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Darren Frost
BSc (Hons) CEnv MCIEEM CBiol MRSB
April 2018
© Cambridge Ecology
Hilton House
37 Hilton Street
Over
Cambridgeshire
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Telephone: +44 (0)1954 231239
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E-mail: [email protected]
Web address: www.cambridgeecology.com
Cambourne to Cambridge Better Public Transport:
Winter Bird Survey 2017-18 Survey
FINAL REPORT
For: Greater Cambridge Partnership
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Cambourne to Cambridge Better Public Transport: Winter Bird Survey Report 2017-18
P0608-R-006a 2 Cambridge Ecology 19/04/2018
Notice to Interested Parties
© Cambridge Ecology Limited. All rights reserved.
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permission from Cambridge Ecology Limited. If you have received this report in error, please
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Opinions and information provided in the report are on the basis of Cambridge Ecology
Limited using due skill, care and diligence in the preparation of the same and no explicit
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independent verification of any of the documents or information supplied to Cambridge
Ecology Limited has been made.
To achieve the study objectives stated in this report, we were required to base our
conclusions on the best information available during the period of the investigation and within
the limits prescribed by our client in the agreement.
No investigative method can completely eliminate the possibility of obtaining partially
imprecise or incomplete information. Thus, we cannot guarantee that the investigations
completely defined the degree or extent of e.g. species abundances or habitat management
efficacy described in the report.
This report is only valid for external use in its final issued version.
Document Information
Report title: Cambourne to Cambridge Better Public Transport: Winter Bird Survey 2017-18
Client: Greater Cambridge Partnership
Document ref: P0608-R-006a Final Report
Author(s): Darren Frost
Report date: 19th April 2018
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CONTENTS
0 EXECUTIVE SUMMARY ....................................................................................................5
1 INTRODUCTION ................................................................................................................7
Aims and objectives ......................................................................................... 7
Survey area ....................................................................................................... 7
2 METHODS ..........................................................................................................................9
Registration Mapping ....................................................................................... 9
Arable Land Usage ......................................................................................... 11
Survey Constraints......................................................................................... 11
3 RESULTS ........................................................................................................................ 12
Wintering birds between Bourn Airfield and Grange Road, Cambridge ..... 12
Wintering birds at Bourn Airfield .................................................................. 15
Nocturnal Wintering birds between Bourn Airfield and Grange Road,
Cambridge and Bourn Airfield ....................................................................... 17
Other Observations of Ecological Receptors ............................................... 17
4 EVALUATION .................................................................................................................. 18
Species account. ............................................................................................ 18
Red Kite ........................................................................................................... 18
Woodcock ........................................................................................................ 18
Kingfisher ......................................................................................................... 18
Skylark ............................................................................................................. 18
Starling ............................................................................................................. 19
Fieldfare ........................................................................................................... 19
Song Thrush .................................................................................................... 19
Redwing ........................................................................................................... 19
Mistle Thrush ................................................................................................... 20
Dunnock ........................................................................................................... 20
Bullfinch ........................................................................................................... 20
Linnet ............................................................................................................... 20
Lesser Redpoll ................................................................................................. 21
Yellowhammer ................................................................................................. 21
Reed Bunting ................................................................................................... 21
Combined Species Distribution ........................................................................ 21
5 KEY POINTS AND FINDINGS ........................................................................................ 23
6 BIBLIOGRAPHY ............................................................................................................. 25
7 APPENDIX A ................................................................................................................... 27
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TABLES
Table 2.1 Weather conditions during the 2017-2018 winter bird survey visits
......................................................................................................................... 10
Table 3.1: Bird species, their behaviour and conservation status recorded
during the 2017-2018 winter bird surveys between Bourn Airfield and
Grange Road, Cambridge. ............................................................................. 12
Table 3.2: Total number of birds recorded each visit and peak flock size in
brackets during the 2017-2018 winter bird surveys between Bourn Airfield
and Grange Road, Cambridge ....................................................................... 14
Table 3.3: Bird species, their behaviour and conservation status recorded
during the 2017-2018 winter bird surveys at Bourn Airfield and their
Conservation Status ....................................................................................... 15
Table 3.4: Total number of birds recorded each visit and peak flock size in
brackets during the 2017-2018 winter bird surveys at Bourn Airfield ........ 16
Table 8.1: Species recorded during the 2017-2018 winter bird survey. ...... 27
FIGURES
Figure 1.1: Extent of Survey Area and Site Boundary ................................. 29
Figure 3.1: Arable field usage in the eastern section of the survey area ... 30
Figure 3.2: Arable field usage in the central section of the survey area .... 31
Figure 3.3: Arable field usage in the western section of the survey area... 32
Figure 3.4: Distribution of the winter bird species of conservation
importance in Section 1 of the survey area at the Grange Road end. ........ 33
Figure 3.5: Distribution of the winter bird species of conservation
importance in Section 2 of the survey area centred around the M11
motorway. ....................................................................................................... 34
Figure 3.6: Distribution of the winter bird species of conservation
importance in Section 3 of the survey area around Madingley Wood SSSI 35
Figure 3.7: Distribution of the winter bird species of conservation
importance in Section 4 of the survey area around the Water Tower at
Madingley Mulch ............................................................................................ 36
Figure 3.8: Distribution of the winter bird species of conservation
importance in Section 5 of the survey area around Hardwick and Scotland
Farm ................................................................................................................ 37
Figure 3.9: Distribution of the winter bird species of conservation
importance in Section 6 of the survey area around the eastern entrance to
Bourn Airfield ................................................................................................. 38
Figure 3.10: Distribution of the winter bird species of conservation
importance in Section 7 of the survey area on Bourn Airfield .................... 39
Figure 4.1: Combined distribution of winter bird species of conservation
importance across the entire survey area. ................................................... 40
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0 EXECUTIVE SUMMARY
0.1 On behalf of Greater Cambridge Partnership, Cambridge Ecology Ltd was
commissioned in October 2017, to carry out a winter bird survey on land
associated with Cambourne to Cambridge Better Public Transport Scheme.
The survey comprised the sections between Bourne Airfield and Grange
Road, Cambridge. Subsequently the survey area was extended to include
the northern part of Bourn Airfield between the entrance at Wellington Way
and entrance at Broadway.
0.2 The survey recorded a total of 53 bird species. Of these 24 species were
considered to be of particular conservation importance. These species
comprised Red Kite, Kingfisher, Woodcock, Skylark, Starling, Fieldfare,
Redwing, Song Thrush, Mistle Thrush, Dunnock, Bullfinch, Linnet, Lesser
Redpoll, Yellowhammer and Reed Bunting; plus, Mute Swan, Teal, Mallard,
Shoveler, Snipe, Black-headed Gull, Stock Dove, Kestrel and Meadow Pipit,
which are Amber listed on the Birds of Conservation Concern.
0.3 Without mitigation, the presence of these species could constitute a
constraint to the scheme and therefore are of material consideration during
the planning decision process.
0.4 The diurnal survey of Bourn Airfield recorded a total of 21 bird species in the
survey area, between eastern and western entrances along the northern
perimeter. Of these 9 species were considered to be of particular
conservation importance. These species comprised Skylark, Dunnock, and
Reed Bunting; plus, Black-headed Gull, Common Gull, Lesser Black-backed
Gull, Stock Dove, Kestrel and Meadow Pipit, which are Amber listed on the
Birds of Conservation Concern.
0.5 Without mitigation, the presence of these species could constitute a
constraint to the scheme and therefore are of material consideration during
the planning decision process.
0.6 During the nocturnal surveys between Bourn Airfield and Grange Road,
Cambridge and on Bourn Airfield itself, no target species, namely wintering
plovers (Lapwing and Golden Plover) or owl species were seen or heard.
The absence of these species indicates that currently they do not constitute
a constraint to the scheme.
0.7 Observations of bird behaviour during the survey visits indicated that the
birds were using the survey area for feeding and roosting, and was therefore
an important area for the survival of the species assemblage present.
0.8 The distribution of wintering birds recorded during the survey visits was not
evenly spread across the survey area, but was focused on seven particular
areas that provided the wintering birds with suitably safe feeding and
roosting habitat.
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0.9 Based on the findings of this survey, mitigation measures would be
considered necessary; the detail of these would depend on the actual route
of the scheme The mitigation measures would be necessary to enable the
scheme to proceed without causing a significant adverse effect on the local
wintering bird population.
0.10 During the winter bird surveys observation of other ecological features were
made. A peak count of 11 Brown Hare was made; with six being the largest
number seen together. Observations of their behaviour indicated that they
were using the survey area for feeding, sheltering and courting.
0.11 Without mitigation, the presence of Brown Hare could constitute a constraint
to the scheme and therefore are of material consideration during the
planning decision process.
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1 INTRODUCTION
1.1 On behalf of Greater Cambridge Partnership, Cambridge Ecology Ltd was
commissioned in October 2017, to carry out a winter bird survey on land
associated with the Cambourne to Cambridge Better Public Transport
Scheme. The survey comprised the sections between Bourne Airfield and
Grange Road, Cambridge. Subsequently the survey area was extended to
include the northern part of Bourn Airfield between the entrance at
Wellington Way and entrance at Broadway.
1.2 This survey was required to investigate the potential for wintering birds
(especially wintering waders, i.e. Lapwing and Golden Plover; and wintering
thrushes, i.e. Redwing and Fieldfare), to be present along the proposed
route of the scheme and which could therefore potentially be affected by the
development and could cause a constraint to the proposed development. If
present, wintering birds would need to be considered further in relation to
maintaining compliance with wildlife legislation and planning policy.
1.3 For clarity in this report the development site (or 'site') refers to land within
the survey area including the red line boundary of the Cambourne to
Cambridge Better Public Transport Scheme, and the northern part of Bourn
Airfield.
Aims and objectives
1.4 The objectives of the 2018 winter bird survey were to provide information on
the:
current assemblage and abundance of wintering birds in the survey
area;
presence of wintering waders, i.e. Lapwing and Golden Plover; and
wintering thrushes, i.e. Redwing and Fieldfare;
conservation status of the wintering birds found in the survey area;
distribution of wintering birds of conservation concern found in the
survey area;
use of the survey area by wintering birds.
Survey area
1.5 The site was located between Grange Road, Cambridge at the eastern end
and the Bourn Airfield entrance off the A1303 at the western end. To the
north the site was bordered by the A428 dual carriageway and to the south
mainly by arable land. The site also included three potential park and ride
sites; one at Bourne Airfield, one adjacent to Scotland Farm and the other
near the water tower adjacent to Madingley Mulch.
1.6 In March 2018, land across the northern part of Bourn Airfield between the
entrances at Wellington Way and Broadway; along which the scheme may
pass in order to reach Cambourne, was added to the survey area.
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1.7 The survey area included a buffer zone up to 250m beyond the red line
boundary of the Cambourne to Cambridge Better Public Transport Scheme.
This excluded areas where access was not possible and excluded areas
beyond significant features such as major roads (e.g. A428), commercial,
and residential developments. These features were considered to likely
influence the movement and behaviour of wildlife and beyond which the
scheme would be unlikely to have an adverse effect.
1.8 Figure 1.1 shows the extent of the survey area.
1.9 Within the survey area:
the dominant habitat was arable land;
other habitats included amenity and improved grassland, tall ruderal,
dense and scattered scrub, ephemeral/short perennial;
habitats of conservation value included, semi-improved grassland,
broad-leaved lowland deciduous woodland (including plantation
woodland), traditional orchards, hedgerows, wet and dry ditches other
waterbodies (such as ponds and a lake) and Bin Brook.
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2 METHODS
2.1 The English names, scientific names and taxonomic order of birds detailed
in this report follows the British List (BOU, 2014).
Registration Mapping
2.2 The survey methodology involved standard territory (registration) mapping
techniques as detailed in Bibby et al. (2000). Registrations of birds, using
standard British Trust for Ornithology (BTO) two letter species codes, were
placed onto an appropriate field map (scale 1:5000). Specific codes were
also used to record the birds’ behaviour e.g. feeding, roosting.
2.3 Two diurnal surveys were made each month, plus a single nocturnal survey
was carried out each month to detect wintering plovers (namely Lapwing
and Golden Plover) and owls.
2.4 The survey area was walked at a slow pace in appropriately fine weather in
order to locate and identify all individual birds observed. All field boundaries
and suitable habitats were walked. Diurnal visits were undertaken generally
between 08:30 – 1600 over a 2-day period. The whole survey area was
covered during each visit, using suitable optical equipment (binoculars and
telescope) to observe bird behaviour. Survey routes were mapped and
routes were alternated on each visit, to ensure that all areas were covered at
various times of day across the duration of the survey.
2.5 The nocturnal visits were undertaken generally between 1800 and 2300 over
a single evening, the focus for these surveys were the arable fields, where
wintering plovers and owls may feed and/or roost at night. To detect birds at
night, the surveyor used a thermal camera (Flir Scout BTS Series Thermal
Night Vision Camera) to scan the fields and listened for the characteristic
calls to detect the presence of wintering plovers and search for owls.
2.6 Surveys were undertaken between November 2017 and March 2018, with
six survey visits taking place. The survey dates were as follows:
11th-12th and 24th-25th October 2017
9th-10th, 14th and 20th-21st November 2017
7th- 8th, 11th and 18th-19th December 2017
15th-16th, 26th and 29th-30th January 2018
6th-7th, 15th, and 21st-22nd February 2018
8th-9th, 19th, 20th and 23rd March 2018
12th-13th, 23rd, and 26th-27th March 2018 (Bourn Airfield)
2.7 The weather conditions encountered during the surveys are detailed in
Table 2.1
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Table 2.1 Weather conditions during the 2017-2018 winter bird survey visits
Survey Visit
Diurnal/Nocturnal Survey
Date Wind conditions Temperature (Ave.
oC)
Rain (y/n)
Direction Maximum Gust (mph)
Speed (Ave. mph)
BOURN AIRFIELD TO GRANGE ROAD
1 Diurnal 11/10/17 12/10/17
SW SW
16 12
14 5
16 15
n n
2 Diurnal 24/10/17 25/10/17
W W
11 10
10 5
16 16
n n
3 Diurnal 09/11/17 10/11/17
NW W
23 14
9 6
11 11
n n
4 Nocturnal 14/11/17 SW 18 8 10 n
5 Diurnal 20/11/17 21/11/17
SW SW
29 16
14 7
9 12
n n
6 Diurnal 07/12/17 08/12/17
SSW W
34 30
15 15
12 3
Light drizzle
n
7 Nocturnal 11/12/17 N 16 9 -1 n
8 Diurnal 18/12/17 19/12/17
NW SW
10 8
5 6
6 5
n n
9 Diurnal 15/01/18 16/01/18
SSW WSW
36 31
17 16
10 3
Y n
10 Nocturnal 26/01/18 W 11 7 4 n
11 Diurnal 29/01/18 30/01/18
WSW SW
32 17
17 7
11 6
Y n
12 Diurnal 06/02/18 07/02/18
N NNW
14 23
9 11
3 2
n n
13 Nocturnal 15/02/18 WSW 10 5 0 n
14 Diurnal 21/02/18 22/02/18
N E
17 17
8 10
6 5
n n
15 Diurnal 08/03/18 09/03/18
WSW SW
33 11
25 6
6 10
Occasional shower
n
16 Nocturnal 19/03/18 NNE 23 10 1 n
17 Diurnal 20/03/18 23/03/18
NNE SSW
27 28
15 15
8 10
n n
BOURN AIRFIELD
A Diurnal 12/03/18 N 7 4 10 n
B Diurnal 13/03/18 NW 16 8 8 n
C Nocturnal 23/03/18 S 18 10 7 n
D Diurnal 26/03/18 W 9 6 8 n
E Diurnal 27/03/18 SSW 21 13 11 Occasional shower
weather data obtained from: http://www.metoffice.gov.uk and
http://www.accuweather.com
2.8 Observations of birds made in the field were recorded directly on to
handheld computers. These devises displayed Ordnance Survey (OS) base
maps and the location of the surveyor - using Global Positioning Systems
(GPS) technology. This aided in the accurate recording of the birds’
location. Upon completion of the surveys the data were then downloaded
and used to create master maps.
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2.9 The conservation status of the species recorded as wintering were
compared against the following criteria:
Annex 1 of the EU Birds Directive (Directive 79/409/EEC);
Schedule 1 of the Wildlife and Countryside Act 1981, (as amended);
Species of Principal Importance Natural Environment & Rural
Communities Act (2006), (as amended);
UK Biodiversity Action Plan (UK BAP) priority species (Anon, 2007);
Cambridge Biodiversity Action Plan Priority Species
(http://www.cpbiodiversity.org.uk/biodiversity-action-plans/priority-
species);
Birds of Conservation Concern (BoCC) Red/Amber List (Hayhow et
al., 2017).
2.10 The master maps were used for those species that are covered by one or
more of the above criteria, to create a species of conservation concern
distribution map.
Arable Land Usage
2.11 A record of the arable field usage was made, as it was recognised that this
could influence the winter bird distribution and assemblage.
Survey Constraints
2.12 The surveys were carried out in suitable weather conditions and at a time of
day when birds would likely be most active and visible to surveyors. The
results were considered to provide a valid indication of the abundance,
assemblage and distribution of winter birds within the survey areas at the
time of the survey visits.
2.13 It was recognised that there were two specific constraints associated with
the survey data. These are as follows:
The survey of Bourn Airfield was carried out in March only and would
not represent a full winter survey; therefore, the data may not be
representative of the actual abundance, assemblage and distribution
of wintering birds at the airfield.
The surveys were carried out over one winter 2017-18; therefore,
natural annual variations, and variations due to arable field
management would not be identified.
2.14 These limitations should be noted and considered when using these data for
any assessment of effects by the scheme proposals on wintering birds.
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3 RESULTS
3.1 The English and Latin names of all the species recorded during the survey
detailed in this report can be found in Appendix A.
3.2 The arable field usage varied and comprised; cereal, oil seed rape, and
pea/bean crops. There were also some ploughed fields and unploughed
fallow fields. To the east of the M11 motorway there were three fields sown
with a game cover mix. Figure 3.1 illustrates the arable field usage within
the survey area.
Wintering birds between Bourn Airfield and Grange Road, Cambridge
3.3 During the winter bird survey, a total of 53 bird species were recorded
between October 2017 and March 2018. Of these 24 species are
considered to be of particular conservation importance, based on the criteria
set out in para 2.9.
3.4 Two species (Red Kite and Kingfisher) are listed as Annex 1 species under
the EU Birds Directive. Four species (Red Kite, Kingfisher, Fieldfare and
Redwing) are listed as Schedule 1 species under the Wildlife & Countryside
Act 1981 (as amended). Nine species (Skylark, Starling, Song Thrush,
Dunnock, Bullfinch, Linnet, Lesser Redpoll, Yellowhammer and Reed
Bunting) are listed as Species of Principal Importance under the NERC Act
2006, these species are also UKBAP priority species. Eleven species are
Birds of Conservation Concern (BoCC) red listed (these comprise the nine
UKBAP priority species, plus Mistle Thrush and Woodcock). Thirteen
species are BoCC amber listed, of which nine species (Mute Swan, Teal,
Mallard, Shoveler, Snipe, Black-headed Gull, Stock Dove, Kestrel and
Meadow Pipit) were not listed on any other form of citation.
3.5 All species recorded during the winter bird surveys, their usage of the survey
area, together with their conservation status are detailed in Table 3.1.
Table 3.1: Bird species, their behaviour and conservation status
recorded during the 2017-2018 winter bird surveys between Bourn
Airfield and Grange Road, Cambridge.
Species Behaviour Conservation Status
Mute Swan Feeding Amber
Teal Feeding, Roosting Amber
Mallard Feeding, Roosting Amber
Shoveler Feeding, Roosting Amber
Red-legged Partridge Feeding
Pheasant Feeding
Little Grebe Feeding
Red Kite Overhead Annex 1, WCA 1
Sparrowhawk Feeding
Buzzard Feeding
Moorhen Feeding
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Species Behaviour Conservation Status
Coot Feeding
Woodcock Feeding, Roosting Red
Snipe Feeding, Roosting Amber
Black-headed Gull Feeding Amber
Stock Dove Feeding Amber
Woodpigeon Feeding
Collared Dove Feeding
Kingfisher Feeding Annex 1, WCA 1, Amber
Green Woodpecker Feeding
Great Spotted Woodpecker Feeding
Kestrel Feeding Amber
Magpie Feeding
Jay Feeding
Jackdaw Feeding
Rook Feeding
Carrion Crow Feeding
Goldcrest Feeding
Blue Tit Feeding
Great Tit Feeding
Coal Tit Feeding
Skylark Feeding/Resting UKBAP, SPI, LBAP, Red
Long-tailed Tit Feeding
Nuthatch Feeding
Wren Feeding
Starling Feeding UKBAP, SPI, Red
Blackbird Feeding
Fieldfare Feeding WCA 1, Red
Song Thrush Feeding UKBAP, SPI, Red
Redwing Feeding WCA 1, Red
Mistle Thrush Feeding Red
Robin Feeding
Dunnock Feeding UKBAP, SPI, Amber
Pied Wagtail Feeding
Meadow Pipit Feeding Amber
Chaffinch Feeding
Bullfinch Feeding UKBAP, SPI, Amber
Greenfinch Feeding
Linnet Feeding UKBAP, SPI, Red
Lesser Redpoll Feeding UKBAP, SPI, Red
Goldfinch Feeding
Yellowhammer Feeding UKBAP, SPI, Red
Reed Bunting Feeding UKBAP, SPI, Amber Annex 1 - Annex 1 of the Birds Directive; WCA1 - Wildlife and Countryside Act 1981 (as amended) Schedule 1; UKBAP - UK Biodiversity Action Plan species; SPI -
Species of Principal Importance under Section 41 of the Natural Environment and Rural Communities (NERC) Act 2006; LBAP - Cambridgeshire Biodiversity Action Plan
Species; Red - Birds of Conservation Concern Red list; Amber - Birds of Conservation Concern Amber list;
3.6 Table 3.2 details the number of each species recorded during each diurnal
survey visit, with the largest individual flock shown in brackets.
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3.7 Figures 3.2 to 3.7 provides an illustration of the distribution of the 15
species, listed on at least one conservation criteria (Birds of Conservation
Concern Red List and higher) conservation importance.
Table 3.2: Total number of birds recorded each visit and peak flock
size in brackets during the 2017-2018 winter bird surveys between
Bourn Airfield and Grange Road, Cambridge
BTO Code
Species Visit 1
Visit 2
Visit 3
Visit 5
Visit 6
Visit 8
Visit 9
Visit 11
Visit 12
Visit 14
Visit 15
Visit 17
MS Mute Swan 2 (1) 2 (2) 2 (2)
T Teal 23 (12)
13 (8)
9 (5)
MA Mallard 15 (8)
10 (6)
20 (10)
13 (7)
34 (6)
26 (6)
28 (5)
26 (5) 30 (6)
40 (6)
10 (4)
8 (2)
SV Shoveler 2 (1)
RL Red-legged Partridge
8 (2) 12 (4)
18 (2)
4 (2) 6 (2) 2 (2) 2 (1)
PH Pheasant 2 (1) 2 (2) 2 (2) 48 (15)
24 (3)
32 (4)
32 (4) 8 (1) 22 (3)
12 (2)
8 (2)
LG Little Grebe 2 (2) 2 (1) 2 (1) 2 (1) 2 (1)
KT Red Kite 2 (1)
SH Sparrowhawk 1 (1) 2 (1) 2 (1) 2 (1)
BZ Buzzard 5 (3) 5 (3) 2 (1) 3 (2) 2 (1) 6 (2) 4 (2) 2 (1) 2 (1) 2 (1) 2 (2) 5 (3)
MH Moorhen 3 (2) 6 (2) 9 (4) 6 (2) 26 (4)
10 (2)
14 (2)
16 (2) 10 (2)
22 (3)
12 (2)
10 (2)
CO Coot 3 (3) 2 (2) 6 (6) 5 (5) 14 (5)
4 (2) 8 (2) 16 (3) 10 (3)
6 (3) 4 (2) 4 (2)
WK Woodcock 13 (10)
13 (10)
18 (4)
6 (1) 16 (5)
6 (2)
SN Snipe 2 (2) 3 (3) 2 (1) 4 (1) 4 (1)
BH Black-headed Gull
4 (2) 4 (2) 4 (2) 6 (6) 8 (8)
SD Stock Dove 6 (3) 20 (10) 4 (2) 6 (2)
WP Woodpigeon 61 (24)
57 (20)
71 (40)
60 (14)
244 (25)
422 (36)
196 (18)
148 (17)
270 (125
)
118 (10)
195 (45)
126 (38)
CD Collared Dove 6 (3) 16 (4)
40 (5)
4 (2) 18 (2)
8 (2) 8 (2) 6 (2) 6 (2)
KF Kingfisher 1 (1) 1 (1) 2 (1) 2 (1) 2 (1)
G Green Woodpecker
1 (1) 3 (1) 4 (1) 2 (1) 6 (1) 4 (1) 4 (1) 4 (2) 2 (1)
GS Great Spotted Woodpecker
3 (1) 3 (1) 16 (1)
12 (2)
8 (1) 8 (1) 2 (1) 8 (2) 6 (2) 2 (1)
K Kestrel 2 (1) 1 (1) 3 (1) 1 (1) 4 (1) 4 (1) 2 (1) 4 (1) 2 (1) 2 (1) 2 (1)
MG Magpie 5 (2) 10 (2)
13 (4)
10 (2)
56 (3)
32 (5)
44 (2)
34 (2) 12 (3)
28 (2)
20 (4)
18 (2)
J Jay 1 (1) 6 (1) 6 (1) 6 (1) 2 (1) 2 (1) 6 (1) 2 (1) 2 (1)
JD Jackdaw 19 (19)
3 (3) 36 (20)
16 (12)
108 (28)
82 (15)
36 (7)
12 (4) 28 (11)
16 (5)
18 (6)
RO Rook 65 (30)
8 (8) 11 (11)
10 (5)
C Carrion Crow 70 (27)
12 (5)
29 (10)
25 (5)
70 (6)
76 (5)
60 (5)
50 (3) 36 (4)
44 (2)
26 (4)
20 (5)
GC Goldcrest 13 (7)
3 (3) 1 (1) 3 (3) 34 (6)
12 (4)
20 (4)
4 (2) 2 (1) 2 (1) 2 (1) 2 (1)
BT Blue Tit 11 (7)
17 (10)
12 (4)
37 (10)
104 (12)
108 (6)
104 (5)
76 (3) 60 (6)
80 (5)
58 (4)
50 (4)
GT Great Tit 1 (1) 10 (6)
8 (4) 20 (9)
52 (4)
70 (4)
68 (4)
40 (3) 32 (1)
56 (3)
28 (4)
25 (2)
CT Coal Tit 2 (1) 6 (3) 6 (2) 4 (2) 6 (1) 2 (1)
S Skylark 1 (1) 60 (28)
26 (10)
8 (4) 8 (1) 2 (1) 2 (1) 2 (1)
LT Long-tailed Tit 43 (21)
28 (14)
22 (16)
35 (11)
100 (10)
42 (6)
42 (7)
38 (5) 68 (10)
36 (6)
30 (6)
28 (7)
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BTO Code
Species Visit 1
Visit 2
Visit 3
Visit 5
Visit 6
Visit 8
Visit 9
Visit 11
Visit 12
Visit 14
Visit 15
Visit 17
NH Nuthatch 1 (1) 2 (1) 4 (2) 4 (2) 2 (1) 2 (1) 4 (2) 4 (2) 4 (2)
WR Wren 1 (1) 5 (4) 13 (1)
68 (1)
42 (1)
70 (2)
28 (1) 20 (1)
38 (1)
40 (2
36 (2)
SG Starling 4 (4) 6 (3) 10 (5) 130 (37)
26 (8)
16 (8)
20 (6)
B Blackbird 5 (1) 9 (6) 26 (4)
15 (4)
72 (1)
120 (6)
68 (2)
32 (2) 50 (3)
70 (3)
62 (2)
53 (2)
FF Fieldfare 8 (4) 22 (12)
178 (28)
386 (85)
64 (15)
98 (21) 154 (41)
36 (18)
102 (48)
24 (24)
ST Song Thrush 2 (1) 5 (5) 6 (5) 34 (1)
20 (3)
18 (1)
14 (1) 6 (1) 14 (1)
12 (2)
10 (2)
RE Redwing 6 (3) 19 (15)
91 (28)
51 (30)
284 (29)
262 (32)
122 (14)
80 (14) 28 (4)
74 (15)
59 (32)
46 (15)
M Mistle Thrush 1 (1) 2 (2) 2 (2) 4 (2) 4 (2) 8 (2) 12 (2)
2 (1) 4 (1) 6 (2) 2 (2) 2 (2)
R Robin 8 (1) 11 (3)
32 (5)
29 (8)
74 (1)
62 (1)
94 (1)
68 (1) 52 (1)
66 (1)
64 (2)
52 (2)
D Dunnock 4 (1) 3 (1) 5 (1) 13 (4)
26 (4)
42 (4)
44 (4)
32 (5) 12 (1)
42 (1)
40 (3)
44 (4)
PW Pied Wagtail 6 (3) 4 (2) 2 (1) 2 (1) 2 (1) 6 (2) 4 (2)
MP Meadow Pipit 18 (15)
1 (1) 12 (6)
98 (39)
6 (3) 16 (5) 6 (3) 22 (11)
18 (12)
26 (18)
CH Chaffinch 6 (2) 10 (6)
15 (10)
19 (8)
36 (14)
64 (6)
68 (11)
54 (12) 60 (23)
40 (5)
BF Bullfinch 1 (1) 4 (2) 4 (2) 2 (2) 2 (2)
GR Greenfinch 20 (10)
4 (2) 20 (8) 2 (1) 22 (8)
15 (10)
12 (6)
LI Linnet 44 (22)
132 (38)
32 (16)
24 (12) 20 (10)
12 (12)
15 (15)
LR Lesser Redpoll 1 (1)
GO Goldfinch 70 (28)
30 (20)
78 (54)
52 (25)
68 (18)
100 (26)
50 (14)
44 (16) 134 (34)
54 (12)
47 (22)
45 (18)
Y Yellowhammer 6 (5) 24 (12)
6 (3) 8 (4) 22 (11) 96 (45)
8 (4) 6 (6) 6 (2)
RB Reed Bunting 12 (12)
7 (4) 64 (18)
22 (7)
20 (7) 36 (18)
16 (4)
12 (6)
14 (8)
Wintering birds at Bourn Airfield
3.8 During the winter bird survey visits in March 2018, a total of 21 species were
recorded. Of these nine species are considered to be of particular
conservation importance, based on the criteria set out in para 2.9.
3.9 Three species (Skylark, Dunnock and Reed Bunting) are listed as Species of
Principal Importance under the NERC Act 2006, these species are also
UKBAP priority species. One species (Skylark) is a LBAP priority species
and is red listed, while a further seven species are amber listed.
3.10 All species recorded during the winter bird survey visits, their usage of the
survey area, together with their conservation status are detailed in Table 3.3.
Table 3.3: Bird species, their behaviour and conservation status
recorded during the 2017-2018 winter bird surveys at Bourn Airfield
and their Conservation Status
Species Behaviour Conservation Status
Red-legged Partridge Feeding
Pheasant Feeding
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Species Behaviour Conservation Status
Buzzard Overhead
Black-headed Gull Roosting Amber
Common Gull Roosting Amber
Lesser Black-backed Gull Roosting Amber
Stock Dove Feeding Amber
Woodpigeon Feeding
Collared Dove Feeding
Kestrel Feeding Amber
Magpie Feeding
Jackdaw Feeding
Rook Feeding
Carrion Crow Feeding
Skylark Feeding UKBAP, SPI, LBAP, Red
Blackbird Feeding
Robin Feeding
Dunnock Feeding UKBAP, SPI, Amber
Meadow Pipit Feeding Amber
Chaffinch Feeding
Reed Bunting Feeding UKBAP, SPI, Amber
3.11 Table 3.4 details the number of each species recorded during each diurnal
survey visit, with the largest individual flock shown in brackets.
Table 3.4: Total number of birds recorded each visit and peak flock
size in brackets during the 2017-2018 winter bird surveys at Bourn
Airfield
BTO Code Species Visit A Visit B Visit D Visit E
RL Red-legged Partridge 2 (2) 2 (2) 2 (2) 2 (2)
PH Pheasant 1 2 (1) 2 (1) 2 (1)
BZ Buzzard 2 (2) 2 (2)
BH Black-headed Gull 16 (16) 10 (10) 8 (8)
CM Common Gull 12 (12) 8 (8) 2 (2)
LB Lesser Black-backed Gull 20 (2) 18(18)
SD Stock Dove 4 (4) 2 (2) 2 (2)
WP Woodpigeon 6 (6) 4 (4) 18 )10) 13 (8)
CD Collared Dove 2 (2) 2 (2)
K Kestrel 1 (1) 1 (1) 1 (1)
MG Magpie 2 (2) 2 (2) 5 (2) 2 (2)
JD Jackdaw 3 (2) 2 (2) 7 (4) 2 (2)
RO Rook 5 (5) 4 (2) 6 (3) 5 (2)
C Carrion Crow 2 (2) 2 (2) 3 (3) 4 (4)
S Skylark 4 (1) 3 (1) 3 (1) 3 (1)
B Blackbird 1 1
R Robin 2 (1) 2 (1) 3 (1) 2 (1)
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BTO Code Species Visit A Visit B Visit D Visit E
D Dunnock 1
MP Meadow Pipit 2 (1)
CH Chaffinch 2 (2) 1 (1) 2 (1) 2(2)
RB Reed Bunting 2 (2) 1(1) 1 (1)
Nocturnal Wintering birds between Bourn Airfield and Grange Road,
Cambridge and Bourn Airfield
3.12 Nocturnal survey visits of the area between Grange Road, Cambridge and
Bourn Airfield were carried out during visits 4, 7,10,13 and 16. A nocturnal
survey of Bourn Airfield was carried out during visit C.
3.13 No wintering waders (namely Lapwing and/or Golden Plover) or owls, were
recorded during any of the nocturnal winter bird surveys between November
2017 and March 2018.
Other Observations of Ecological Receptors
3.14 During the winter bird surveys, observation of other ecological receptors
were also noted.
3.15 Brown Hare, a UK BAP species, was observed during eight of the survey
visits. These were mainly observed on arable land south of the A1303
between Madingley Rise and Coton village and in the grassland associated
with the covered reservoir adjacent to Madingley Mulch. Brown Hare were
also seen on the arable land to the east of the M11 motorway and on Bourn
Airfield.
3.16 The peak count of 11 Brown Hare was made, with six being the largest
number seen together. Observations of their behaviour indicated that they
were using the survey area for feeding, sheltering and courting.
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4 EVALUATION
Species account.
4.1 The following accounts of bird species relate to those considered as
wintering, within the survey area that are listed on: Annex 1 of the EC Birds
Directive, Schedule 1 of the Wildlife & Countryside Act 1981, Section 41 -
Species of Principal Importance of the NERC Act 2006, UK and Local BAP
Priority Species and the Birds of Conservation Concern Red List. These
species are, therefore, regarded as of high conservation importance either
nationally or locally.
Red Kite
4.2 Red Kite is listed as an Annex 1 in the European Birds Directive and
Schedule 1 species in the Wildlife & Countryside Act 1981 (as amended).
Two Red Kite were seen on one occasion during visit 8. These birds were
seen flying over the arable fields in the survey area to the south of the West
Cambridge site and appeared to be searching for food.
Woodcock
4.3 Woodcock is listed under the Birds of Conservation Concern as a red list
species. Woodcock were seen during six of the survey visits, with a peak
count of 18 birds on visit 6.
4.4 A peak assemblage of 10 birds seen in the same area, rather than as a
flock, was on visits 3 and 6. These birds were located in the woodland area
north of the covered reservoir at the top of Madingley Rise and the dense
scrub area to the south and east of Coton Orchard. The birds appeared to
be using the survey area for feeding and roosting.
Kingfisher
4.5 Kingfisher is listed as an Annex 1 in the European Birds Directive and
Schedule 1 species in the Wildlife & Countryside Act 1981 (as amended).
Up to two Kingfisher were seen during five of the survey visits. Although
only one bird was seen at any one time.
4.6 These birds were observed along Bin Brook and at one of the ponds north of
the Emmanuel College Sports Ground. The birds appeared to be using the
survey area for feeding.
Skylark
4.7 Skylark is listed as a UKBAP, Local BAP, Species of Principal Importance
and cited under the Birds of Conservation Concern as a red list species.
Skylark were seen during eight of the survey visits. The peak count
comprised 60 birds on visit 6, during which the largest flock of 28 birds was
also observed.
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4.8 Observations of Skylark were made across the entire survey area,
principally in arable fields. However, most birds were located in the arable
fields south of Madingley Rise to the west of the M11 motorway as well as
on the arable land on Bourn Airfield. The birds appeared to be using the
survey area for feeding and roosting.
Starling
4.9 Starling is listed as a UKBAP, Species of Principal Importance and cited
under the Birds of Conservation Concern as a red list species. Starling were
seen during seven of the surveys visits. The peak count comprised 137
birds on visit 12, during which the largest flock of 37 birds was also
observed.
4.10 Starling were located from Madingley Rise eastward towards Cambridge,
principally associated with grassy fields such as sports fields. The birds
appeared to be using the survey area for feeding.
Fieldfare
4.11 Fieldfare is a Schedule 1 species in the Wildlife & Countryside Act 1981 (as
amended) and cited under the Birds of Conservation Concern as a red list
species. Fieldfare were seen during ten of the surveys visits. The peak
count comprised 386 birds on visit 8, during which the largest flock of 85
birds was also observed.
4.12 Observations of Fieldfare were made across the survey area between
Madingley Rise and Grange Road, Cambridge, principally in the network of
hedgerows around the arable fields. The birds appeared to be using the
survey area for feeding and roosting.
Song Thrush
4.13 Song Thrush is listed as a UKBAP, Species of Principal Importance and
cited under the Birds of Conservation Concern as a red list species. Song
Thrush were seen during 11 of the survey visits. The peak count comprised
34 birds on visit 6. The largest flock contained 5 birds seen during visits 3
and 5.
4.14 Observations of Song Thrush were made across the entire survey area,
principally in the hedgerows around the arable fields and amongst the scrub
and woodland habitat. The birds appeared to be using the survey area for
feeding and roosting.
Redwing
4.15 Redwing is a Schedule 1 species in the Wildlife & Countryside Act 1981 (as
amended) and cited under the Birds of Conservation Concern as a red list
species. Redwing were seen during all of the survey visits. The peak count
comprised 284 birds on visit 6. The largest flock contained 32 birds during
visits 8 and 15.
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4.16 Observations of Redwing were made across the entire survey area,
principally in the hedgerows around the arable fields and amongst the scrub
and woodland habitat. The birds appeared to be using the survey area for
feeding and roosting.
Mistle Thrush
4.17 Mistle Thrush is cited under the Birds of Conservation Concern as a red list
species. Mistle Thrush were seen during all of the survey visits. The peak
count was of 12 birds on visit 9. Being a highly territorial species, even
during the winter the highest number of this species seen together was two
observed during nine of the survey visits.
4.18 Observations of Mistle Thrush were made across most of the survey area
between Hardwick and Grange Road, Cambridge, principally in woodland,
scrub and mature garden habitats. The birds appeared to be using the
survey area for feeding and roosting.
Dunnock
4.19 Dunnock is listed as a UKBAP, Species of Principal Importance and cited
under the Birds of Conservation Concern as an amber list species. Dunnock
were seen during all of the survey visits. The peak count comprised 44 birds
seen during visit 9 and 17. The largest number of Dunnock seen together
was five during visit 11.
4.20 Observations of Dunnock were made across the entire survey area,
principally in hedgerows, scrub, woodland and mature garden habitat. The
birds appeared to be using the survey area for feeding and roosting.
Bullfinch
4.21 Bullfinch is listed as a UKBAP, Species of Principal Importance and cited
under the Birds of Conservation Concern as an amber list species. Bullfinch
were seen during five of the survey visits. The peak count comprised four
birds on visits 12 and 14. The largest number of Bullfinch seen together was
two during visits 12-17.
4.22 Observations of Bullfinch were made in the survey area between Coton
Orchard and Grange Road, Cambridge, principally associated with dense
scrub habitat. The birds appeared to be using the survey area for feeding.
Linnet
4.23 Linnet is listed as a UKBAP, Species of Principal Importance and cited
under the Birds of Conservation Concern as a red list species. Linnet were
seen during seven of the survey visits. The peak count comprised 132 birds
on visit 8, during which the largest flock of 38 birds was also observed.
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4.24 Linnet were observed in the game cover crops located amongst the arable
land in the survey area, to the east of the M11 motorway. The birds
appeared to be using the survey area for feeding and roosting.
Lesser Redpoll
4.25 Lesser Redpoll is listed as a UKBAP, Species of Principal Importance and
cited under the Birds of Conservation Concern as a red list species. A single
Lesser Redpoll on visit 3.
4.26 The Lesser Redpoll was observed feeding in tall ruderal habitat near the
eastern entrance to Bourn Airfield.
Yellowhammer
4.27 Yellowhammer is listed as a UKBAP, Species of Principal Importance and
cited under the Birds of Conservation Concern as a red list species.
Yellowhammer were seen during nine of the survey visits. The peak count
comprised 96 birds on visit 12, during which the largest flock of 45 birds was
also observed.
4.28 Observations of Yellowhammer were made across the entire survey area,
but principally in the game cover crops located amongst the arable land in
the survey area, to the east of the M11 motorway. The birds appeared to be
using the survey area for feeding and roosting.
Reed Bunting
4.29 Reed Bunting is listed as a UKBAP, Species of Principal Importance and
cited under the Birds of Conservation Concern as an amber list species.
Reed Bunting were seen during nine of the survey visits. The peak count
comprised 64 birds on visit 8. The largest flock of Reed Bunting contained
18 birds during visits 8 and 12.
4.30 Reed Bunting were primarily seen in the game cover crops located amongst
the arable land in the survey area, to the east of the M11 motorway. The
birds appeared to be using the survey area for feeding and roosting.
Combined Species Distribution
4.31 The combined distribution of those species listed on at least one
conservation criteria (Birds of Conservation Concern Red List and higher) is
showing in Figure 4.1.
4.32 The distribution map indicated that the key areas for bird species listed on at
least one conservation criteria were as follows:
The areas around the balancing ponds adjacent and north of the
A1303.
The woodland and grassland associated with the covered reservoir
adjacent to Madingley Mulch.
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Madingley Wood SSSI.
The arable land between Madingley Rise and Coton Village.
The land around Coton Orchard and Coton Country Park.
The game cover crop on arable land and network of hedgerows to the
east of the M11 motorway.
The mosaic of fields, scrub, network of hedgerows and grassland
adjacent to Bin Brook.
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5 KEY POINTS AND FINDINGS
5.1 Winter bird surveys were conducted between October 2017 and March 2018
and therefore throughout the period when wintering birds would likely be
present. Twelve of the visits were made during the day, in addition five
nocturnal visits were made.
5.2 It is considered that the survey results present an accurate reflection of the
wintering bird assemblage and species population size present during the
2017-18 wintering season between Bourn Airfield and Grange Road,
Cambridge.
5.3 The diurnal survey recorded a total of 53 bird species between Bourn Airfield
and Grange Road, Cambridge. The survey recorded a total of 53 bird
species. Of these 24 species were considered to be of particular
conservation importance. These species comprised Red Kite, Kingfisher,
Woodcock, Skylark, Starling, Fieldfare, Redwing, Song Thrush, Mistle
Thrush, Dunnock, Bullfinch, Linnet, Lesser Redpoll, Yellowhammer and
Reed Bunting; plus, Mute Swan, Teal, Mallard, Shoveler, Snipe, Black-
headed Gull, Stock Dove, Kestrel and Meadow Pipit, which are Amber listed
on the Birds of Conservation Concern.
5.4 During March 2018 the survey area was extended to include the northern
section of Bourn Airfield itself. Four diurnal visits and one nocturnal visit
were made.
5.5 As the survey of Bourn Airfield was only carried out during March, the survey
was considered to partially inform the status of, assemblage and species
population size present in the Bourn Airfield survey area.
5.6 The diurnal survey of Bourn Airfield recorded a total of 21 bird species in the
survey area, between eastern and western entrances along the northern
perimeter. Of these 9 species were considered to be of particular
conservation importance. These species comprised Skylark, Dunnock, and
Reed Bunting; plus, Black-headed Gull, Common Gull, Lesser Black-backed
Gull, Stock Dove, Kestrel and Meadow Pipit, which are Amber listed on the
Birds of Conservation Concern.
5.7 Without mitigation, the presence of the species of conservation importance
could constitute a constraint to the scheme and therefore are of material
consideration during the planning decision process.
5.8 During the nocturnal surveys between Bourn Airfield and Grange Road,
Cambridge and on Bourn Airfield itself, no target species, namely wintering
plovers (Lapwing and Golden Plover) and owl species were seen or heard.
5.9 The absence of these species indicates that currently they do not constitute
a constraint to the scheme.
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5.10 Observations of bird behaviour during the survey visits indicated that the
birds were using the survey area for feeding and roosting, and was therefore
an important area for the survival of the species assemblage present.
5.11 The distribution of wintering birds recorded during the survey visits was not
evenly spread across the survey area, but was focused on seven particular
areas that provided the wintering birds with suitably safe feeding and
roosting habitats.
5.12 For instance, wintering thrushes (e.g. Fieldfare, Redwing and Song Thrush)
were feeding on the berries provided by the network hedgerows, such as
those to the east of the M11 motorway.
5.13 The other areas particularly important to the wintering bird assemblage
included:
the balancing ponds adjacent and north of the A1303;
the woodland and grassland associated with the covered reservoir
adjacent to Madingley Mulch;
Madingley Wood SSSI;
the arable land between Madingley Rise and Coton Village;
the land around Coton Orchard and Coton Country Park; and
the mosaic of fields, scrub, network of hedgerows and grassland
adjacent to Bin Brook, including the various city and county wildlife
sites.
5.14 During the winter bird surveys observation of other ecological features were
made. Brown Hare were observed, located on arable land south of the
A1303 between Madingley Rise and Coton village, in the grassland
associated with the covered reservoir adjacent to Madingley Mulch, game
cover crop on the arable land to the east of the M11 motorway and on Bourn
Airfield.
5.15 Based on the findings of this survey, mitigation measures would be
considered necessary; the detail of these would depend on the actual route
of the scheme The mitigation measures would be necessary to enable the
proposed development to proceed without causing a significant adverse
effect on the local wintering bird population.
5.16 During the winter bird surveys observation of other ecological features were
made. A peak count of 11 Brown Hare was made; with six being the largest
number seen together. Observations of their behaviour indicated that they
were using the survey area for feeding, sheltering and courting.
5.17 Without mitigation, the presence of Brown Hare could constitute a constraint
to the scheme and therefore are of material consideration during the
planning decision process.
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6 BIBLIOGRAPHY
Bacon, L., Cooper, A., Venebles, H. (2013). Cambridgeshire Bird Atlas
2007-2011. Published by the Cambridgeshire Bird Club
Bibby, C.J. Burgess, N.D. Hill, D.A. & Mustoe, S.H. (2000). Bird Census
Techniques. 2nd edition. Academic Press, London.
British Ornithologists’ Union (BOU) (2014). The British List: The Official List
of Bird Species Recorded in Britain.
Brown, A. and Grice. P. (2005). Birds in England. Natural England. T. & A.D.
Poyser. London.
Cambridge Ecology (2017a). Cambourne to Cambridge Better Public
Transport: Protected Species Constraints Survey 2017. Final Report.
P0608-R-001a.
Cambridge Ecology (2017b). Cambourne to Cambridge Better Public
Transport: Phase 1 Habitat Survey 2017. Final Report. P0608-R-
003a.
Department for Communities and Local Government (2012) National
Planning Policy Framework.
Drewitt, A.L., Whitehead, S. and Cohen, S. (2015). Guidelines for the
Selection of Biological SSSIs. Part 2: Detailed Guidelines for Habitats
and Species Groups. Chapter 17 Birds. Joint Nature Conservation
Committee, Peterborough.
Eaton, M.A., Aebischer, N.J., Brown, A.F., Hearn, R.D., Lock, L., Musgrove,
A.J., Noble, D.G., Stroud, D.A. & Gregory, R.D. (2015). Birds of
Conservation Concern 4: the population status of birds in the United
Kingdom, Channel Islands and Isle of Man. British Birds 108: 708–
746.
EU. (1979). On the Conservation of Wild Birds. Council Directive
79/409/EEC, Brussels.
Fuller, R.J. (1980). A method for assessing the ornithological interest of sites
for conservation. Biological Conservation 17:229-239.
Gilbert, G., Gibbons D.W. & Evans J., (1998). Bird Monitoring Methods: A
manual of techniques for key species.
RSPB/BTO/JNCC/WWT/ITE/The Seabird Group RSPB/BTO, Sandy.
Hayhow DB, Bond AL, Douse A, Eaton MA, Frost T, Grice PV, Hall C, Harris
SJ, Havery S, Hearn RD, Noble DG, Oppel S, Williams J, Win I and
Wotton S (2017). The state of the UK’s birds 2016. The RSPB, BTO,
WWT, DAERA, JNCC, NE, NRW and SNH, Sandy, Bedfordshire.
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HM Government (2006). Natural Environment and Rural Communities Act.
HM Government (1981). Wildlife and Countryside Act.
Marchant, J. (1983). Common Bird Census Instructions. BTO, Tring.
Musgrove, A. J., Aebischer, N. J., Eaton, M. A., Hearn, R. D., Newson, S. E.,
Noble, D. G., Parsons, M., Risely, K., & Stroud, D. A. (2013).
Population estimates of birds in Great Britain and the United Kingdom.
Brit. Birds 106: 64–100.
Robinson, R.A., Leech, D.I., Massimino, D., Woodward, I., Eglington, S.M.,
Marchant, J.H., Sullivan, M.J.P., Barimore, C., Dadam, D., Hammond,
M.J., Harris, S.J., Noble, D.G., Walker, R.H. & Baillie, S.R. (2016)
BirdTrends 2016: trends in numbers, breeding success and survival
for UK breeding birds. Research Report 691. BTO, Thetford.
www.bto.org/birdtrends
Robinson, R.A. (2017). BirdFacts: profiles of birds occurring in Britain &
Ireland (BTO Research Report 407). BTO, Thetford.
Thomson Ecology (2014). Bourn Airfield, Cambridge Cambridgeshire:
Wintering Birds Survey for Countryside Properties Plc.
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7 APPENDIX A
Table 8.1: Species recorded during the 2017-2018 winter bird survey.
Common Name Scientific Name Conservation Status
Mute Swan Cygnus olor Amber
Teal Anas crecca Amber
Mallard Anas platyrhynchos Amber
Shoveler Anas clypeata Amber
Red-legged Partridge Alectoris rufa
Pheasant Phasianus colchicus
Little Grebe Tachybaptus ruficollis
Red Kite Milvus milvus Annex 1, WCA 1
Sparrowhawk Accipiter nisus
Buzzard Buteo buteo
Moorhen Gallinula chloropus
Coot Fulica atra
Woodcock Scolopax rusticola Red
Snipe Gallinago gallinago Amber
Black-headed Gull Chroicocephalus ridibundus Amber
Common Gull Larus canus Amber
Lesser Black-backed Gull Larus fuscus Amber
Stock Dove Columba oenas Amber
Woodpigeon Columba palumbus
Collared Dove Streptopelia decaocto
Kingfisher Alcedo atthis Annex 1, WCA 1, Amber
Green Woodpecker Picus viridis
Great Spotted Woodpecker Dendrocopos major
Kestrel Falco tinnunculus Amber
Magpie Pica pica
Jay Garrulus glandarius
Jackdaw Corvus monedula
Rook Corvus frugilegus
Carrion Crow Corvus corone
Goldcrest Regulus regulus
Blue Tit Cyanistes caeruleus
Great Tit Parus major
Coal Tit Periparus ater
Skylark Alauda arvensis UKBAP, SPI, LBAP, Red
Long-tailed Tit Aegithalos caudatus
Nuthatch Sitta europaea
Wren Troglodytes troglodytes
Starling Sturnus vulgaris UKBAP, SPI, Red
Blackbird Turdus merula
Fieldfare Turdus pilaris WCA 1, Red
Song Thrush Turdus philomelos UKBAP, LBAP, SPI, Red
Redwing Turdus iliacus WCA 1, Red
Mistle Thrush Turdus viscivorus Red
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Common Name Scientific Name Conservation Status
Robin Erithacus rubecula
Dunnock Prunella modularis UKBAP, SPI, Amber
Pied Wagtail Motacilla alba
Meadow Pipit Anthus pratensis Amber
Chaffinch Fringilla coelebs
Bullfinch Pyrrhula pyrrhula UKBAP, SPI, Amber
Greenfinch Chloris chloris
Linnet Linaria cannabina UKBAP, SPI, Red
Lesser Redpoll Acanthis cabaret UKBAP, SPI, Red
Goldfinch Carduelis carduelis
Yellowhammer Emberiza citrinella UKBAP, SPI, Red
Reed Bunting Emberiza schoeniclus UKBAP, SPI, Amber
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FIGURES
Figure 1.1: Extent of Survey Area and Site Boundary
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Figure 3.1: Arable field usage in the eastern section of the survey area
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Figure 3.2: Arable field usage in the central section of the survey area
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Figure 3.3: Arable field usage in the western section of the survey area
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Figure 3.4: Distribution of the winter bird species of conservation importance in Section 1 of the survey area at the Grange Road end.
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Figure 3.5: Distribution of the winter bird species of conservation importance in Section 2 of the survey area centred around the M11 motorway.
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Figure 3.6: Distribution of the winter bird species of conservation importance in Section 3 of the survey area around Madingley Wood SSSI
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Figure 3.7: Distribution of the winter bird species of conservation importance in Section 4 of the survey area around the Water Tower at Madingley Mulch
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Figure 3.8: Distribution of the winter bird species of conservation importance in Section 5 of the survey area around Hardwick and Scotland Farm
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Figure 3.9: Distribution of the winter bird species of conservation importance in Section 6 of the survey area around the eastern entrance to Bourn Airfield
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Figure 3.10: Distribution of the winter bird species of conservation importance in Section 7 of the survey area on Bourn Airfield
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Figure 4.1: Combined distribution of winter bird species of conservation importance across the entire survey area.