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MOOR GREEN LAKES GROUP

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CHAPTER 1

Introduction to the Ninth Report of the Moor Green Lakes Group

Ken Crick
Chairman of the Moor Green Lakes Group

Reserve Management and Wildlife Recording

2001 started with some work on the Reserve but by mid February Foot & Mouth restrictions were coming into effect and access to the Reserve was in theory prohibited, with all public footpaths to the Reserve blocked. There are four points of entry to the Reserve, administered by three different local authorities, so the method of control adopted varied from a single strand of tape, with a piece of paper flapping on it, to a complete barrier of bright orange plastic mesh with plastic weather proof signs.

It was not surprising therefore that I received a number of phone calls from concerned members and others, all living local to the Reserve and the Blackwater Valley footpath informing me of irresponsible dog walkers breaching the barriers. I was informed by a representative of Wokingham District Council that the restrictions were not legally enforceable as Foot & Mouth was not actually in the district. During this period someone took the opportunity to try and break in to the Colebrook Hide but the lock held and only superficial damage resulted to the door jam.

Plans to erect an anti mink fence, on Tern Island, were first given impetus with the sighting of a mink on Long Island, the fence posts (paid for by RMC) were duly commissioned and delivered but Foot & Mouth and the onset of the Tern breeding season prevented erection until December.

Work on the Management Plan progressed during the early part of the year but remained in abeyance throughout the dragonfly flight season as I chased up and down the valley in search of these fascinating insects. Work on the plan recommenced at the end of September with a first draft ready for comment by Christmas.

Sue Dent and Adrian Douglas joined the Blackwater Valley Countryside Service just in time for the start of our 2001/2 work party season. Sue now represents the BVCS on our Management Committee in place of Steve Bailey who now heads up the Countryside Service. Both Sue and Adrian have already made significant contributions to the management of the reserve. Amanda Simpson-Atkins despite leaving the BVCS continues to lead our Sunday work parties with her husband Julian, for which we are very grateful. Our gratitude is also extended to all those members who turned out to help with work party activities.

This year Chris Hall was commissioned to carry out an aquatic plant survey. Also Bob Merritt, one time national dragonfly recorder and now something of a specialist on beetles and spiders was prevailed upon to spend some time on the Reserve. Their findings adding significantly to our overall knowledge of the site's flora and fauna. Steve Bailey (bats), Sue Proudley (butterflies), Kevin Briggs, lan Brown, Delphine Hoyle, Katrina Slocombe and myself continued to collect data in our respective fields of interest. The results of these efforts are to be found recorded throughout the report. A special thanks also to Chris Rose who has again compiled our individual efforts to form this report.


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CHAPTER 2

Conservation Work Programme since the last AGM

April 2001 to March 2002

Sue Dent

This has been a busy year for the conservation volunteers on the reserve, with a great deal achieved.

The Sunday conservation work parties have continued with seven tasks through the winter with an average of 14 volunteers each time, a tremendous turnout. This was supplemented by four visits by the Blackwater Valley Conservation Volunteers and a number of visits by BVCS staff to pick up the odds and ends'. A total of 174 volunteer days in all. Many thanks to all the volunteers, it simply wouldn't be possible to maintain the reserve to its current - improving - standard without all their effort. Special thanks also to Amanda Simpson-Atkins for leading the Sunday tasks and to Steve and Sheila Farmer for encouraging new and old members alike to come along.

Regular Conservation Tasks completed this year:

There are a number of jobs which need to be done each year to maintain the habitats and the general infrastructure of the site:

  • Cutting viewing slots alongside the lake, the volunteers cleared one area with the remainder done by Julian Simpson-Atkins as a contractor.

  • Keeping islands clear of vegetation. Tern Island and Goose Island have both been cleared of scrub this year so that they are suitable for breeding birds. Goose Island also provides open shingle areas that some species of dragonfly like.

  • Grassland. We are aiming to keep a mixture of grassland and scrub around the lakes and so have continued to clear bramble, not to get rid of it entirely but to limit it to its current extent. The aim has been to keep the lake edges clear of long vegetation and willow and in particular this year 3 bays on the northern edge of Grove lake have been cleared of scrub and trees completely to create short grass areas where the birds can feed and rest.

  • Cattle. The cattle continue to do a vital job maintaining the grassland areas of the site. Unfortunately we were unable to have the Highlands again this year but were able to arrange a substitute herd, of in-calf heifers, perhaps not quite as picturesque as the highlands but they have done their job well. They were on site from December to March.

Apart from the routine work we have also had a number of special projects this, year.

Hibernaculum
The most recent is the hibernaculum, which has been organised by Peter Scott as part of his Earthwatch grant. Everything fell into place miraculously and the hibernaculum was installed by a Sunday work party on the 10th February. This should provide a useful extra habitat for the reserve. Peter Scott is going to monitor the area for reptile activity in the future and would appreciate it if members would report any sightings of reptiles on the reserve this year either direct to Peter or via Ken or myself.

Mink fence on Tern Island

The mink fencing has been installed on Tern Island, or Stalag 19 as I have heard it called, The fence was installed because mink have been reported on site in order to protect the breeding terns on the island. The finished article isn't too obtrusive and hopefully will do its job well and keep the mink away from the nesting birds.

Crassula helmsii
This year there have been moves on several fronts to tackle the problem of Crassula helmsii on the reserve. There is no quick and easy solution to the problem but hopefully the work proposed should begin to tackle it. Chris Hall's survey of the aquatic and wetland plants of the reserve (see elsewhere in this report) showed that at present Colebrook lake is heavily infested with Crassula while there were only a few of plants on the scrape next to the hide on Grove.

 

In June 2001 the Crassula in the scrape beside Colebrook Hide was cut and dug out by hand. This was back breaking work and the sheer physical bulk of the Crassula makes it impossible to tackle more than a very small area this way. This kind of mechanical removal is not recommended by any recognised Crassula authority and will not be undertaken again.

In autumn 2001 the Crassula on the new scrape in front of Grove Hide was covered by remnants of household carpet in an attempt to shade it out of existence. A technique used successfully at Frensham Pond. It has proved quite difficult to get the carpet to stay and thanks to Ken Crick and Steve Farmer for replacing it when it moved. When water levels drop the remainder of the scrape will be assessed and any other patches will either be carpeted or possibly sprayed or dug out if very small. The condition of the Crassula under the carpet will be assessed in the summer to see if it has been killed.

Ken Crick has assessed the options for tackling the infestation on Colebrook Lake and we hope to be implementing a programme of limited spraying with herbicide to try and get it under control.

Finally Having joined the BVCS team in September 2001 I would like to thank the Moor Green Lakes Group for making me welcome and for all their help in getting me up to speed on the site and what needs to be done.


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CHAPTER 3

REPORT ON BIRDS 2001

Recorder: lan Brown

During the year 127 species were recorded of which 66 were present in suitable breeding habitat in the summer. Three new species were added to the site list, Green Winged Teal, Lesser Yellowlegs and Ring Necked Parakeet bringing the total number of species recorded to 201.

In the early winter period there were good numbers of surface feeding duck, with a site record count of 585 Wigeon. This contrasts markedly with ten years ago when there were approximately 50 birds using the site. There were moderate numbers of Goosander roosting on the site and other early year highlights included Pintail, Peregrine and a brief appearance by a Ring Necked Parakeet in February.

By the time the site was reopen following closure due to FMD many spring migrants had already returned. Wader passage although generally light produced some good local species including Sanderling and Turnstone but the spring highlight was the first Temminck's Stint for nine years. This bird was well watched during its four day stay most of which was spent in the vicinity of Tern island. Other spring records of note were a Mediterranean Gull and several Black Terns.

As in recent years breeding success was mixed but Little Ringed Plovers bred successfully on the reserve although the other wading species were unsuccessful with Redshank leaving the site relatively early. Little and Great Crested Grebes both bred successfully on the reserve. However as in 2000 Common Terns continue to flourish on Tern Island with nine pairs rearing a total of 18 young (cf 6pairs / 14 young in 2000), yet another record success. Most of the birds feeding in the valley come from this colony and travel distances of many miles to keep their hungry young satisfied! Mandarin were again successful in nestboxes and Tufted Ducks were very successful rearing a minimum of 25 young. Woodlark bred on the site for the fourth year running and Kingfisher and Grey Wagtail prospered in their traditional sites on the river. The brief appearance of a Lesser Yellowlegs on the Hampshire part of the complex in June was an unexpected find and constitutes the first record of this North American species.

Late summer/autumn saw a scattering of interesting waders mainly on the drained Hampshire pits with Ruff, Black Tailed Godwit and several Curlew Sandpipers. Other highlights included two records of Little Egret and two Caspian Gulls. Wader passage on the reserve area was generally light due to vegetation encroachment.

The year closed with returning waterfowl building up early. This included the highlight of the year, a drake Green Winged Teal that gave obliging views to many (from far and wide!) on the reserve from November into 2002. Another first, involving a North American species. Other highlights during this period included Mediterranean Gull, Hen Harrier (only the second site record, the first in 1988), several sightings of Barn Owl and good numbers of finches including Siskin, Redpoll and especially Brambling, the latter frequenting land near Longwater SF.

Last but not least many thanks to the growing band of observers who submit records including those who provide observers names on the log sheet. 


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CHAPTER 4

BOTANICAL SURVEY 2001

Dr Delphine Hoyle

Records of the plants on the Reserve have been kept since 1992 (excluding 1996 and 1999) and since 1997 these records have been quantitative surveys of the areas around the Colebrook Lakes.

The methods used since 1997 are based on National Vegetational Classification (NVC) Methodology.

Ten random samples (1 x 1 m) were surveyed on 14th July 2001, five on the north side and five on the west side of Colebrook Lake North. In each of the sample squares the species present were identified and quantified both on abundance and frequency (see previous Annual Reports for further details of this method)

Table A shows the frequency and abundance of the species found in each of the samples. Table B lists other species found in the surrounding areas.

Eighteen species from the original seed mix were found in the sample squares and one more in the surrounding area.

Predominant species were Leucanthemum vulgare, Plantago lanceolata and Centaurea nigra and of the grasses Agrostis spp and Holcus lanatus. This is in line with previous findings.

Again there was little evidence of tree and shrub invasion although there were patches of bramble outside the survey area.

Thanks are due to Irene, Draper, Helen Edwards, Marjorie Trendall, Katrina Slocombe, and Gill and Michael Wells for their help in this survey.

Table A

LATIN NAME

COMMON NAME

COLEBROOK LAKE NORTH

 

North Side

West Side

S

Achillea millefoliurn

Yarrow

 III (1-9)

0

 

Arrhenatherum elatius

False Oat

 I (1)

I (5)

S

Centaurea nigra

Black Knapweed

0

I (1)

 

Cerastium fontanum

Mouse-ear Chickweed

0

I (1)

 

Cirsium arvense

Creeping Thistle

 II (1-5)

II (4-5)

 

Crepis capillaris

Smooth Hawk's Beard

 I (2)

0

S

Daucus carota

Wild Carrot

II (1-5)

II (4-5)

S

Galium verum

Lady's Bedstraw

III (3-5)

II (5-7)

S

Geranium pratense

Meadow Crane's-bill

0

 1 (1)

S

Hypericum perforatum

Perforate St. John's Wort

II (1)

0

S

Hypochaeris radicata

Common Cat's-ear

I (3)

0

S

Knautia arvensis

Field Scabious

0

 I (1)

 

Lathyrus pratensis

Meadow Vetchling

II (1-9)

0

S

Leucanthemum vulgare

Ox-eye Daisy

V (4-7)

V (1-4)

S

Lotus corniculatus

Common Bird's-foot Trefoil

I (2)

0

S

Medicago lupulina

Black Medick

0

I (1)

S

Plantago lanceolata

Ribwort Plantain

V (2-7)

V (1-8)

S

Prunella vulgaris

Selfheal

0

I (3)

 

Prunus spinosa

Blackthorn

I (1)

0

 

Quercus robur

Oak

I (1)

0

S

Ranunculus acris

Meadow Buttercup

I (1)

II (2-5)

 

Ranunculus repens

Creeping Buttercup

II (1-2)

IV (4-9)

 

Rubus fruticosus

Bramble

0

I (5)

S

Rumex acetosa

sorrel

II (1-3)

III (2-3)

 

Rumex spp

Dock spp.

I (1)

I (4)

S

Stachys officinali s

Betony

I (1)

I (4)

 

Stellaria graminea

Lesser Stitchwort

II (3-4)

I (3)

S

Taraxacum officinale agg.

Dandelion

0

I (2)

 

Trifolium pratense

Red Clover

0

II (2-4)

 

Trifolium repens

White Clover

I (8)

0

 

Vicia hirsuta

Hairy Tare

0

II (1-4)

 

Vicia sativa

Common Vetch

0

I (1)

S

Vicia tetrasperma

Smooth Tare

0

IV (1-3)

 

 

 

 

 

 

Agrostis spp.

Bent spp.

V (5-9)

IV (4-9)

 

Holcus lanatus

Yorkshire Fog

III (1-5)

V (1 -5)

 

Lolium perenne

Perennial Rye Grass

II (1-5)

I (5)

 

Vulpia bromoides

Squrrel-tail Fescue

I (5)

0

Note: S = Sown Species

Table B

Other plants recorded outside the sample squares

 

Agrimonia eupatoria

Agrimony

 

Arctium minus agg

Lesser Burdock

 

Centaurium erythtaea

Common Centaury

 

Crataegus monogyna

Hawthorn

 

Dactylis glomerata

Cocksfoot

 

Deschamosia cespitosa

Tufted flair Grass

 

Elymus repens

Couch Grass

 

Epilobium spp

Willowherb

 

Filago vulgaris

Cudweed

 

Galium aparine

Cleavers

 

Galium palustre  app

Marsh Bedstraw

 

Geranium dissectum

Cutleaved Cranesbill

 

Heracleum sphondyliurn

Hogweed

 

Linaria vulgaris

Common Toadflax

 

Lycnis flos-cuculi

Ragged Robin

 

Lycopus europacus

Gipsywort

 

Lysimachia vulgaris

Yellow Loosestrife

 

Malva sylvestris

Common Mallow

 

Pulicaria d ysenterica

Common Fleabane

 

Senecio jacobaea

Ragwort

 

Silene alba

White Campion

S

Sisymbrium officinale

Hedge Mustard

 

Stachys sylvatica

Hedge Woundwort

 

Trifolium arvense

Haresfoot Clover

 

Ulex europaeus

Gorse

 

Urtica dioica

Nettle

 

Vicia cracca

Tufted Vetch

 S = Sown species


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CHAPTER 5

 REPORT ON BUTTERFLIES FOR 2001

Recorder Sue Proudley

The foot and mouth restrictions prevented access before April in 2001 so the Brimstone butterflies seen flying in good numbers outside (and probably inside) the reserve at the end of March are not recorded. Despite this omission the Brimstone did well until July then tailed off sharply.

Skippers faired very poorly this year, possibly due to the wet conditions at the end of last year.

Orange Tip and White butterfly numbers were slightly up, but Red Admiral and Small Tortoiseshell were slightly down on last year.

Just two Purple Hairstreaks were seen in August and there were no records of Small Copper this year.

The Common Blue was not recorded until August. It was probably missed in June as this is a popular holiday month.

The Holly Blue was not seen in 2000 but reappeared in 2001.

Peacock numbers were up, but Comma records were halved.

The Gatekeeper did well but Meadow Brown, Speckled Wood and Ringlet numbers were lower than last year.

No Clouded Yellow visitors were seen and only a single Painted Lady in August.

My thanks to 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 list of species observed on the reserve in 2001 is as follows:

Small Skipper Purple Hairstreak Speckled Wood
Essex Skipper Common Blue Gatekeeper
Large Skipper Holly Blue Meadow Brown
Brimstone Red Admiral Ringlet
Large White Painted Lady  
Small White Small Tortoiseshell  
Green-veined White Peacock  
Orange Tip Comma Number of species 20

The following observers contributed to the records:

Ken Crick G Rowland JEW
Chris Rose J P R & J W
Colin Proudley R W A B
S Farmer R J G A T

 

  MOOR GREEN BUTTERFLIES  

Recorded numbers April - Nov 2001

JAN

FEB

MAR

APR

MAY

JUN

JUL

AUG

SEP

OCT

NOV

DEC

Small Skipper   

(Thymelicus sylvestris)

 

 

 

 

 

 

3

 

 

 

 

 

Essex Skipper  

(Thymelicus lineola)

 

 

 

 

 

 

5

 

 

 

 

 

Large Skipper 

(Ochlodes venata)

 

 

 

 

 

3

7

 

 

 

 

 

Clouded Yellow 

(Colias crocea)

 

 

 

 

 

 

 

 

 

 

 

 

Brimstone

(Gonepteryx rhamni)

 

 

 

7

12

3

4

 

1

 

 

 

Large White

(Pieris brassicae)

 

 

 

 

2

2

22

4

2

 

 

 

Small White

(Pieris rapae)

 

 

 

 

4

2

8

10

4

1

 

 

Green-veined White

(Pieris napi)

 

 

 

 

1

1

5

6

1

 

 

 

Orange tip

(Anthocharis cardamines)

 

 

 

1

14

 

 

 

 

 

 

 

Green Hairstreak

(CaIIophrys rubi)

 

 

 

 

 

 

 

 

 

 

 

 

Purple Hairstreak

(Quercusia quercus)

 

 

 

 

 

 

 

2

 

 

 

 

Small Copper

(Lycaena phlaeas)

 

 

 

 

 

 

 

 

 

 

 

 

Common Blue

(polyommatus icarus)

 

 

 

 

 

 

 

3

 

 

 

 

Holly Blue

(Celastrina argiolus)

 

 

 

 

3

 

7

2

 

 

 

 

Red Admiral

(Vanessa atalanta)

 

 

 

 

1

 

5

4

4

2

2

 

Painted Lady

(Cynthia cardui)

 

 

 

 

 

 

 

1

 

 

 

 

Small Tortoiseshell

(Aglais urticae)

 

 

 

2

2

 

 

2

 

 

 

 

Peacock

(Inachis io)

 

 

 

13

18

3

2

 

2

1

 

 

Comma

(polygonia c-aIbum)

 

 

 

3

3

 

5

1

8

 

 

 

Speckled Wood

(Pararge aegeria)

 

 

 

 

4

 

5

10

6

1

 

 

Marbled White

(Melanargia galathea)

 

 

 

 

 

 

 

 

 

 

 

 

Grayling

(Hipparchia semele)

 

 

 

 

 

 

 

 

 

 

 

 

Gatekeeper

(Pyonia tithonus)

 

 

 

 

 

 

81

150

 

 

 

 

Meadow Brown

(Maniola jurtina)

 

 

 

 

 

5

40

20

1

 

 

 

Ringlet (Aphantopus hyperantus) 17 1


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CHAPTER 6

REPORT ON DRAGONFLIES AND DAMSELFLIES FOR 2001

Ken Crick

The Dragonfly and Damselfly flight season for 2001 at Moor Green has been mixed in many ways. The weather was generally not favourable characterized by poor light levels, low temperatures and strong winds on many of the days associated with the survey data collection. In fact it often seemed to improve shortly after I left the reserve. Numbers were generally down on last year, however some species did well. There were good numbers of Southern Hawker about not only at Moor Green but also throughout the valley.

The planned for collection of Dragonfly & Damselfly larva during the early spring did not take place with Foot & Mouth restrictions barring access to the site. Bob Merritt the editor and author of two well known books on Odonata visited the site during the first week in April and as an aside to his main objective reported elsewhere, recorded the presence of five types of damselfly larva and one dragonfly larva.

The flight season was late getting underway with Common Blue Damselfly not showing until halfway through May. Emerald Damselfly & Golden Ringed Dragonfly both failed to make an appearance on site though good numbers were to be seen elsewhere in the area. Four Spotted Chaser and Emperor Dragonfly numbers were again disappointingly low. A single Keeled Skimmer made an appearance in mid June, Downy Emerald Dragonfly bred for a second year and I was again fortunate to see one emerging from its larval state on the north shore of Colebrook Lake North. In all Sixteen species were recorded as present within the constraints of the proscribed data collection methodology.

Whilst searching for exuvia the opportunity was taken to measure the water pH (acidity/alkalinity) at a number of sites round the reserve, the results can be found at Appendix F.

Once again my thanks to those of you who have taken the trouble to record your sightings on the hide charts, it is appreciated. Special thanks go to Alex Twyford who provided data for 23 visits to site from May to September covering 13 species and detailed climatic conditions. Alex recorded a Beautiful Demoiselle on the 13th June. During July 1999 a male was seen on the wing at Owlsmoor so the odd migrant can be expected.

Those providing information were:

Dr.lan Brown Mrs.Chris Rose Mr. Chris Hall Mr.John Warren
Mr. Gilbert Rowland Mr. Maurice Budden Mr. Alex Twyford  
and  SFSC CD RJD  

ODONATA CHECKLIST

DAMSELFLIES Zygoptera

BLUE-TAILED DAMSELFLY Ischnura elegans

Larva for this species was confirmed as present in the reserve's waters during April. The first sightings on the wing were not until the 18th May, and then only two males. It was not until the 26th May that double figures were recorded. The population counts peaked at 149 during the first week in June and started a steady decline from the third week in July. The last recorded population survey sighting being the 26th August when a single male was seen. Chris Hall during his aquatic botanical survey recorded the presence of this species on the 6th Sept. One unusual record on site was of a green bodied male mating with the blue form female. This is unusual because the males are invariably blue in the thorax, the colour variations being restricted to the female of the species. A photograph was taken.

BANDED DEMOISELLE
Caloperyx splendens

As with last year the weather conditions were not conducive to aiding early sightings of this species. Two were seen on the 12th May by Alex Twyford. The survey noted their presence on the 18th May when 60 were recorded. On the 6th June the population peaked at a count of 393. A second peak occurred in the second & third weeks of August, This has happened three times, over the past five years, in 1998, 99 and 2001 each time in mid August The last of the Banded Demoiselle were seen on the 10th September. The larvae proved easy to catch in the River Blackwater during April.

LARGE RED DAMSELFLY Pyrrhosorna nymphala

Again one of the four species of damselfly for which the presence of larva was confirmed in April. Exuvia were noted and both sexes seen on the wing on the 3rd May. Population numbers are down on previous years. The surveys highest count was only 19, but Alex Twyford had a count of 37 on the 28th May. No further sightings were made after the 2nd July.

EMERALD DAMSELFLY Lestes sponsa

No recorded sightings for 2001.

COMMON BLUE DAMSELFLY Enallagama cyathigerum

Again Alex Twyford was first to report the appearance of this species on the 12th May, numbers steadily increased as the month progressed and copulating pairs were seen from the 30th May. The population count peaked at 795 on the 27th June; numbers hovered around the 300 mark until the 20th August and by the end of that month were declining rapidly. An odd male was still to be seen hanging on, on the 30th October. From the all time high population figures recorded in 1999 & 2000 the 2001 numbers more closely resemble those of 1998. This is the first year that the current annual survey technique has recorded any Common Blue Damselflies as present during October. I am indebted to those of you who recorded the number of CBDs seen on the hide charts. The correlation between our respective counts was quite close.

AZURE DAMSELFLY Coenagrion puellao

Another species whose larva was confirmed as present by Bob Merritt. This species appeared for the first tune on the wing in the form of a single male on the 18th May. The population survey never achieved double figures, however Alex Twyford did achieve an 80 count on the 28th May The species was observed copulating and ovipositing on floating vegetation on the most north-westerly part of Colebrook Lake North. Ovipositing takes place with the male remaining attached to the female (in tandem) thus denying her to any other male. The last sighting was on the 1st August, again recorded by Alex.

RED-EYED DAMSELFLY Erythromma najas

Another species who's observed numbers barely made double figures. It was first observed on the 30th May when four were seen, further sightings occurred twice in June, once in July and twice in August. On the last occasion both males and females were present. This was also the highest count of the season with twelve individuals. Adult males spend much of their time over water and away from the bank, as only transect 1 actually touches the waters edge and then only for a distance of approximately 100 meters the opportunity for observing this species is limited. Off transect when water pH was being sampled to the east of Goose Island red-eyed damselflies were frequently seen. Horseshoe Lake's lily pad was again a Mecca for this species. Chris Hall who had free range across the reserve for his aquatic botanical survey recorded at least twelve members of this species over a two-day period in September.

 

DRAGONFLIES Anisoptera

FOUR-SPOTTED CHASER Libellula quadrimaculata

There were no independent sightings of this species during 2001. It was only recorded during the year's survey as present on site on three occasions. Single specimens on the 30th May & 3rd July, with two on the 11th June.

DOWNY EMERALD
Cordulia aenea

This is the second consecutive year that Downy Emerald dragonflies have been seen at Moor Green. They were seen in May, June & July, all sightings were at the north west corner of Colebrook Lake North. On the 23rd of May a single specimen was found as it emerged from its larval stale, photos were taken and the exuvia recovered. The remains of a dead Downy Emerald were found in a spiders web local to the emergent point some days later. Sightings on any given day never exceeded two in number. An independent sighting of a single male was recorded by Alex Twyford on the 14th July.

BLACK-TAILED SKIMMER Orthetrum cancellatum

Immature specimens appeared at the end of May and continued to be observed until the 19th June. The population of mature insects peaked during the first week in July with a count of 30. A second smaller population peak was observed during the last week of the same month. The last population survey sitting was on the 28th August. The numbers recorded for the year were the highest to date.

Bob Merritt's April dip produced only one dragonfly larva and it was a Black-tailed Skimmer. Chris Hall recorded single sightings over both Colebrook Lake North & Grove Lake on the 5th & 6th of September respectively.

KEELED SKIMMER Orthetrum coerulescens

A single immature Keeled Skimmer was observed during a work party on the 21st June in the vicinity of the scrape in front of Colebrook hide. There are breeding sites on two sides of Moor Green where this species thrives at Bramshill and Owlsmoor.

EMPEROR DRAGONFLY Anax Imperator

The Emperor Dragonfly was only observed on site during July and then only twice, three were seen on the 3rd July and one on the 16th, all were males.

BROWN HAWKER Aeshna grandis

This species was twice seen ovipositing in the river. Numbers were slightly down on previous years; at no point did we reach double figures. 5 individuals being the largest single sighting spread over the two River transects. Members using the hide charts recorded very few sightings and then only in August & September. The survey data indicates their presence on site from the first week m July through to the very end of September.

GOLDEN-RINGED DRAGONFLY Cordulegaster boltonii

Following last years clarion cry "Our best year yet" this species failed to make an appearance at Moor Green.

BROAD-BODIED CHASER Libellula depressa
No recorded sightings this year at Moor Green.

MIGRANT HAWKER Aeshna mixta

The numbers for this species held up well this year, first appearing on the 1st August its presence was noted right through till the 22nd October. Twice numbers peaked at 18 individuals, once on August the 28th and again on the 27th September. Both sexes were present with copulating pairs to be seen on the wing.

SOUTHERN HAWKER Aeshna cyanea

Alex Twyford told me that the best time to see this species at Moor Green was in the early evening. This is the sites best year to date for this species with recordings on the hide charts for September & October. They were first seen on a survey walk during the third week in August and a single female was present on transect 4 on the 30th  October. The largest number of sightings on a single day was 5 individuals. Both sexes were present but never seen together. Elsewhere in the valley the numbers were up and many specimens were photographed.

 

COMMON HAWKER Aeshna juncea

This not so common insect was not seen at all during the course of any population survey visits.

RUDDY DARTER Sympetrum sanguineum

Numbers were down on last year but it was still the second best year to date. Present from the second week in August, one male was still to be found on the 30th of October. The population peaked at the end of August, beginning of September, but never reached double figures on any given day. The hide charts recorded two examples both on the same day, the 9th of September.

COMMON DARTER Sympetrum striolatum

There was a steady emergence of this species during the last week of June, first week of July. Good numbers of exuvia were found, as were the corresponding newly emerged insect. The number present dropped dramatically in mid July only to recover as the mature adults returned to the water to breed around the second and third weeks in August. The numbers, though down on last year, are comparable with those of 1998 & 99. A total of 14 males, females and copulating pairs were recorded on the last day of the years survey i.e. 30th October. Steve & Sheila Farmer reported the presence of several pairs of darters on the wing on the 9th November.


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CHAPTER 7

Mammal Report for 2001

Recorder Katrina Slocombe

Roe deer continue to be the most obvious mammal on the reserve and nearby fields but the FMD outbreak prevented observation of any young roe in the early summer period. Stoats are occasionally seen on the surrounding footpaths but the water vole, as our most endangered mammal, has again been absent from reserve and river. This is not unexpected due to the continued presence of mink: as reported in the August 2001 Newsletter, work party members observed a mink on Long Island under the upturned Moor Green boat where it was consuming a fish. The anti-mink fence around Tern Island may deter the mink and encourage it to go elsewhere for more 'easy meals'!

Although no small mammal surveys were possible during the period, partly due to FMD, it is hoped that populations are being maintained, certainly hunting by owls on the site throughout the year would suggest that they are continuing to source the reserve grasslands for their mammal prey. The presence of harvest mice is evident from several breeding nests of woven grasses discovered on work party days.

Steve Bailey is continuing a series of bat surveys throughout the Blackwater Valley and results will be presented to members, as they become available.

Surveys and observations will continue in the coming year and members are encouraged to send all sightings of wild and feral mammals to Katrina Slocombe, 28 Green Lane, Blackwater, Camberley, Surrey. GU17 9DH or pass them to any member of the committee.


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CHAPTER 8

Reptile Report for 2001

Peter Scott

This is more a statement of intent than a true report.

As most members will be aware, in February this year we built a reptile hibernaculum about 20 metres back from the north shore of Colebrook Lake North. This is intended to encourage population growth of this animal group, small numbers of which (mostly grass snakes) have been seen on site from time to time. Clearly we should follow this up with some effort to monitor reptile numbers, if only to check whether our installation has been effective. To that end, I have 'been volunteered' as the Group's reptile recorder.

A number of small sheets of corrugated iron have been distributed along the north banks of Colebrook and Grove Lakes, to (hopefully) act as attractive basking sites and to form a focus for surveys.

In addition to making systematic surveys of regular sites, I will be keeping records of 'casual sightings' anywhere on the reserve or the surrounding paths. Therefore I should be grateful if members would let me know of any reptiles they see. The details that I should (ideally) like to know are:

  • date and time of sighting;

  • species and numbers seen;

  • location - e.g. "close to Colebrook Hide", if possible including a grid reference;

  • observer's name;

  • any other comments - e.g. sex of the animal (difficult to tell for most species without a very close look, of course), behaviour (basking, foraging,...).

However, any report, no matter how incomplete, will be welcome. Even "'some sort of snake (species unknown)" is useful information.

Please send reports by post, phone or email to Peter Scott:

Address:      5 Globe Farm Lane, Blackwater, Camberley, Surrey, GU17 0DZ
Telephone:   01252 878205
Email:          ppscott(at)aol.com.


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CHAPTER 9

 A Survey of Aquatic and Wetland Plants, August - September 2001

Chris Hall

The on-going botanical surveying and monitoring at Moor Green has been continued with a survey of the aquatic and wetland plants, carried out by Chris Hall in August 1 September 2001. This follows up the 1991 survey and provides the opportunity to assess the botanical and conservation value of the wetland plant communities.

Overall the survey shows that, under the current management regime, the flora of the site continues to develop and improve and it is now a locally, and could soon be a nationally, significant site. Chris has identified one, possibly two, national Biodiversity Action Plan priority species, four that are regionally scarce and a further six which are locally significant. The survey has also highlighted the continuing issue of alien species on the reserve, Crassula helmsii in particular.

The following is a summary of the major findings of the survey. The full report is held in the Moor Green Lakes Group library.

Species Abundance
  •  

A total of 76 wetland species were recorded in 2001. These consisted of 13 submerged of floating species, 30 emergent and 33 riparian species. Five others were found in 1991 which were not re-found in 2001, making a total of 81 overall. In 1991 only 41 species were recorded (see Table 1).

Species Diversity
  •  

The diversity of the wetland flora of the reserve continues to improve. English Nature uses a criteria of 40 submerged, floating and emergent species (that is, not including riparian species which also occur in a number of other habitats) as an indication of a 'diverse' wetland habitat a status reached by only 2% of wetland sites in Great Britain. Using this criterion, and excluding alien species, the Moor Green Lakes as a group just qualify with 40 native species found in this survey. As this is based on a single survey, taken at one time of year, regular monitoring through the spring and summer months would almost certainly add a few more.

  •  

 

Colebrook Lake North was the most diverse with 32 species, Chris Hall knows of only 12 wetland sites in the area that support more than 30 species. 30 species were found on Colebrook Lake South and 26 on Grove Lake. The figure for Grove in particular is probably an underestimate as, because of logistical problems, it was not possible to carry out a survey of the open water.
Scarce and Uncommon Species
  •  
Pillwort Pilularia blobulifera A National BAP Priority Species

A small fern of pond margins and shallow pans found in lowland areas throughout the British Isles. It is an opportunist requiring areas of bare mud or gravel in shallow water where, under suitable conditions, it may form large populations; However, it is unable to compete for long amongst taller vegetation and will soon decrease unless management or some natural process maintains patches of open habitat.

Found on five sites on the margins of the lakes, two on each of the Colebrook Lakes and one at the eastern end of Grove Lake.

 

  •  
Hair-like pondweed Potamogeton trichoides Nationally Scarce

A pondweed known to colonise new gravel pits and to reappear in old sites after disturbance such as dredging. This record needs to be confirmed in the summer to be certain of the identification.

There are a few modern records from Berkshire or surrounding counties, though it has recently been found in the Basingstoke Canal near Woking and near Aldershot and Hawley in the Blackwater Valley.

 

  •  
Waterwort  Elatine hexandra Regionally Scarce

A small plant of lake margins, growing on seasonally inundated mud or in shallow water. It is widespread at Moor Green Lakes, especially around the north and east margins of Grove Lake where the open habitat is ideal. There are thousands of plants here. It is more localised though still plentiful around parts of Colebrook North Lake but scarce in Colebrook South.

 

  •  

Needle Spike-rush, Eleocharis acicularis Regionally Scarce

At Moor Green Lakes Needle Spike-rash has a similar distribution to waterwort but is more abundant, forming extensive lawns. It may be confused with pillwort but the latter species is usually bright (not dull) green and some stems will be curved or coiled, betraying its place amongst the ferns.

 

  •  

Blunt-leaved Pondweed, Potamogeton obtusifolius Regionally Scarce

Records of this pondweed were widely scattered around the margins of Colebrook North Lake. It was locally plentiful in one place on the west side of Colebrook South Lake. There were no records from Grove Lake but it was locally frequent in 1991 and may well be re-found during a boat survey.

 

  •  

Lesser Pondweed, Potamogeton pusillus Regionally Scarce

Another species which will need confirmation of identification from better quality summer vegetation. However, possible P. pusillus was seen on Colebrook Lake North around Plover and Long Islands.

 

Locally Scarce Species

There were six aquatic and wetland species that are uncommon in the modern countryside generally and particularly in the area surrounding Moor Green Lakes.

  •

Hornwort, Ceratophyllum demersum

  •

Small Pondweed, Potamogeton berchtoldii
  • A Water Crowfoot, Ranunculus sp.
  • Ivy leaved crowfoot, R hederaceus. decreasing in Europe, Britain has special conservation responsibility for this species.
  • Water Purslane, Lythrum portula
  • Fen Bedstraw, Galium allginosum
Alien Species
A total of four alien plant species were found m the survey.
  • Australian Swamp Stonecrop or New Zealand pigmyweed, Crassula helsmii was found to be abundant around almost the entire perimeter and the islands of Colebrook North Lake but less plentiful and more patchy around Colebrook South Lake. At Grove Lake it was only found on the new scrape below the bird hide with almost 50 small patches along some 25 metres of the lakeshore at the south end of the scrape.
Nuttall's Water Thyme, Elodea nuttallii was abundant in all three lakes, as indeed it is throughout the Blackwater Valley.
American Duckweed, Lemna minuta, another North American species, was discovered in one bay of Colebrook South Lake. It is spreading rapidly in southern England.
Orange Balsam, Impatiens capensis also from North America, has been established in the wild in southern England for 175 years. It grows amongst bankside vegetation and has become a problem in some wetlands. It was recorded from Plover Island, Long Island, the margin of Colebrook South Lake and Grove Lake but the only significant population was on the south side of Long Island. The related Himalayan balsam Importers glandulifera is frequent beside the River Blackwater but was not seen within the reserve.


Crassula helmsii is the most abundant alien species on the reserve and the one which poses the greatest threat to the native flora. It became naturalized in Britain in 1956 and began to spread significantly in the 1970s. Since then it has spread rapidly, especially in South East England, where it is of great conservation concern due to its ability to quickly dominate shallow waters and to smother native vegetation. Several of the uncommon species at Moor Green, including pillwort, waterwort and needle spike-like are at risk. It was first recorded on the north margin of Colebrook North Lake in 1991 when it was already locally well established It is now abundant around this lake and has spread to the other two lakes as well. The creation of scrapes for waterfowl also creates ideal habitat for C helmsii to colonize. It is spread by waterfowl, on footwear and on machinery. It is widespread in the Blackwater Valley, the Basingstoke Canal and other wetlands in the region. Even if it were successfully eradicated at Moor Green it would probably re-colonize from nearby sites.

Table 1:  Aquatic and Wetland Plant Species - SPECIES LIST

   

1991

2001

 

Colebrook Grove Lake Total
North South
A. Submerged and Floating Species
Callitriche hamulata Intermediate Water Starwort

a

a a
C. stagnalis Common Water Starwort a a a
Callitriche sp. Water Starwort a a
Ceratophyllum demersum Rigid Hornwort a a Locally scarce
Chara sp Stonewort a a a
Elodea nuttallii Nuttall's Water-thyme a a a a a Established alien
Lemna minor Common Duckweed a a a a
L. minuta American Duckweed a a Established alien
Myriopyllum spicatum Spiked Water Millfoil a a Species needs confirmation
Potarnogeton berchtoldii Small Pondweed a a a a a Infrequently seen in local area
P. natans Broad-leaved Pondweed a
P. obtusifolius Blunt-leaved Pondweed a a a   a Regionally scarce
P. pusillus Lesser Pondweed a a a

Regionally scarce. Species needs confirmation.

P trichoides Hair-like Pondweed   a     a

National BAP priority species. Identification needs confirmation

Ranunculus peltatus Pond Water Crowfoot a a

Infrequently seen in local area. Species needs confirmation

Total 7(6) 10 (9) 8(6) 4(3) 13 (11)

Figures in brackets exclude established alien species

B. Emergent species
Agrostis stolonifera Creeping Bent a a a a

Alisma plantago-aguatica Water Plantain a a a a a

Apium nodiflorum Fool's Watercress a a a

Crassula helmsii Australian Swamp Stonecrop a a a a a

Established alien

Elatine hexandra Waterwort a a a a a

Regionally scarce

Eleocharis acicularis Needle Spikerush a a a a

Regionally scarce

E. palustris Pond Spikerush a a a a

Equisetum uviatile Water Horsetail a a

E. palustre Marsh Horsetail a a a

Galium palustre Marsh Bedstraw a a a a

Glyceria declinata Glaucous Sweet-grass a

G, fluitans Floating Sweet-grass a a a a a

Hydrocotyle vulgaris Marsh Pennywort a a a a

Iris pseudacorus Yellow Flag a a a

Juncus effusus Soft Rush a a a a a

Lythrum portula Water Purslane a a a a

Infrequently seen in local area

Mentha aquatica Water Mint a a a a a

Myositis laxa Tufted Forget-me-not a

M. scorpioides Water Forget-me-not a a a a a

Myosoton aquaticum Water Chickweed a a a a a

Nasturtium officinale Watercress a a

Species needs confirmation

Oenanthe crocala Hemlock Water Dropwort a a a a

Persicaria hydropiper Water Pepper a a a a a

Phalaris arundinacea Reed Canary Grass   a a a a

 

Phragmites australis Reed     a   a

 

Pilularia globulifera Pillwort   a a a a

National BAP priority species

Ranunculus flammula Lesser Spearwort a a a a a

 

R. hederaceus Ivy-leaved Crowfoot a     a a

Infrequently seen in local area

R. sceleratus Celery-leaved Buttercup   a   a a

 

Rorripa amphibia Great Yellow Cress     a   a

 

Sparganium erectum Branched Bur-reed a a a a a

 

Typha latifolia Common Reedmace a a a a a

 

Veronica beccabunga Brooklime a        

 

Total   18 (17) 24 (23) 25 (24) 24 (23) 30 (29)

Figures in brackets exclude established alien species

C. Riparian species
Agrostis canina Velvet Bent   a     a  
Angelica sylvestris Angelica   a a   a  
Bidens cernua Nodding Bur-marigold a a a a a  
B. tripartita Trifid Bur-marigold a a a a a  
Cardamine pratensis Lady's Smock   a a a a  
Carex ovalis Oval Sedge   a     a  
C. remota Remote Sedge     a   a  
Cirsium palustre Marsh Thistle a a     a  
Deschampsia cespitosa Tufted Hair Grass   a a a a  
Epilobium hirsutum Great Willowherb a a a a a  
Epilobium parviflorum Hoary Willowherb a a     a  
Eupatorium cannabinum Hemp Agrimony a a   a a  
Filipendula ulmaria Meadowsweet   a a a a  
Galium uliginosum Fen Bedstraw     a a a Infrequently seen in local area
Impatiens capensis Orange Balsam a a a a a Established alien
Isolepsis setacea Bristle Club-rush a a     a  
Juncus acutiflorus Sharp-fruited Rush   a a a a  
J. articulatus Jointed Rush   a     a  
J bufonius Toad Rush a          
Lotus pedunculatus Marsh Birds-foot Trefoil a a a a a  
Lychnis flos-cuculi Ragged Robin     a   a  
Lycopus europaeus Gipsywort a a a a a  
Lysimachia nummularia Creeping Jenny     a   a  
L. vulgaris Yellow Loosestrife a a a   a  
Lythrum salicaria Purple Loosestrife a a a a a  
Persicaria lapathifolium Pale Persicaria   a     a  
Potentilla erecta Tormentil a   a   a  
Pulicaris dysenterica Fleabane   a     a  
Rorripa palustris Marsh Yellow Cress a a a a a  
Scirpus sylvaticus Wood Club-rush     a   a  
Scrophularia auriculata Water Figwort   a a a a  
Scutellaria galericulata Skullcap   a a   a  
Solanum dulcamara Bittersweet a a a a
Stachys pahustris Marsh Woundwort a a a
Total 16 (15) 25 (24) 24 (23) 17 (16) 33 (32) Figures in brackets exclude established alien species

Table 2:     Total number of aquatic and Wetland plant species

   Category

ALL SPECIES

EXCLUDING ALIEN SPECIES

1991

2001

1991

2001

Colebrook Grove Lake Total Colebrook Grove Lake Total
North South North South
  • Floating / submerged

7

10

8

4

13

6

9

6

3

11

  • Emergent

18

24

25

24

30

17

23

24

23

29

  'Wetland' Subtotal

25

34

33

28

43

23

32

30

26

40

 

 

 

 

 

 

 

 

 

 

 

  • Riparian

16

25

24

17

33

15

24

23

16

32

    TOTAL

41

59

57

45

76

38

56

53

42

72


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CHAPTER 10

BEETLES AND SPIDERS

Bob Merritt
Introduction Ken Crick

Bob was going to provide Moor Green with a report on his findings but owing to a hoax computer virus scare, which caused a lot of grief for him and his computer, this has proved impossible to achieve. However prior to his computer problems he did supply us with a comprehensive listing of those Beetles & Spiders he found on our Reserve.

He visited the reserve on both the 25 & 27 of April recording 199 different insects with approximately 110 new to our known species list. Several of the spiders could be identified to genus only owing to their immaturity. They are included in the list where it is clear they are additional species, albeit incompletely identified.

Several of the beetles, Bob felt, needed double checking by another authority and subsequently two amendments were made. These appear as hand written changes to the original text. [incorporated in web version]

From a personal standpoint it is gratifying to have an independent record of Dragonfly & Damselfly larva all of which I have claimed in the past to be breeding on site.

We are indebted to Bob giving his time and specialist knowledge to the reserve, for free, especially as he has to travel from Chesterfield in Derbyshire.

Moor Green Lakes Nature Reserve: details of visit by R. Merritt on 25th and 27th April 2001.
(first draft)

Table 1. Location details, and date of visits

LOCATION GRID DATE OF VISIT SITE DESCRIPTION
Car-park SU 805627 27-Apr-01 sandy, gravely car-park
Colebrook Cut SU 809622 25-Apr-01 channel between 2 lakes, with Sparganium, ochrous ooze, and marginal Juncus, grasses and Salix. Some central water flow
Colebrook Lake North SU 805626 25-Apr-01 lake in former gravel pit with marginal Sparganium, Crassula helmsii and decaying plant litter
Colebrook lake opposite Goose Island SU 809623 25-Apr-01 lake in former gravel pit, with marginal Juncus, Eleocharis and Mentha aquatica
Grove lake SU 815622 27-Apr-01 sheltered bay of lake in former gravel pit, with Juncus, Phalaris, Alisma and grasses
Grove Lake (adjacent land) SU 814622 27-Apr-01 rough grassland, hawthorn scrub, gorse, and nettle bed
River Blackwater

SU 809622

SU 807621

25-Apr-01 part-shaded, medium-slow river with marginal rushes

Table 2. Locations, with species and their national statuses

LOCATION SPECIES FAMILY COMMON NAME GB-STATUS
Car-park Staphylinus dimidiaticornis Staphylinidae a rove beetle Local
Colebrook Cut Agabus bipustulatus Dytiscidae a diving water beetle Common
Colebrook Cut Agabus sturmii Dytiscidae a diving water beetle Common
Colebrook Cut Agonum albipes Carabidae a ground beetle Common
Colebrook Cut Anacaena globulus Hydrophilidae a scavenger water beetle Common
Colebrook Cut Anacaena limbata Hydrophilidae a scavenger water beetle Common
Colebrook Cut Cercyon convexiusculus Hydrophilidae a scavenger water beetle Local
Colebrook Cut Cercyon ustulatus Hydrophilidae a scavenger water beetle Notable/Nb
Colebrook Cut Dromius linearis Carabidae a ground beetle Common
Colebrook Cut Dytiscus marginalis Dytiscidae Great Diving Beetle Common
Colebrook Cut Hydrobius fuscipes Hydrop ilidae a scavenger water beetle Common
Colebrook Cut Hydrochus angustatus Hydrochidae a scavenger water beetle Notable/Nb
Colebrook Cut Hydroporus incognitus Dytiscihae a diving water beetle Local
Colebrook Cut Hydroporus memnonius Dytiscihae a diving water beetle Common
Colebrook Cut Hydroporus neglectus Dytiscihae a diving water beetle Notable/Nb
Colebrook Cut Mecinus pyraster Curculionidae a weevil Common
Colebrook Cut Ocyusa maura Staphylinidae a rove beetle Local
Colebrook Cut Paederus riparius Staphylinidae a rove beetle Local
Colebrook Cut Stenus cicindeloides Staphylinidae a rove beetle Local
Colebrook Cut Stenus impressus Staphylinidae a rove beetle Common
Colebrook Cut Stenus nitidiusculus Staphylinidae a rove beetle Common
Colebrook Cut Stenus solutus Staphylinidae a rove beetle Local
Colebrook Cut Gerris lacustris Gerridae Common Pondskater Common
Colebrook Cut Gerris odontogaster Gerridae Toothed Pondskater Common
Colebrook Cut Gerris thoracicus Gerridae a pondskater Common
Colebrook Cut Hydrometra stagnorum Hydrometridae Water Measurer Common
Colebrook Cut Nepa cinerea Nepidae Water Scorpion Common
Colebrook Cut Velia caprai Veliidae Common Water Cricket Common
Colebrook Cut Asellus aquaticus Asellidae a water slater Common
Colebrook Cut Bathyphantes approximatus Linyphiidae a money spider Local
Colebrook Cut Clubiona sp. Clubionidae a foliage spider
Colebrook Cut Gnathonarium dentatum Linyphiidae a money spider Common
Colebrook Cut Hypomma ituberculatum Linyphiidae a money spider Common
Colebrook Cut Linyphia clathrata Linyphiidae a money spider Common
Colebrook Cut Lophomma punctatum Linyphiidae a money spider Local
Colebrook Cut Metellina segmentata Metidae an orb-weaver spider Common
Colebrook Cut Pardosa amentata Lycosidae a wolf spider Common
Colebrook Lake North Anacaena limbata. Hydrophilidae a scavenger water beetle Common
Colebrook Lake North Coelostoma orbiculare Hydrophilidae a scavenger water beetle Common
Colebrook Lake North Haliplus lineolatus Haliplidae a crawling water beetle Local
Colebrook Lake North Helochares lividus Hydrophilidae a scavenger water beetle Local
Colebrook Lake North Hyphydrus ovatus Dytiscidae a diving water beetle Common
Colebrook Lake North llybius fenestratus Dytiscidae a diving water beetle Notable/Nb
Colebrook Lake North Gerris lacustris Gerridae Common Pondskater Common
Colebrook Lake North llyocoris cimicoides Naucoridae Saucer Bug Common
Colebrook Lake North Nepa cinerea Nepidae Water Scorpion Common
Colebrook Lake North Coenagrion puella Coenagriidae Azure Damselfly Common
Colebrook Lake North Hypomma bituberculatum Linyphiidae a money spider Common
Colebrook Lake North Larinioides cornutus Araneidae an orb-weaver spider Common
Colebrook Lake North Pardosa amentata Lycosidae a wolf spider Common
Colebrook Lake North Philodromus cespitum Philodromidae a running crab spider Common
Colebrook Lake North Pirata sp. Lycosidae a wolf spider
Colebrook Lake North Tetragnatha montana Tetragnathidae a long-jawed spider Local
Colebrook Lake North Tetragnatha striata Tetragnathidae a long-jawed spider Notable/Nb
Colebrook Lake North Theridion sisyphium Theridiidae a comb-footed spider Common
Grove Lake Agonum albipes Carabidae a ground beetle Common
Grove Lake Agonum gracile Carabidae a ground beetle Local
Grove Lake Anacaena bipustulata Hydrophilidae a scavenger water beetle Notable/Nb
Grove Lake Anacaena globulus Hydrophilidae a scavenger water beetle Common

Grove Lake

Anisosticta novemdecimpunctata

Coccinellidae

19-spot Ladybird

Local

Grove Lake Anotylus rugosus Staphylinidae a rove beetle Common
Grove Lake Atheta fungi Staphylinidae a rove beetle Common
Grove Lake Bembidion guttula Carabidae a ground beetle Common
Grove Lake Cercyon convexiusculus Hydrophilidae a scavenger water beetle Local
Grove Lake Ceutorhynchus melanostictus Curculionidae a weevil Local
Grove Lake Coccidula rufa Coccinellidae a ladybird Common
Grove Lake Coelostoma orbiculare Hydrophilidae a scavenger water beetle Common
Grove Lake Dryops luridus Dryopidae a long-toed water beetle Common
Grove Lake Enochrus testaceus Hydrophilidae a scavenger water beetle Local
Grove Lake Eutrichapion punctigerum Apionidae a seed weevil Local
Grove Lake Gyrinus marinus Gyrinidae a whirligig water beetle Common
Grove Lake Haliplus confinis Haliplidae a crawling water beetle Common
Grove Lake Haliplus flavicollis Haliplidae a crawling water beetle Local
Grove Lake Haliplus fulvus Haliplidae a crawling water beetle Local
Grove Lake Helochares lividus Hydrophilidae a scavenger water beetle Local
Grove Lake Helophorus brevipalpis Helophoridae a scavenger water beetle Common
Grove Lake Hydrobius fuscipes Hydrophilidae a scavenger water beetle Common
Grove Lake Hydroporus palustris Dytiscidae a diving water beetle Common
Grove Lake Hyphydrus ovatus Dytiscidae a diving water beetle Common
Grove Lake Laccobius bipunctatus Hydrophilidae a scavenger water beetle Common
Grove Lake Laccobius minutus Hydrophilidae a scavenger water beetle Local
Grove Lake Laccophilus hyalinus Dytiscidae a diving water beetle Common
Grove Lake Laccophilus minutus Dytiscidae a diving water beetle Local
Grove Lake Lesteva heeri Staphylinidae a rove beetle Common
Grove Lake Meligethes aeneus Nitidulidae Common Pollen Beetle Common
Grove Lake Noterus clavicornis Noteridae a water beetle Local
Grove Lake Ocyusa maura Staphylinidae a rove beetle Local
Grove Lake Paederus riparius Staphylinidae a rove beetle Local
Grove Lake Phaedon armoraciae Chrysomelidae Mustard Beetle Common
Grove Lake Rhantus exsoletus Dytiscidae a diving water beetle Local
Grove Lake Stenus boops Staphylinidae a rove beetle Common
Grove Lake Stenus cicindeloides Staphylinidae a rove beetle Local
Grove Lake Stenus ossoum Staphylinidae a rove beetle Local
Grove Lake Stenus latifrons Staphylinidae a rove beetle Common
Grove Lake Stenus nitidiusculus Staphylinidae a rove beetle Common
Grove Lake Stenus butrintensis Staphylinidae a rove beetle Notable/Nb
Grove Lake Thryogenes festucae Curculionidae a weevil Local
Grove Lake Corixa dentipes Corixidae a waterboatman Local
Grove Lake Corixa panzeri Corixidae a waterboatman Local
Grove Lake Gerris lacustris Gerridae Common Pondskater Common
Grove Lake Microvelia pygmaea Veliidae lesser water-cricket Notable/Nb
Grove Lake Microvelia reticulata Veliidae a lesser water-cricket Common
Grove Lake Nepa cinerea Nepidae Water Scorpion Common
Grove Lake Notonecta glauca Notonectidae Common Backswimmer Common
Grove Lake Notonecta marmorea Notonectidae a backswimmer Common
Grove Lake Sigara distincta Corixidae a waterboatman Common
Grove Lake Sigara dorsalis Corixidae a waterboatman Common
Grove Lake Sigara falleni Corixidae a waterboatman Common
Grove Lake Sigara fossarum Corixidae a waterboatman Common
Grove Lake Sigara lateralis Corixidae a waterboatman Common
Grove Lake Sigara nigrolineata Corixidae a waterboatman Common
Grove Lake Coenagrion puella Coenagriidae Azure Damselfly Common
Grove Lake Ischnura elegans Coenagriidae Blue-tailed Damselfly Common
Grove Lake Orthetrum cancellatum Libellulidae Black-tailed Skimmer Local
Grove Lake Bathyphantes approximatus Linyphiidae a money spider Local
Grove Lake Bathyphantes gracilis Linyphiidae a money spider Common
Grove Lake Clubiona phragmitis Clubionidae a foliage spider Local
Grove Lake Enoplognatha ovata Theridiidae a comb-footed spider Common
Grove Lake Gnathonarium dentatum Linyphiidae a money spider Common
Grove Lake Hypomma bituberculatum Linyphiidae a money spider Common
Grove Lake Lophomma punctatum Linyphiidae a money spider Local
Grove Lake Oedothorax gibbosus Linyphiidae a money spider Common
Grove Lake Oedothorax retusus Linyphiidae a money spider Common
Grove Lake Pachygnatha clercki Tetragnathidae a long-jawed spider Common
Grove Lake Pardosa amentata Lycosidae a wolf spider Common
Grove Lake Pirata sp. Lycosidae a wolf spider
Grove Lake Tetragnatha extensa Tetragnathidae a long-jawed spider Common
Grove Lake Tetragnatha montana Tetragnathidae a long-jawed spider Local
Grove Lake Trochosa terricola Lycosidae a wolf spider Common
Grove Lake (adj.land) Agriotes obscurus Elateridae a click beetle Common
Grove Lake (adj.land) Altica lythri Chrysomelidae a leaf beetle Common
Grove Lake (adj.land) Apion haematodes Apionidae a seed weevil Common
Grove Lake (adj.land) Bembidion guttula Carabidae a ground beetle Common
Grove Lake (adj.land) Ceutorhynchus pollinarius Curculionidae a weevil Common
Grove Lake (adj.land) Cidnorhinus quadrimaculatus Curculionidae Small Nettle Weevil Common
Grove Lake (adj.land) Coccinella septempunctata Coccinellidae Seven-spot Ladybird Common
Grove Lake (adj.land) Deporaus betulae Attelabidae Birch Leaf Roller Beetle Common
Grove Lake (adj.land) Dromius linearis Carabidae a ground beetle Common
Grove Lake (adj.land) Eutrichapion punctigerum Apionidae a seed weevil Local
Grove Lake (adj.land) Longitarsus dorsalis Chrysomelidae a leaf beetle Notable/Nb
Grove Lake (adj.land) Meligethes nigrescens Nitidulidae a pollen or sap beetle Common
Grove Lake (adj.land) Mycetoporus lepidus Staphylinidae a rove beetle Common
Grove Lake (adj.land) Oulema rufocyanea Chrysomelidae Cereal Leaf Beetle Common
Grove Lake (adj.land) Philonthus cognatus Staphylinidae a rove beetle Common
Grove Lake (adj.land) Phyllobius pyri Curculionidae Common leaf Weevil Common
Grove Lake (adj.land) Rhyzobius litura Coccinellidae a ladybird Common
Grove Lake (adj.land) Sitona lepidus Curculionidae a weevil Common
Grove Lake (adj.land) Sitona lineatus Curculionidae Pea and Bean Weevil Common
Grove Lake (adj.land) Stenus clavicornis Staphylinidae a rove beetle Common

Grove Lake (adj.land)

Subcoccinella vigintiquattuorpunctata

Coccinellidae

24-spot Ladybird

Common
Grove Lake (adj.land) Tachyporus hypnorum Staphylinidae a rove beetle Common
Grove Lake (adj.land) Tychius picirostris Curculionidae a weevil Common
Grove Lake (adj.land) Xantholinus longiventris Curculionidae a rove beetle Common
Grove Lake (adj.land) Alopecosa pulverulenta Lycosidae a wolf spider Common
Grove Lake (adj.land) Clubiona sp. Clubionidae a foliage spider
Grove Lake (adj.land) Dictyna arundinacea Dictynidae a mesh webbed spider Common
Grove Lake (adj.land) Enoplognatha ovata Theridiidae a comb-footed spider Common
Grove Lake (adj.land) Erigone atra Linyphiidae a money spider Common
Grove Lake (adj.land) Gongylidiellum vivum Linyphiidae a money spider Common
Grove Lake (adj.land) Larinioides cornutus Araneidae an orb-weaver spider Common
Grove Lake (adj.land) Milleriana inerrans Linyphiidae a money spider Local
Grove Lake (adj.land) Oedothorax fuscus Linyphiidae a money spider Common
Grove Lake (adj.land) Pachygnatha degeeri Tetragnathidae a long-jawed spider Common
Grove Lake (adj.land) Pardosa amentata Lycosidae a wolf spider Common
Grove Lake (adj.land) Philodromus cespitum Philodromidae a running crab spider Common
Grove Lake (adj.land) Pisaura mirabilis Pisauridae Tent Spider Common
Grove Lake (adj.land) Tetragnatha extensa Tetragnathi a long-jawed spider Common
Grove Lake (adj.land) Tetragnatha montana Tetragnathidae a long-jawed spider Local
Grove Lake (adj.land) Theridion bimaculatum Theridiidae a comb-footed spider Common
Grove Lake (adj.land) Theridion sisyphium Theridiidae a comb-footed spider Common
Grove Lake (adj.land) Xysticus sp. Thomisidae a crab spider
opp. Goose Island Acilius sulcatus Dytiscidae a diving water beetle Common
opp. Goose Island Agabus sturmii Dytiscidae a diving water beetle Common
opp. Goose Island Anacaena bipustulata Hydrophilidae a scavenger water beetle Notable/Nb
opp. Goose Island Anacaena limbata Hydrophilidae a scavenger water beetle Common
opp. Goose Island Anacaena lutescens Hydrophilidae a scavenger water beetle Common
opp. Goose Island Dryops luridus Dryopidae a long-toed water beetle Common
opp. Goose Island Enochrus testaceus Hydrophilidae a scavenger water beetle Local
opp. Goose Island Haliplus fulvus Haliplidae a crawling water beetle Local
opp. Goose Island Haliplus lineolatus Haliplidae a crawling water beetle Local
opp. Goose Island Haliplus ruficollis Haliplidae a crawling water beetle Common
opp. Goose Island Hygrobia hermanni Hygrobiidae Squeak Beetle Local
opp. Goose Island Hyphydrus ovatus Dytiscidae a diving water beetle Common
opp. Goose Island llybius fenestratus Dytiscidae a diving water beetle Notable/Nb
opp. Goose Island Laccobius minutus Hydrophilidae a scavenger water beetle Local
opp. Goose Island Laccophilus hyalinus Dytiscidae a diving water beetle Common
opp. Goose Island Laccophilus minutus Dytiscidae a diving water beetle Local
opp. Goose Island Noterus clavicornis Noteridae a water beetle Local
opp. Goose Island Rhantus exsoletus Dytiscidae a diving water beetle Local
opp. Goose Island Gerris odontogaster Gerridae Toothed Pondskater Common
opp. Goose Island Hydrometra stagnorum Hydrometridae Water Measurer Common
opp. Goose Island Ilyocoris cimicoides Naucoridae Saucer Bug Common
opp. Goose Island Nepa cinerea Nepidae Water Scorpion Common
opp. Goose Island Notonecta glauca Notonectidae Common Backswimmer Common
opp. Goose Island Plea minutissima Pleidae Lesser Backswimmer Common
opp. Goose Island Sigara distincta Corixidae a waterboatman Common
opp. Goose Island Ischnura elegans Cooenagriidae  Blue-tailed Damselfly Common
opp. Goose Island Orthetrum cancellatum Libellulidae Black-tailed Skimmer Local
opp. Goose Island Pyrrhosoma nymphula Coenagriidae Large Red Damselfly Common
River Blackwater Calopteryx splendens Calopterygidae Banded Demoiselle Local


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CHAPTER 11

REPORT FOR 2001 on the REED BED PROJECT

Steve Farmer

The extraction of gravel by RMC Aggregates (Southern) Ltd. from the Manor Farm site, immediately to the west of the Moor Green Nature Reserve, is now well under way. As the gravel extraction is completed the land will be progressively restored. This will take about 10 years to complete. Although the details have not been finalised the initial plans are well advanced. The major pail of the site will be restored as a nature reserve with smaller parts returned to agriculture or used as amenity land It is envisaged that the nature reserve will include three large reed beds with another large shallow lake with reedy margins. The existing Colebrook Cut will be reinstated but on a slightly different course. Water from this Cut will be fed via sluices through the reed beds.

During the next couple of years the Moor Green Lakes Group, in co-operation with RMC will set up a small pilot reed bed. This will be used to investigate which methods of reed propagation will be most suitable for planting up the new reed beds. Several methods are available such as sowing seed directly, raising plants from seed in pots for planting out or taking stem cuttings. The most suitable planting medium will also be established. The pilot reed bed will be set up at the southeast corner of the Manor Farm site, close to the river and just west of Colebrook South Lake. A temporary water supply will be drawn from the diverted Colebrook Col The pilot reed bed is unlikely to be available for tests to start for at least a year.

In the meantime a Reed Bed Project lead by Ken Crick and Steve Farmer, has already been set up. The first objective has been to establish a reliable source of reed seed. These seed will be used to raise plants for the pilot reed bed. Ideally they should be obtained from a local source. During the late autumn and winter panicles of ripe seed of the common reed (Phragmites australis) were collected from 7 different sites. Two of these were very local, being the small reed bed close to the Colebrook hide and the Watersports Lake near Moulsham Lane. Seed were also collected from Fleet Pond, Lakeside Park near Ash and Greywell Fen. In addition seed were collected from two sites much further away, at Arundel in Sussex and Charmouth in Dorset.

Samples of 100 seed were extracted from single panicles. The seed were soaked in cold water overnight. The seed were then sown on the surface of pots of steam sterilized garden loam. The pots were put m a heated propagating box for periods between 8 and 19 days. The soil was kept saturated by standing the pots in containers of water. The propagating box was maintained at a temperature between 18 and 31C (most of the time between 21 and 28C). Germination of viable seed was usually achieved between 1 and 8 days.

A total of 33 samples from the 7 sites were tested. The germination rate varied markedly from zero to 47% for an exceptionally good sample from Arundel. Combining the results for each of the sites showed that the best 3 sites were Arundel, Fleet Pond and Lakeside Park (in descending order of average germination rate). A further test was then conducted using larger samples extracted from a large number of panicles (not used in the previous trials) for each of these three sites. These results showed that Fleet Pond seed had a higher germination rate than Arundel seed with Lakeside Park again lying third.

Finally a trial was conducted using the 5 best individual panicle samples to establish whether the previous results were repeatable. The germination rates were lower in all cases suggesting that the viability of the seed had started to deteriorate in storage.

This series of trials has yielded a number of useful conclusions. The best samples of seed were obtained from large reed beds such as Fled Pond and Arundel. This may reflect the abundance of pollen available for pollination. The final set of trials suggested that the seed may begin to deteriorate unless kept cold and dry, so that storage in a cold, well ventilated garden shed may be necessary.

The next stage in this project will be to raise a small number of pots of seedlings in shallow troughs of water to find out how long it takes to raise plants which are large enough to be planted out in the pilot reed bed. We also intend to try to raise stem cuttings during this summer. Hopefully we will then be in a position to start trials in the field in about a year's time.


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APPENDIX A

 PROFILE OF THE RESERVE

The Moor Green Lakes 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 RMC Aggregates (Southern) Ltd, Blackwater Valley Countryside Service 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 H. The necessary costs of the Group not covered by membership subscriptions are met by RMC. 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 RMC 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 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 SU805628). The shortest access to the Grove Lake hide is from the Rambler's Cat 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 2001

 

LITTLE GREBE Resident and winter visitor. A good breeding season with five pairs rearing a total of at least 11 young. One pair bred on the reserve. A maxima of 18 were recorded on Sept. 15th.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

9

5

3

5

4

7

6

9

18

8

6

6

GREAT CRESTED GREBE Common resident. A maxima of 20 were recorded on Jan. 16th. A total of five pairs were present during the summer, three pairs successfully rearing a total of 3 young.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

20

10

-

9

10

8

7

13

9

16

17

16

CORMORANT Common winter visitor that oversummers in small numbers. Recorded in all months with maximum count of 47 on Dec. 12th
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

33

32

13

7

4

3

2

5

23

9

20

47

LITTLE EGRET Scarce visitor. Two records; One on Jul. 17th (MW) and presumably the same bird on Jul. 20th (GR). Recorded in three of the last four years reflecting the increased numbers in southern England.

GREY HERON Common resident.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

1

4

3

2

7

3

5

12

7

2

4

5

MUTE SWAN Common resident and winter visitor. Two pairs bred rearing a total of 8 young.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

12

7

- -

12

6

18

23

26

48

63

40

GREYLAG GOOSE Regular visitor. Recorded between Apr.7th and Sept.2nd with a maximum of four on Apr. 14th.

SNOW GOOSE Common resident, with birds from the nearby free flying flock regularly visiting the site. In the early and late winter periods up to 17 (including 4 first-winters) and 16 (including 1 first-winter) birds were present respectively. Although birds were present on the site in summer there was no evidence of breeding.

CANADA GOOSE Abundant resident. The maximum count was of 221 on Dec.22nd.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

86

77

- -

59

149

104

80

16

127

126

221

BARNACLE GOOSE Very common resident. Seven pairs attempted to breed, two of which raised broods but only three young survived due to predation.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

160 159 120 16 14 18 10 114 190 226 236 245

EGYPTIAN GOOSE Occasional visitor. A good year with up to 7 birds (11th present from Feb.6th to 13th and two on Jul. 3rd.

SHELDUCK Irregular visitor. Recorded as follows: 2, Apr.8th, 1, Apr.22nd, 2, Apr. 29th and 2, May 5th.

MANDARIN Summer visitor in increasing numbers, irregular in winter. Breeding birds recorded from Mar.24th. Four pairs bred successfully in nest boxes. In winter there were singletons on Dec. 18th and 23rd.

WIGEON Very common winter visitor. Birds were recorded up to Apr. 7th and from Aug.29th. The maximum count was of 585 on Jan. 16th, a site record (KBB). This is the third year in succession that a site record count has been achieved.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

585* 353 100 1 1 0 0 2 181 188 349 416

GADWALL Common winter visitor, irregular in summer. Two/three males were present until the end of May with up to 2 females but breeding could only be considered possible.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

122 104 12 8 5 1 0 15  31 81 122 121

TEAL Common winter visitor that occasionally summers. One pair was present irregularly through the summer but breeding was not suspected. Recorded in all months except May. The maximum count was 63 on Jan. 13th.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

63 62 8 11 0 2 2 13 35 31 18 33

GREEN WINGED TEAL Very rare visitor. A male was present from Nov. 17th into 2002 (IHB et at) and gave obliging views to many during its stay. This is the first record of this North American duck that has recently been assigned status as a full species.

MALLARD Common resident and winter visitor. Numbers may be declining. The maximum count was 239 on Jan.20th.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

239 30 - - 23 66 42 45 60 56 44 45

PINTAIL Uncommon but regular visitor. The only record was of a pair on Feb.9th (JW, RW).

SHOVELER Common winter visitor. Recorded until Apr.15th and from Sept. 13th.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

14  0 3  2 0 0 0 0 3 3 6 12

POCHARD Common winter visitor, irregular in summer. The maximum was 52 on Dec. 16th.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

46 36 1 0 0 0 6 6 7 7 27 52

TUFTED DUCK Abundant resident and winter visitor. During the summer six broods totalling 25 young were raised. The best breeding success since records began. Winter numbers peaked at 182 on Jan. 16th.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

182 137 - 69 18 35 84 65 35 60 85 127

GOLDENEYE Winter visitor in increasing numbers. In the early year birds were recorded until Apr. 16th. First returns were from Nov. 8th.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

7 6 4 2 0 0 0 0 0 0 4 6

GOOSANDER Common winter visitor. The early winter max at roost was 41 in January. The last early year record was a singleton on Apr.15th. First returns were from Nov.17th. The late year max was 55 on Dec.23rd.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

41 17 4 1   0 0 0 0 0 8 55

RUDDY DUCK Occasional visitor of annual occurrence. One imm male was present from Jan. 19th to 27th (IHB, IT).

HEN HARRIER Rare visitor. A male on was present behind Grove lake on Dec. 12th (KBB). This is only the second record for the site, the first being in 1988.

SPARROWHAWK Common resident that breeds nearby.

BUZZARD Occasional but regular visitor. Three records; singletons on Aug.29th, Sep.29th and Dec.26th.

KESTREL Common resident. One pair reared one young.

HOBBY Common summer visitor. Up to 4 birds were recorded between May 3rd and Oct. 1st.

PEREGRINE Scarce visitor. The only record was of 1 on Jan.6th (IT).

PHEASANT Common resident.

WATER RAIL Winter visitor. Up to three were present in both early and late winter periods.

MOORHEN An abundant resident.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

14 21 - - 15 8 20 16 17 16 5 16

COOT Abundant resident.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

161 67 - - 30 44 65 123 216 288 337 334

LITTLE RINGED PLOVER Summer visitor and passage migrant. Recorded until Jul.30th. Three pairs successfully reared a total of 2 young.

RINGED PLOVER Summer visitor and passage migrant which formerly bred. Three records: 1. Apr.29th, 2, May 20th and 1, Jun. 17th.

GOLDEN PLOVER Uncommon visitor. Two records: 1, Feb.3rd (IT) and 9, Sept.20th (IHB).

LAPWING Common resident and winter visitor. Nine pairs attempted to breed unsuccessfully. The maximum count was of 503 on Feb. 14th.
Monthly maxima:

Jan

Feb

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov

Dec

300 503 250 25 250 18 30 220 200 210 400 450

SANDERLING Infrequent visitor. One in summer plumage was present on Apr.24th (M). The first record since 1997.

TEMMINCK'S STINT Scarce visitor. One well watched bird was present from May 8th to 11th(MW, BB, RC). The earliest record for the site and the first for nine years. The previous three records have all been in May.

CURLEW SANDPIPER Scarce visitor. On the Hampshire part of the complex there was 1 on Sept.22nd (IHB) and 2 on Sept.24th to 25th (IHB). The first records since 1997.

DUNLIN Regular passage migrant. Singletons were recorded on 10 dates between Apr.26th and Sept.25th.

RUFF Infrequent visitor. One was present on Sept.25th (IHB).

COMMON SNIPE Common passage migrant and winter visitor. Recorded until May 6th and from Aug.4th.

BLACK TAILED GODWIT Scarce visitor. One juvenile was present on the Hampshire pits on Sept. 23rd (JMC et al). Recorded in three of the last five years.

REDSHANK Summer visitor and passage migrant. Recorded from Mar.24th. Up to two pairs were present on the reserve until Apr.23rd but breeding was not suspected. Other records were of singletons on May 10th and Jul.27th.

GREENSHANK Regular passage migrant. The records were as follows; 1, Aug.12th, 2, Aug.18th to 24th with one remaining until Sept.4th.

LESSER YELLOWLEGS Very rare visitor. The first record for the site of this North American wader was of a bird on the Hampshire pits in the evening of Jun.12th (GCS, MAS), but was apparently gone the next morning.

GREEN SANDPIPER Winter visitor and common passage migrant. Up to three birds were present in the early and late winter periods. Recorded until Apr.26th and from Jun.28th. Records were mainly of 1 to 3 birds, with a maxima of 7 on Sept.1st and 8 on Aug.25th.

COMMON SANDPIPER Common passage migrant. In spring the records were of 1/3 between Apr.16th and May 28th. Returns were from Jun.30th to Oct.8th (maximum 6 on Aug.25th).

TURNSTONE Uncommon visitor. One on May 10th (RJG) was the first since 1997.

MEDITERRANEAN GULL Uncommon visitor. Two records: Single first-winters on Mar.24th (IHB) and Nov.18th (IT, GCS).

BLACK BEADED GULL Very common visitor. Recorded in all months. The largest count was of 224 on Sept.24th.

COMMON GULL Common winter visitor. The maximum count was of 236 on Mar.24th.

LESSER BLACK BACKED GULL Very common visitor. Birds roosted regularly on the Hampshire part of the site from late summer with a maximum of 570 on Sept.22nd.

HERRING GULL Common winter visitor but in reduced numbers. Small numbers roosted occasionally with Lesser Black Backed Gulls.

YELLOW LEGGED HERRING GULL Regular visitor of annual occurrence. Records of 1 adult, Aug.24th, 1 adult and 1 second year on Sept.24th, 6 adults roosting on Sept.22nd and 1 adult, Sept.29th.

CASPIAN GULL Very rare visitor. One adult and one second-winter on Oct. 14th (JMC, GCS). The first site records of this race of Herring Gull, widely considered as a full species.

GREAT BLACK BACKED GULL Frequent winter visitor with numbers of records declining. Records as follows: 1, Aug. 12th, 2, Sept.2nd and 5, Dec.16th. All records required again for next year.

COMMON TERN Summer visitor and passage migrant. Recorded from Apr.14th. Nine pairs attempted to breed on Tern Island and all were successful rearing a total of 18 young. This is the second successive year that breeding success has exceeded previous records (exceeding 14 young in 2000). Breeding birds and young lingered in the area until Aug. 12th. The only other record was of 3 on Sept. 18th.

BLACK TERN Regular but uncommon passage migrant. Six were present on May 11th (GWB) and one on May 14th (AW). The vast majority of site records are in May.

STOCK DOVE Common resident.

WOOD PIGEON Abundant resident.

COLLARED DOVE Common resident breeding nearby.

TURTLE DOVE Occasional visitor. Three records all of singletons on Jul.1st, Sept.1st and 12th.

RING NECKED PARAKEET Very rare visitor. One was seen and heard as it moved over east on Feb.17th (SF, SFa). The first record for the site of these species whose stronghold is in Surrey to the north east.

CUCKOO Summer visitor. Only one record of a single on Apr.28th, The first year since records began that breeding is considered unlikely.

BARN OWL Formerly bred. Singletons on Dec.28th (GR) and Dec.29th (IT).

LITTLE OWL Moderately common resident. Breeding was successful with two/three territories.

TAWNY OWL Moderately common resident. Breeding was successful with birds present in 2 territories.

SWIFT Numerous summer visitor. Recorded between Apr.28th and Aug.14th.

KINGFISHER Moderately common resident. Two pairs bred successfully.

GREEN WOODPECKER Common resident.

GREAT SPOTTED WOODPECKER Common resident.

WOODLARK Irregular visitor that has bred. One pair bred successfully. The fourth consecutive year that breeding has at least been attempted.

SKYLARK Common resident and winter visitor. Six singing males held territory. The maximum winter count was 17 on Jan.1st.

SAND MARTIN Common summer visitor. Recorded between Mar.24th and Sept.21st. There were 116 nest holes (cf 161 in 2000) on the new workings on the Hants side of the complex.

SWALLOW Common summer visitor. Recorded between Apr.7th and Oct.7th.

HOUSE MARTIN Abundant summer visitor. Recorded between Apr.11th and Oct.10th. Maximum count was 500 on Sept.15th.

MEADOW PIPIT Common winter visitor and passage migrant that has summered.

YELLOW WAGTAIL Moderately common passage migrant that has bred. Singletons recorded in spring on Apr.13th, May 8th, May 12th, and May 17th. In autumn records were of 1, Aug.25th , 3, Sept.8th, 1, Sept.9th, 4, Sept.15th and 1, Sept.24th.

GREY WAGTAIL Moderately common resident. Two pairs bred successfully.

PIED WAGTAIL Common resident and winter visitor.

WREN Abundant resident.

DUNNOCK Common resident.

ROBIN Very common resident.

WHINCHAT Moderately common passage migrant. Only two records; 1, Aug.23rd and 2, Sept.29th.

STONECHAT Irregular resident and passage migrant. In the early winter there were up to 3 present. One/two pairs were present in suitable breeding habitat until late June and breeding was likely though not proven. In the late year 1 or 2 birds were recorded from Sept.23rd.

WHEATEAR Moderately common passage migrant. Three records all in autumn; 2, Aug.19th, 1, Aug.24th and 1, Sept.1st.

BLACKBIRD Common resident.

FIELDFARE Common winter visitor. Recorded until Apr.4th and from Nov.4th. Maximum counts were of 197 on Nov.4th.

SONG THRUSH Common resident.

REDWING Very common winter visitor. Recorded until Mar.24th (max 100 on Feb.3rd) and from Sept.25th.

MISTLE THRUSH Common resident.

SEDGE WARBLER Moderately common summer visitor. Recorded from Apr.7th. Eight singing mates held territory (cf 6 in 2000)

REED WARBLER Moderately common summer visitor. Recorded from Apr.25th. Five singing males held territory.

LESSER WHITETHROAT Summer visitor. Recorded from Apr.28th. One singing male held territory.

WHITETHROAT Very common summer visitor. Recorded between Apr.8th and Sept.8th.

GARDEN WARBLER Very common summer visitor. Recorded between Apr.14th and Aug.18th. At least thirteen singing males held territory.

BLACKCAP Summer visitor and occasional winter visitor. Recorded between Apr.14th and Oct.27th. Twelve singing males held territory.

CHIFFCHAFF Common summer visitor and regular winter visitor. Recorded between Mar.24th and Oct.12th. Six singing males held territory.

WILLOW WARBLER Common summer visitor. Recorded from Apr.7th until Sept.1st. Six singing males held territory.

GOLDCREST Common winter visitor and passage migrant.

SPOTTED FLYCATCHER Regular passage migrant that may breed. The only record was of 2 on Aug.31st.

LONG TAILED TIT Abundant resident.

COAL TIT Uncommon visitor. The only record was of 1 on Sept. 15th.

BLUE TIT Abundant resident.

GREAT TIT Abundant resident.

NUTHATCH Moderately common resident.

TREECREEPER Moderately common resident.

JAY Common resident.

MAGPIE Common resident.

JACKDAW Common resident.

ROOK Regular visitor.

CARRION CROW Common resident.

STARLING Common resident.

HOUSE SPARROW Common resident nearby.

CHAFFINCH
Abundant resident and winter visitor. Maximum count of 80 on Dec.1st.

BRAMBLING Regular winter visitor usually in small numbers. A very good year with a large flock building towards the years end. Three on Oct.27th and Nov.17th prior to a maximum of 100 in December feeding on fields to the west of the reserve.

GREENFINCH Common resident and winter visitor. Maximum count of 20 on Jan. 27th.

GOLDFINCH Very common resident and winter visitor.

SISKIN Common winter visitor. The maximum count was 400 on Nov.17th.

LINNET Moderately common resident and winter visitor. The maximum count was 80 on Jan.20th. Breeding successful.

LESSER REDPOLL Moderately common winter visitor. The maximum count was 30 on several November dates.

BULLFINCH Moderately common resident.

YELLOWHAMMER Resident in small numbers. Two/three singing males held territory. The maximum count was 15 on Feb. 17th.

REED BUNTING Common resident. Approx ten territories were located. The maximum count was 20 on Feb. 17th.

OTHER RECORDS

BAR HEADED GOOSE Records as follows; 2, May 15th, 2, Oct.41 and 5, Oct.5th.

BLACK SWAN One on May 4th.

LIST OF OBSERVERS

B.M.Archer
S.Bailey
B.Bennett
Dr K.B.Briggs
D.Broadley
Dr I.H.Brown
G.Bryant
M.Budden
D.F.Callam
J.M.Clark
Dr M.N.Clilford
R.Crawford
K.Crick
TJ.Crompton
C.Davis
S.Dean
Mrs S.Farmer
S.Farmer (SFa)
T.Fuller
C.R.Gent
N.R.Godden
R.E.Godden
R.J.Godden
C.Good
P.Hollom
Ms D.Housley
M.Hunt
C.Jones
R.Kersham
G.Randall
Mrs C.Rose
G.J.S.Rowland
M.A.Scott
J.B.Sheridan
G.C.Stephenson
J.C.Tanner

Mrs L.D.M.Tanner

C.D.Taylor

M Taylor

A Twyford

M Walford

M Ward

J Westmacott

J E Warren

C White


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APPENDIX C

EVERSLEY GRAVEL PITS (inc MOOR GREEN LAKES)

BIRD SPECIES LIST 1990-2001

Click here to open the spreadsheet with Excel (42Kb)

If you do not have Excel, the following link provides a pdf version

Click here for a pdf version (44Kb)

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

PH SURVEY 2001

Ken Crick

The stimulus for this work came from the strategy meetings held twice a year with RMC Aggregates. At these meetings the acidity / alkalinity of the reserve's water has been a regular topic of conversation. So armed with a Hanna Instruments pHep 3 pH meter borrowed from our friends at the Blackwater Valley Countryside Service and calibration buffers supplied by Dr. Jim Bennett, a survey was undertaken commencing on the 19th June 2001 and for the purpose of this report finishing on the 5th April 2002.

Measurements were taken at 12 locations, at a rate of one per week, per location throughout the summer and autumn reducing to twice per month while the wildfowl were over wintering on the reserve. At each location the water temperature was also recorded. A total of 324 readings for pH were recorded the results of which can be seen on the attached charts.

A reading of 7 represents a neutral condition with those figures below 7 indicating increased acidity as they approach 0 and increasing alkalinity as the value rises above 7. pH is a cheap, easy and rapid indicator to measure. Acidity and alkalinity limits of 4.5 & 9.5 respectively are rarely exceeded within the general run of ordinary freshwater habitats, according to T. T. Macan & E.B. Worthington in their book Life in Lakes and Rivers.

In general the pH throughout most of the reserve's water tended towards an alkaline condition within both the scrapes and main lakes. At 9 of the 12 measurement sites the pH rose from approximately 7 to 8 or 8. 5 by the end of the measurement period. At 4 sites a figure approaching 9.5 was reached. The remaining three sites were acidic at the start of the measuring period. The spring on the northern shore of Colebrook Lake (A2) started at 6.5 but still registered an alkalinity value of 8 by week 24. The smaller Grove Lake scrape (W12) fluctuated either side of neutral for the first 15 weeks before it to climbed to reach an alkalinity value of 8. The graphs show an underlying trend towards increased alkalinity throughout the trial period. Heavy rain, on shore wave action and the presence of vigorous weed growth at any given location all seemed to result in a higher than expected alkalinity measurement. The Goose Island chart demonstrates a level of chaos, the measurement point being subject to wave action from two opposite directions, also to periods of complete calm. It is relatively shallow and has a significant level of vigorous weed growth. Very similar fluctuations in pH are seen at the entrance to Colebrook Lake South which was also notable for incoming wave action mixing with flow from the cut and vigorous weed growth

Water entering the system from Horseshoe Lake has similar pH profiles at both entry points W11 & W12. Its pH profile has significantly changed during its transit through Grove Lake and the cut leading to Colebrook Lake South. The water leaving the reserve via the sluice at A10 has a much smoother pH profile more closely mirroring the input to Colebrook Lake North via the spring on the lakes northern shore at A2. Temperature measurements varied from just above freezing on days when the ice had to be broken to take readings to 23 C at the height of summer. At the spring the temperature remained almost constant varying between 10 & 12 C except on cold days with an onshore wave action when temperatures dropped as low as 8 C.

The most recently excavated scrape on Grove Lake is very acidic, reflecting conditions on the reserve when it was originally inundated some 10 years ago. Out of interest I placed the pH meter into neat lemon juice and it measured 2.7. A not dissimilar value to that of the scrape throughout the summer. The significant move towards a neutral condition resulted from heavy rainfall over weeks 21, 22, & 23.

Measurements will continue on a regular basis at all 12 monitoring points until June 2002 to complete an annual cycle. It will be interesting to see if the measured levels remain high or return to the June 2001 levels. An alkaline pH may indicate a high concentration of calcium but the alkalinity could equally be due to other substances such as magnesium. In water where there is very little in solution, pH may vary considerably according to whether the plants are producing oxygen, which they do in daylight, or carbon dioxide which they do at low light intensities. pH gives only a rough indication of the conditions within any body of water. Acidic or slightly alkaline conditions have been sighted in one recently published Dragonfly book to define species specific habitat, a line of inquiry I am keen to follow up.


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APPENDIX G

Moor Green Lakes Nature Reserve Reference Library

The contents of the library so far collected are listed below. Three items (marked *) have been added this year.

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 Moor 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
   
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 any body would like to view the information please contact me Steve Bailey on 01276 686615 to make arrangements.


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APPENDIX H

MOOR GREEN LAKES GROUP COMMITTEE MEMBERS

2001-2002

Officer Committee Post/Responsibilities
Ken Crick* Chairman and Report Editor, Dragonfly and Damselfly Recorder and Newsletter Editor
Dr Delphine Hoyle Vice-Chairman and Recorder for Plants
Peter Scott Secretary
Sue Dent Blackwater Valley Countryside Service Manager
Amanda Simpson-Atkins Sunday Working Party Organiser
Chris Rose Treasurer
Sheila Farmer Membership Secretary
Dr Kevin Briggs* Reserve Consultant
Dr lan Brown Recorder for Birds
Katrina Slocombe Recorder for Mammals
Sue Proudley Recorder for Butterflies
Peter Standley*  

 
* Represents Moor Green Lakes Group on the Steering Group.


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APPENDIX I

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