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MOOR GREEN LAKES GROUP

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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)

 

 

 

 

 

 

 

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

Habitat Map of the Reserve

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