake
from Jan.17th to Feb.17th, with one remaining till Mar.31st. A third bird
unsexed/aged was present on Feb.10th. The only other record was of a male on
May 24th.
RED KITE
Regular visitor, records increasing. Only two
records of singletons on Apr.10th (BMA) and Aug.9th (IHB).
SPARROWHAWK
Common resident. Breeding strongly suspected.
BUZZARD
Very frequent visitor that breeds nearby.
Recorded in all months except June with a maxima of 4 on Sept.24th. There
were records on 43 dates (exactly the same as in 2006!). On Nov.9th one was
seen to take a Moorhen.
KESTREL
Common resident. One pair bred rearing two
young. Another or the same failed in an attempt to nest in the ‘upper
apartment’ of the west owl box.
HOBBY
Common summer visitor. One to three birds were
recorded between Apr.24th and Sept 15th.
PEREGRINE
Frequent visitor of increasing occurrence. A
male was recorded on 14 dates to May 2nd and the same or another male was
present on 8 dates from Aug.19th to the year end. Recorded in all months
except April, June, July and October.
RED LEGGED PARTRIDGE
Formerly bred, with birds in suitable breeding
habitat during the summer. Breeding possible with a pair seen on several
dates in April and May. There were further records from Aug.18th till mid
Sept with three birds on two dates.
PHEASANT
Common resident.
WATER RAIL
Winter visitor. Up to two were recorded until
Mar.22nd and from Oct.26th.
MOORHEN
An abundant resident.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
20 |
30 |
10 |
- |
- |
- |
- |
5 |
16 |
23 |
37 |
26 |
COOT
Abundant resident.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
211 |
156 |
80 |
- |
- |
44 |
- |
124 |
153 |
166 |
190 |
226 |
OYSTERCATCHER
Regular visitor. Four records of singletons,
the first on the early date of Feb.21st (DC), followed by Apr.9th (GR, BMA),
May 12th (IHB) and Jul.24th (BMA). A typical years showing.
AVOCET
Very rare visitor. One on Apr.20th was present
on the reed bed trial area of the new workings from at least 07.00 to 07.45
(NS, BMA, RG). Only the second site record the first being in 1992.
LITTLE RINGED PLOVER
Summer visitor and passage migrant. Recorded
from Mar.16th until Jun.28th. Five pairs were on the site all of which
attempted breeding. Several young broods were seen during late May and June
but only one bird is thought to have survived. The only other record was of
a passage bird on Aug.5th.
RINGED PLOVER
Summer visitor and passage migrant that
formerly bred. Breeding considered unlikely. A single was recorded
intermittently from Mar.12th to May 1st with 3, on Mar.19th. One to two
birds were recorded (on 9 dates) from May 13th to Jun.8th. Eight were
present on May 27th, six remaining till the following day. In autumn records
as follows, 1, Aug.7th, 2, Aug.17th, 1, Aug.24th and 2, Sept.28th.
GOLDEN PLOVER
Regular visitor. In the early winter: 8,
Feb.17th and 20, Feb.20th. In late winter there was a remarkable influx of
birds most probably originating from a large flock wintering in the Theale
area. Records as follows: 1, Sept.5th, 2, Oct.25th, 5, Oct.27th, 70,
Nov.30th, 159, Dec.1st, 100, Dec.3rd, 400, Dec.8th, 630, Dec.9th (CRG) and
480, Dec.10th. The count on Dec.9th was easily a site record (cf 40 in
2006!).
LAPWING
Common resident and winter visitor.
Approximately eleven pairs attempted to breed rearing a total of three young
from two broods.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
550 |
900 |
50 |
16 |
22 |
50 |
196 |
235 |
400 |
343 |
300 |
400 |
KNOT
Very rare visitor. One in partial summer
plumage was located on the works at 09.50 (initially in poor visibility) and
remained until at least mid afternoon (IHB et al). The third site record,
the first being in 1987.
SANDERLING
Irregular visitor. A very good year with
records as follows: 7, May 27th (JBS) and 4, May 28th (NS, BMA et al). The
group on May 27th was the largest recorded for the site. The twelfth and
thirteenth site records.
LITTLE STINT
Irregular visitor. Recorded as follows: 1, May
1st (NS, BMA et al) and 1, Aug.11th to 16th (IHB et al).
CURLEW SANDPIPER
Scarce visitor. The only record was of three
juveniles on the new workings on Sept.23rd (BMA, JMC et al). The fifth site
record and the first since 2001.
DUNLIN
Regular passage migrant. An exceptional year,
the best on record. In the early winter period: 1, Feb.24th. Then in spring
recorded on 16 dates between Mar.19th and May 27th with a maxima of 11 on
May 11th. In autumn recorded on 33 dates (66 bird days) between Jul.17th and
Sept.30th, with a maxima of 4, Sept.3rd. The only other record was of 1,
Nov.24th. Habitat availability on the new workings was the major factor and
several small groups lingered for days and even weeks.
RUFF
Occasional visitor. A good year with records
of two birds both of which stayed for more than one day. A juvenile male was
present Aug.16th to 17th (RMW et al) and a juvenile female from Sept.10th to
25th (BMA et al). The latter is the site record for the longest duration of
stay for the species. Recorded in 11 of the last 16 years.
COMMON SNIPE
Common passage migrant and winter visitor.
Recorded until May.9th and from Aug.7th. A maxima of 32 on Mar.4th.
JACK SNIPE
Regular winter visitor and passage migrant.
The only record was of 1, Oct.27th (IHB).
BLACK TAILED GODWIT
Irregular visitor of increasing occurrence. An
exceptional year with four records totalling 44 birds. Seven spl birds were
present on Colebrook Lake North for 15 minutes on Jul.10th (NS, BMA et al).
Eight spl birds were on the new workings on Aug.7th (RMW, NS, BMA). A
remarkable record of 28 (mostly spl) on the new workings (eastern end) on
Sept.2nd (MM) will if accepted by Berkshire be the largest flock recorded in
the county. Finally, 1, Sept.10th (GR). A continuing trend in records
especially with respect to July. Recorded in each of the last seven years.
WHIMBREL
Regular passage migrant. Two records as
follows: 1, May 1st (BMA) and 4, Jul.27th (BMA, KM, RS). Recorded in each of
the last five years.
CURLEW
Occasional visitor. A good year with four
records: 1, Jul.9th (ML, BMA), 1, Jul.13th (ML), 2, Sept.28th (NS) and 1,
Sept 29th (NS).
SPOTTED REDSHANK
Scarce visitor. A very good year with two
records: 1, Apr.16th on the new workings (MGP) and 1, May 10th (DS, MP). The
eighth and ninth site records.
REDSHANK
Summer visitor and passage migrant. First
returns from Mar.12th. Up to four pairs were present on the reserve and the
new workings. Two pairs bred successfully rearing two young. Summering birds
recorded until Jul.18th. In autumn passage records as follows: 1, Aug.20th,
1, Sept.23rd and 1, Oct.1st. Breeding has at least been attempted in each of
the last 17 years!
GREENSHANK
Regular passage migrant. A very good year. In
spring records of singletons on eight dates between Apr.10th and May 29th.
In autumn, 1/2 birds recorded on 24 dates (38 bird days) between Jul.20th
and Sept.7th. Four birds were present on Aug.11th and five on Aug.12th.
GREEN SANDPIPER
Winter visitor and very common passage
migrant. Recorded on 139 dates throughout the year. Only singletons were
recorded intermittently in the early winter period. Recorded until May 4th
(23 bird days) and from Jun.16th. The maximum count was 8, Aug.26th and
Sept.1st. In late winter 1/3 birds were recorded (total bird days since
Jun.16th, 298).
WOOD SANDPIPER
Occasional visitor of annual occurrence. Two
were present on May 1st (NS, BMA, GR, CRG). Only the second multiple
occurrence, the last also of two in August 1997. Recorded in 12 of the last
15 years and the nineteenth site record of which ten have been in spring.
COMMON SANDPIPER
Common passage migrant. In spring records were
mainly of 1 to 2 birds on 24 dates between Apr.17th and May 21st (max 3,
Apr.20th). Returns were of 1 to 5 birds on 40 dates (71 bird days) from
Jul.4th to Sept.8th.
TURNSTONE
Infrequent visitor. A very good year with
records on four dates, all on the new workings: 2, Jul.20th (BMA), 3,
Jul.27th, with one remaining till Jul.29th (BMA, NS) when it was seen to fly
into Hampshire. Fourteenth and fifteenth site records.
LITTLE GULL
Irregular visitor. Four records: 1, 2nd
winter, Apr.12th (JMC), 4, Apr.13th (NS), 3, Apr.19th (CRG) and 1 adult wpl,
Apr.24th (BMA).
BLACK HEADED GULL
Very common visitor and breeding species.
Approximately 163 pairs (cf 188 in 2006) attempted to breed with occupied
nests. A census from Jun.4th revealed 124 nests with a total of 79 young
ringed. However final success was poor with very few young birds becoming
fully fledged and birds dispersed the site relatively early. Disturbance to
the colony by predators likely for the second successive year. Birds
roosted principally on Grove in the late winter period.
Monthly maxima:
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
100 |
200 |
200 |
245 |
220 |
124 |
140 |
- |
30 |
100 |
150 |
113 |
COMMON GULL
Common winter visitor. The maximum count was
of 60 on Jan.12th. Roosted occasionally in small numbers.
LESSER BLACK BACKED GULL
Very common visitor. Recorded in all months.
Birds continued to roost in large numbers especially during September to
December.
Monthly maxima (principally at roost)
|
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
|
130 |
- |
- |
- |
- |
- |
35 |
510 |
991 |
693 |
512 |
320 |
HERRING GULL
Winter visitor regular in summer, but in
reduced numbers. Roosted in small numbers.
YELLOW LEGGED HERRING GULL
Regular visitor. Recorded as follows:1/4 birds
on four dates between Jan.14th and Jan.29th (at roost); 1/2 birds on 24
dates between Jul.6th and Dec.28th with 3, Jul.15th.
CASPIAN GULL
Scarce visitor. The only record was of 1,
first winter on Nov.17th (IHB). The fifth site record.
GREAT BLACK BACKED GULL
Formerly frequent winter visitor with numbers
of records declining sharply. Four records: 1 ad Jan.10th (BMA), 1 ad,
Jan.12th (BMA), 1 ad, Jan.14th (BMA) and 1, Oct.26th (NS). Consistent with
recent years all records required again for next year!
COMMON TERN
Summer visitor and passage migrant. Recorded
from Apr.11th. Up to 31 birds were present in May and June but only two
pairs showed serious intent to breed. 1/2 nests were seen but deserted after
a few days (cf Black Headed Gull). Recorded until Aug.20th.
ARCTIC TERN
Irregular visitor. The only record was of one
on CLN/Horseshoe lakes on May 4th (BMA). Recorded in each of the last three
years after an absence of seven years.
STOCK DOVE
Common resident. Four nestboxes were occupied,
but only three young were successfully fledged. Maxima 31 on Dec.1st.
WOOD PIGEON
Abundant resident. Maxima 700 on Jan.20th.
COLLARED DOVE
Common resident breeding nearby.
CUCKOO
Summer visitor in declining numbers. A
singing male recorded on eight dates between May 1st and Jun.1st.
BARN OWL
Resident breeder. Recorded from Mar.16th till
Nov.17th. One pair bred successfully in the west box rearing four young. The
first successful breeding since 1997.
LITTLE OWL
Moderately common resident. Birds present in
four/five territories.
TAWNY OWL
Resident. Birds present in at least 2
territories.
SWIFT
Numerous summer visitor. Recorded from
Apr.21st till Aug.18th. A maxima of 150 on May 11th and 19th .
KINGFISHER
Moderately common resident. Two pairs bred
successfully. Recorded in all months.
GREEN WOODPECKER
Common resident.
GREAT SPOTTED WOODPECKER
Common resident.
SKYLARK
Resident and winter visitor. Eight singing
males held territory (cf 5 in 2006). Maximum count was 12 on Mar.24th.
SAND MARTIN
Common summer visitor. Recorded from Apr.24th
(very late) to Sept.23rd . No counts exceeded 50. Nest holes (approx 10)
were excavated in Berkshire and breeding may have been attempted but success
was unknown.
SWALLOW
Common summer visitor. Recorded between
Apr.7th and Oct.2nd. Maxima 300, Aug.21st.
HOUSE MARTIN
Common summer visitor. Recorded between
Apr.27th (late date) and Oct.2nd. Maxima 350, May 14th.
MEADOW PIPIT
Moderately common winter visitor and passage
migrant that has summered. Recorded until Apr.7th and from Sept.29th. Maxima
40, Oct.13th.
ROCK PIPIT
Scarce visitor. One, Fox lane area, Hampshire
on Oct.29th (JMC). The sixth site record. The first record since 1997. Two
of the previous five records have also been in October.
YELLOW WAGTAIL
Regular passage migrant that has bred. A very
good year. In spring singletons on six dates between Apr.9th and May 12th.
In autumn recorded on 13 dates between Aug.24th and Sept.29th, all
involving singles apart from 4, Aug.25th and 3, Aug.30th. A bird showing
characteristics of Blue Headed Wagtail, a race of Yellow Wagtail was present
on the new workings on May 25th (CRG). It was considered by the observer to
most closely resemble the ‘Sykes’ (Motacilla flava beema) race. The first
site record of an extra limital UK race of Yellow Wagtail.
GREY WAGTAIL
Moderately common resident. At least one pair
bred successfully.
PIED WAGTAIL
Common resident and winter visitor. Maxima 70,
Aug.21st.
WREN
Abundant resident.
DUNNOCK
Common resident.
ROBIN
Very common resident.
WHINCHAT
Regular passage migrant. The only record was
of 1, Sept.29th to 30th (BMA, GR).
STONECHAT
Irregular winter visitor and passage migrant.
In the early year: pair present till Feb.21st, 1, Mar.18th. In the late
year: 1/2 on 24 dates between Aug.30th and Dec.31st with three birds (1m 2f)
present from Nov.29th.
WHEATEAR
Moderately common passage migrant. In spring
singletons recorded on 7 dates between Apr.9th and May 5th. In autumn: 1,
Aug.9th , 2, Aug.12th, 1, Aug.27th, 1, Sept.9th, 1, Sept.15th and 2,
Sept.23rd.
BLACKBIRD
Common resident.
FIELDFARE
Common winter visitor. Recorded until
Apr.12th and from Oct.23rd. The maximum count was of 35 on Dec.8th.
SONG THRUSH
Common resident.
REDWING
Very common winter visitor. Recorded until
Apr.5th and from Sept.29th. The maxima was 200 on Jan.13th.
MISTLE THRUSH
Common resident.
GRASSHOPPER WARBLER
Infrequent visitor. The only record was of 1,
Sept.2nd (CRG).
SEDGE WARBLER
Moderately common summer visitor. Recorded
from Apr14th. Five singing males held territory (cf 6 in 2006).
REED WARBLER
Moderately common summer visitor. Recorded
from Apr.26th. Five singing males held territory (cf 5 in 2006).
LESSER WHITETHROAT
Summer visitor. Recorded from Apr.26th. Two
singing males briefly in song.
WHITETHROAT
Very common summer visitor. Recorded from
Apr.16th. A minimum of 16 singing males held territory (cf 15 in 2006).
GARDEN WARBLER
Very common summer visitor. Recorded from
Apr.22nd . At least 12 singing males held territory (cf 10 in 2006).
BLACKCAP
Very common summer visitor and occasional
winter visitor. Recorded from Mar.31st . At least 7 singing males held
territory (cf 10 in 2006).
CHIFFCHAFF
Very common summer visitor and regular winter
visitor. Recorded between Mar.14th and Oct.18th. Approx six singing males
held territory (cf 8 in 2006).
WILLOW WARBLER
Common summer visitor. Recorded from Apr.9th
until Sept.8th. Three singing males held territory (cf 3 in 2006).
GOLDCREST
Common winter visitor and passage migrant with
small numbers breeding. At least one singing male was present during the
summer.
LONG TAILED TIT
Abundant resident.
COAL TIT
Regular visitor. Seven records mainly of
singletons on peanut feeders!
BLUE TIT
Abundant resident.
GREAT TIT
Abundant resident.
NUTHATCH
Resident in small numbers. Successfully bred.
TREECREEPER
Resident in small numbers. Successfully bred.
JAY
Common resident. Maxima 10, Dec.15th.
MAGPIE
Very common resident.
JACKDAW
Very common resident. Maxima 30, Sept.22nd.
ROOK
Regular visitor. Maxima 15, Oct.6th.
CARRION CROW
Common resident.
STARLING
Common resident. Maxima 150 on Mar.21st .
HOUSE SPARROW
Resident nearby.
CHAFFINCH
Abundant resident and winter visitor.
BRAMBLING
Regular winter visitor usually in small
numbers. Recorded as follows; 1, Oct.20th, 2, Nov.7th, 1, Nov.8th and 1,
Nov.17th.
GREENFINCH
Moderately common resident and winter visitor.
Maxima 45 at roost Jan.13th.
GOLDFINCH
Very common resident and winter visitor. A
maxima of 35 on Nov.3rd.
SISKIN
Very common winter visitor. The maximum count
was 100 on Dec.24th and 27th. Smaller numbers were recorded in the early
winter period. Two on Jul.4th was an atypical date.
LINNET
Moderately common resident and winter visitor.
LESSER REDPOLL
Moderately common winter visitor. No count
exceeded 10.
MEALY REDPOLL
Very rare visitor. One was present with Lesser
Redpolls in alders near the Longwater bridge on Dec.12th (CRG). The first
site record of this full species originally considered a subspecies.
BULLFINCH
Moderately common resident.
YELLOWHAMMER
Resident in small numbers. Two singing males
held territory (cf 2 in 2006), breeding successful. The maximum count was 12
on Jan.20th.
REED BUNTING
Moderately common resident. Approximately five
singing males held territory (cf 5 in 2006). Breeding successful.
LIST OF OBSERVERS
|
B.M.Archer
R.Cheeseman
R.G.Davies
M.Lenney
D.Nash
R.Purchell
J.B.Sheridan
D.Steven
M.Walford
L.J.Warren
L.Woods |
P.Burden
J.M.Clark
S.F.Farmer
M.Mitchell
M.Parkes
G.Randall
N.Silver
J.C.Tanner
J.J.Walling
J.Westmacott
A.Worgan
|
Dr I.H.Brown
Dr M.N.Clifford
C.R.Gent
K.Moor
M.G.Philpott
J.Reed
G.Smethurst
Mrs L.D.M.Tanner
R.M.Warden
Mrs R.Westmacott
|
K.Carter
K.Crick
R.J.Godden
R.Murfitt
S.Proudley
Mrs C.Rose
R.Stansfield
C.D.Taylor
J.E.Warren
C.D.Williams
|
Other observers only known
by initials to recorder: DJB, KAB, DC, CMD, TD, GFE, KAH, CEK, BM, RCM, APN,
DN, MP, DSS, FS.
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APPENDIX C
EVERSLEY GRAVEL PITS (inc MOOR GREEN LAKES)
BIRD SPECIES LIST 1990-2007
Click here to open the spreadsheet in xls format (61kb)
If you do not have Excel, the following link
provides a pdf version
Click here for a pdf version (49kb)
Click the Back button on your Internet Browser
(I.e. Explorer) to come back to this Report
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APPENDIX D
NOTES AND GUIDELINES ON BIRD RECORDING
Following the creation of Moor Green Lakes
(part of the Eversley Gravel Pit complex) as a nature reserve, it is
necessary to maintain a detailed log of birds using the site in order to
monitor bird populations, with particular reference to conservation
management carried out on the site by the Moor Green Lakes Group and RMC.
These guidelines are designed to assist any persons visiting the site who
wish to submit their records. The collection of such data is an important
function of the group and all contributions, no matter how small are
welcomed.
Recording Area
The
boundaries of the site for recording purposes are defined as:
| |
a) |
South of the
Lower Sandhurst Road |
| |
b) |
West of Mill
Lane |
| |
c) |
East of
Longwater Road |
| |
d) |
North of the
golf course access track running from the Reading Road to Mill Lane. |
Information required
Ideally
records should be submitted on Eversley Gravel Pit recording forms available
from the recorder (please enclose an SAE). Records should be submitted every
3-4 months (or more frequently!) so that the log can be kept as up to date
as possible. Less frequent visitors may wish to submit their records
annually.
Where
possible the following information should be provided:
| |
1) |
Name of
species (include age/sex if known) |
| |
2) |
Number of
individuals (accurate counts particularly useful) |
| |
3) |
Date of
observation (and time if a fly over only sighting or short stay record) |
| |
4) |
Site location |
| |
5) |
Other
observations such as unusual behaviour or direction off flight of birds
flying over, etc. |
| |
6) |
Observer(s) initials. Records not submitted on forms should also include
name and address |
| |
7) |
Accompanying field notes if required. |
The species list for the site
at Appendix C includes a code number in the left hand column. This refers to
the type of records required for that species. The full details are:
| |
1*= |
All records
required. Please submit notes on the sighting with the record. These
notes should include details of the diagnostic identification features
which were observed at the time, other species nearby, the duration and
distance of the observation, weather conditions, optical aids used and
previous experience of the species. |
| |
1 = |
All records
required. |
| |
2 = |
Whole site
counts, reserve area counts, breeding summary (number of pairs and
young, singing males), early/late dates for summer and winter visitors,
movements, unusual dates and interesting behaviour. |
| |
3 = |
Breeding
summary only. |
| |
4 =
|
Only unusual
records for the species e.g. high counts, early breeding records. |
Records should be sent to: lan Brown, 4 Evesham Walk, Sandhurst, Berks. GU46
0YU
Sightings of birds in category 1*, would be gratefully received by phone
(01344 778412), particularly if still present, to enable dissemination of
information to other interested observers!
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APPENDIX E
NOTES AND GUIDELINES ON DRAGONFLY RECORDING
Any person visiting the
site who wishes to submit dragonfly/damselfly records may do so. Any
attributable records are gratefully received. Observers may add their
records to the monthly dragonfly posted in both Grove and Colebrook hides.
Alternatively records of a
more detailed nature may be submitted at any time direct to the recorder but
for preference before the end of October. If submitted after the end of
October the data will be logged on to the Reserve’s database but may be too
late for inclusion in the Annual Report.
Records can be presented
in any form that best suits the observer but should include:
|
Observer’s
name and address |
|
Date/Time/Weather |
|
Site
location, i.e.: |
| |
Colebrook Lake North (CLN) |
| |
Colebrook Lake South (CLS) |
| |
Colebrook Cut (CC) |
| |
Grove Lake (GL) |
| |
Horseshoe Lake |
| |
River Blackwater and path (BR) |
|
|
|
Name(s) of
species observed |
|
|
|
For
each species observed at each site an estimate of the number of: |
| |
Adults |
| |
copulating pairs |
| |
ovipositing females |
All records should be sent
to the Recorder: Ken Crick, 29 Village Way, Yateley, Hants GU46 7SE.
Information on sightings of rare or unusual species would be welcomed by
phone (01252 872508).
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APPENDIX F
WATER ANALYSIS
K. A. Crick
The
northern-most scrape in front of Grove hide continues to register a pH lower
than 3. High water levels across the site and occasional on shore winds have
failed to flush the acidity out of this scrape. The acidity is a function of
the scrape's underlying geology; in such circumstances the application of
solid chalk has been recommended.
The contained
flushing of the southern section (recently bunded) of the same scrape has
produced an abundance of vegetation and the marsh-like transitional phase
that attracted Black Darter and Keeled Skimmer Dragonflies has gone.
The scrapes
on Long Island were again assessed for pH both in January and October 2007.
With minimal improvement registered during the January assessment it was
decided to open up both ends of each southern shore line scrape. That same
day Mr John Coupland set to, deepening the existing openings to the main
body of water and creating new ones. The success of his efforts can be seen
in the results for October reproduced below.
|
Long Island Scrape
Reference |
Date |
|
03-Jun-06 |
23-Jan-07 |
23-Oct-07 |
| pH |
Temp |
pH |
Temp |
pH |
Temp |
| 0623N |
4.7 |
24.1 |
4.7 |
2.6 |
6.3 |
10.2 |
| 723 |
5.5 |
24.0 |
5.3 |
2.0 |
6.5 |
9.3 |
| 823 |
2.6 |
24.3 |
3.1 |
5.0 |
6.9 |
8.8 |
| 822 |
|
|
5.4 |
4.8 |
6.5 |
12.9 |
| 622 |
6.6 |
31.0 |
4.6 |
3.4 |
7.0 |
7.7 |
| 0623S |
6.6 |
23.3 |
6.7 |
3.2 |
6.7 |
12.8 |
Last year's
report commented on the declining dissolved oxygen level in Colebrook Cut.
The build up of a matt of Duckweed Lemna spp., is symptomatic of this
decline. Dissolved oxygen levels remained low through out the spring, summer
and autumn assessments averaging 4.6mFl.
The main
reason for carrying out the water analysis is to check on the stability of
the ecosystem that is the reserve's water body. We have seen significant
localized increases in acidity when our conservation activities have
substantially disturbed the substrate. Also phosphate levels increased in
one area of particular damselfly interest after the cattle had repeatedly
entered the water at the measuring station and defecated material had
entered the system. We also know from our results that we can correct these
problems.
As the data
set builds, one is left speculating what if anything else can be inferred
from the data. The data could be used to infer trophic status (a measure of
nutrient value mainly in terms of phosphates and nitrates.) and how we
compare with other still water bodies in the South of England.
We currently
lack the skills to read very much into our data but were lucky to stumble
upon a European Diatom Database on the web at Newcastle University. This
database presented data for 26 South Eastern England, relatively small,
shallow, lowland, artificial water bodies. From the data set we have
extracted those variables we measure at MGL and equalised the units of
measurement to produce the comparative charts below.
Summary of water analysis data for Moor Green Lakes Nature
Reserve 2004 to 2007
|
Variable |
Sampling Station |
N |
Min |
Max |
Mean |
|
Nitrate/Nitrogen |
SU 80578 62663 (CLN) |
17 |
0 |
0.6 |
0.13 |
| |
SU 80555 62399 (Cut) |
17 |
0 |
0.7 |
0.16 |
| |
SU 81528 62265 (Grove) |
17 |
0 |
1.2 |
0.29 |
| |
SU 81117 62156 (River) |
16 |
3.8 |
29.6 |
8.87 |
| |
Southeast England |
26 |
0.69 |
5.58 |
1.864 |
Units with
the exception of pH are all in mg/l.
N is the
number of samples of data analysed to date for a given location and for
southeast England the number of sites sampled.
|
Variable |
Sampling Station |
N |
Min |
Max |
Mean |
|
pH |
SU 80578 62663 (CLN) |
17 |
5.5 |
7.1 |
6.55 |
| |
SU 80555 62399 (Cut) |
17 |
5.9 |
7.0 |
6.58 |
| |
SU 81528 62265 (Grove) |
17 |
5.8 |
6.9 |
6.60 |
| |
SU 81117 62156 (River) |
16 |
5.9 |
7.3 |
6.53 |
| |
Southeast England |
26 |
6.83 |
8.59 |
7.70 |
|
Variable |
Sampling Station |
N |
Min |
Max |
Mean |
|
Phosphorus |
SU 80578 62663 (CLN) |
17 |
0 |
0.851 |
0.219 |
| |
SU 80555 62399 (Cut) |
17 |
0.026 |
0.394 |
0.146 |
| |
SU 81528 62265 (Grove) |
17 |
0.036 |
0.391 |
0.146 |
| |
SU 81117 62156 (River) |
16 |
0.196 |
0.616 |
0.325 |
| |
Southeast England |
26 |
0.025 |
0.646 |
0.182 |
|
Variable |
Sampling Station |
N |
Min |
Max |
Mean |
|
Dissolved Oxygen |
SU 80578 62663 (CLN) |
16 |
3.6 |
8.0 |
5.9 |
| |
SU 80555 62399 (Cut) |
16 |
4.1 |
8.0 |
5.7 |
| |
SU 81528 62265 (Grove) |
16 |
5.0 |
7.6 |
6.3 |
| |
SU 81117 62156 (River) |
16 |
4.4 |
7.6 |
5.6 |
| |
Southeast England |
No Data |
On the
English-nature web site a 'classification of different standing freshwater
types according to nitrogen and phosphorous content' is reproduced. On the
face of it this seemed ideal, but MGL combinations of these two variables
fail to form a match with any of the combinations used to define Trophic
status.
Another
classification technique on the same web site based on alkalinity employs a
combination of pH and Calcium carbonate. Our equipment will not measure this
variable, as we have not to date purchased suitable reagents. The calcium
carbonate content can to some extent be inferred from the freshwater
invertebrate records, which include
freshwater
shrimp and molluscs. Freshwater shrimp Gammarus spp. is not found in
waters deficient in calcium. However, the thinness of the shells of MGL
freshwater snails has been commented on. So it can be inferred that calcium
carbonate is present but possibly in concentrations towards the low end of
the range that supports Mollusca spp. Further clues lie in the
aquatic plant records, provided by Chris Hall. The presence of Stonewort
Chara spp., Spiked Water Milfoll Myriophyllum spicatum, and Small
Pondweed Potamogeton berchtoldii are indicative of a base rich
lowland water body. (Base enrichment - is determined by the underlying
geology of the lake and the geology its springs have passed through, the
water acquiring calcium, magnesium, sodium and iron.), Iron is present at
MGL, its oxide is found deposited on plants, substrate and aquatic larva
(damselfly) making positive identification difficult. There are plenty of
clues, what we need is someone with the knowledge to interpret them. If that
is you, please get in touch.
References:
Corbet. Dragonflies
behaviour and ecology of Odonata. Harley Books. 1999.
English
nature. The upland management handbook-freshwater habitats. WWW. 2001
Mackereth, Heron & Talling.
Water Analysis. Freshwater Biological Association. 1978.
Macan & Worthington.
Life
in lakes & rivers.
Collins New Naturalist. 1974.
NBN
Habitats Dictionary.
www.nbn.org.uk/habitats/habitatInClass.asp 2007.
C200
Series Instructional Manual Hanna Instruments. 2003.
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APPENDIX G
MOOR GREEN LAKES GROUP COMMITTEE MEMBERS
2007-2008
|
Officer |
Committee Post / Responsibilities |
|
Peter Scott* |
Chairman / Report Editor / Recorder for Reptiles |
|
Robert Godden |
Committee
Secretary (until February 2008) |
|
Roger Murfitt |
Committee
Secretary (from February 2008) |
|
Sue
Dent |
Blackwater Valley Countryside Partnership Representative |
|
Dr.
Bruce Archer* |
Treasurer |
|
Keith Littler |
Membership Secretary (until February 2008) |
|
David Bishop |
Membership Secretary (from February 2008) |
|
Cohn Wilson |
Newsletter Editor |
|
Simon Weeks |
Site Liaison Officer |
|
Dr.
Ian Brown |
Recorder for Birds |
|
Ken
Crick |
Recorder for Dragonflies and Damselflies |
|
Ian
White |
Recorder for Mammals |
|
Sue
Proudley |
Recorder for Butterflies |
|
Colin
Proudley |
Recorder for Moths |
|
Irene Draper |
Postal Secretary |
| Peter
Standley* |
|
|
*
Represents Moor Green Lakes Group on the Steering Group |
|
Peter Scott can be contacted on
ppscott(at)aol.com |
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APPENDIX H
Moor
Green Lakes Nature Reserve Reference Library
The contents of the library so far collected are listed below.
|
Site Survey Data |
|
|
Anon.
1993. |
Plant
list for Moor Green Lakes. (Farnborough College student report) |
|
Briggs, K. 2001 |
Moor Green Lakes Nature Reserve;
ornithological monitoring 2000 |
| Brown, I. 1993 |
Eversley Gravel Pits Bird
Species List |
|
BVRCMS 2000. |
Survey Data. (Includes a number of minor surveys with Moor Green
records) |
|
Crick, K. 1999 |
Green
Lakes Odonata Population Survey, benchmark Report 1997-99 |
|
Gannaway, H. 1997 |
The
Distribution of Small Mammals at Moor Green Lakes (Farnborough College
student report) |
|
Hall
C, 1991 |
Botanical Survey. |
|
Hearn, R. 1993 |
The
Management of Disused Mineral Workings as Habitat for Waterbirds
(Farnborough College student report) |
|
Lovesey, E. 1997 |
Spider Survey |
|
Matthes, G. 1997 |
Hoverfly Surveys 1995 -1997 |
|
Smith, M. 2001 |
Bracknell Forest Borough Council Invertebrate Survey 2000 |
|
Tomlinson D. 1995 |
A Live Trapping Investigation of Small
Mammal Populations at Moor Green Lakes Nature Reserve. (Farnborough
College student report) |
| Hall C, 2001 |
A Survey of Aquatic and
Wetland Plants, August
— September
2001 |
|
Bailey.J.S 2002 |
Bat
Assessment of Moor Green Lakes Nature Reserve |
|
Hall. C 2002 |
Moor
Green Lakes Nature Reserve. A Survey of Aquatic and Wetland Plants |
|
Williams. D 2005 |
Mammal Survey for Moor Green Lakes Reserve, Yateley |
|
Briggs. K 2006 |
Moor
Green Lakes Nature Reserve Ornithological Monitoring 2006 |
|
Crick. K 2004 |
Moor
Green Lakes Odonata Population Survey 1997-2004 |
|
Cooper S 2006 |
Moor
Green Lakes Nature Reserve. An Aquatic and Wetland Plant Survey. Surrey
Wildlife Trust. |
|
|
|
Site Management |
|
|
Fourt
D, 2000 |
Moor
Green Lakes pH & liming records |
|
McAll,
G. Undated |
Management Plan for Moor Green Lakes
(draft plan for BBONT, never adopted) |
|
|
|
Group Administration |
|
|
Annual reports: |
A complete set from the 1st report in 1994 |
|
Moor
Green News |
A full set of the Group Newsletters |
|
Moor
Green Lakes Group Management Committee --
A
complete set of minutes |
I would like
to request that if anybody has information about the reserve, however small,
please could they deposit a copy in the library. I shall be able to copy it
and return the originals.
If
anybody would like to view the information please contact me Steve Bailey on
01252 331353 to make arrangements.
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APPENDIX I
Reserve
Map

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