2 4 1 0 0 0 0 0 0 0 0 0 0 0 0 A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A 0 A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A 50 50 50 50 50 50 50 50 50 50 50 50 50
5 Jan 12 Reproduced with the permission of the controller of Her Majesty’s Stationery Office. © Crown Copyright - Licence No. AR100017235 5 0 A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A 100 100 100 100 100 100 100 100 100 100 100 100 100 50 ! ! ! ! ! ! ! ! ! ! ! ! ! 17 100 200 200 200 200 200 200 200 200 200 200 200 200 200 18 ! ! ! ! ! ! ! ! ! ! ! ! 16 20 ! ! SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS IS IS IS IS IS IS IS IS IS IS SI SI IS IS IS IS IS IS IS IS IS IS IS IS IS IS IS SI SI IS IS IS IS IS IS IS IS IS IS IS IS IS IS IS SI SI IS IS IS IS IS IS IS IS IS IS IS IS IS IS IS SI SI IS IS IS IS IS IS IS IS IS IS IS IS IS IS IS SI SI IS IS IS IS IS IS IS IS IS IS IS IS IS IS IS SI SI IS IS IS IS IS IS IS IS IS IS IS IS IS IS IS SI SI IS IS IS IS IS IS IS IS IS IS IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS 23 SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS 41 ! ! ! ! ! ! ! ! ! ! ! ! ! 42 44 200 45 Phase 1
40 43 ! 29 G 300 300 300 300 300 300 300 300 300 300 300 300 300 SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS 22 ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI SI SISI SI ISI SI SI SISI SI ISI SI SI SISI SI G ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI 0 ISI SI ISI SI ISI SI A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A A ! 15
21 G G 3
50 300 ISI SI ISI SI ISI SI 28 24 14 400 400 400 400 400 400 400 400 400 400 400 400 27 400 Meters Meters Meters Meters Meters Meters Meters Meters 39 Meters Meters Meters SI Meters Meters 100 25 12 26 13 Phase 2 ! 400 G 200 11 ! IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI 19 SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS SI SI IS IS IS IS IS 10 500 38 30
! Meters G 9 IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI 300 32 7 ISI SI ISI SI ISI SI
8
V
V
V V V
V V
V
V IS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS
V
SI SIS IS IS IS V
SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS V V SI SIS IS IS IS V
V V V V IS IS IS IS IS IS IS IS IS IS IS IS SI SIS IS IS IS IS IS IS IS IS IS IS IS SI SIS IS IS IS IS IS IS IS IS IS IS IS SI SIS IS IS IS IS IS IS IS IS IS IS IS SI SIS IS IS IS IS IS IS IS IS IS IS IS
V
V IS IS IS IS
SI SIS IS IS IS SI SIS IS IS IS
SI SIS IS IS IS
SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS
SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS
V
V V
V V IS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS V V SI SIS IS IS IS V
V V V SI SIS IS IS IS V SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS
SI SIS IS IS IS V SI SIS IS IS IS SI SIS IS IS IS
SI SIS IS IS IS SI SIS IS IS IS
SI SIS IS V IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS
V V
V
V V V SI SIS IS IS IS V SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS
SI SIS IS IS IS
V V V V
V
V
V V
V
V V V V
V V V V
V
V
V V
V
V V V V
V V V V
V
V
V V
V
V
V V V
V V V V
V
V
V V
V
V V V V
V V V V
V
V
V V
V
V
V V V
V V V V
V
V
V V
V V V V V
V V V V
31 V
V
V V
V V V V V
V V V V
V
V
V V V V V V V
V V V V
6 V V
V V V V V V V V V V V V V V V V V V
V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V
400 V V V V VI V V V V VI V VI V VI VI VI VI VI I VI VI VI VI VI V V VI V VI VI VI VI VI V VI VI VI VI VI I I I VI V
I V VI VI V VI V 7 VI VV V V VI V V V
VI VI V V VI VI V I V I I VI VI VI
I VI VI IV V V V V VI
VI V VI I V VI VI VI VI VI VI I V
VI VI VI V V VI I I I V V V V VI I VIMeters V VI V VI VV V V V I
VI VI VI V I VI V V I I I V V I V VI V VI VI VV V SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS
I VI VI ISV V IS VI IS IS VI
V VI I VI V VI VI VI VI VI V
I VI V V VI V VI V V V I V V V V
V V I VI VI I V VI VI VI VI VI VI VI V V
VI VI VI V VI V V V VI VI VI VI VI VI VI I V
VI VI V V VI VI VI VI VI VI VI VI VI V
VI I V V V V V V VI V
VI VI V VI I V V I VI I VI VI VI V V V V I
VI VI VI V I VI V V I I I V V I V I I VV V
VI VI VI VI VI V V V VI V
I I VVI VI VI VI VI V V VI V VI V VI VI V I V VI V V V V
V V VI VI VI I V V VI VI VI VI VI VI VI I V V VI V I V VI VI VI VI VI VI VI VI VI V V I V VI VI V VI VI V VI V VI V VI V VI VI V V VI VVI VI V VI VI I V VI V I I I I V V VI V VI VI VI VV V VI VI VI V VI VI VI VI VI VI VI VI VI V I I V VI VI V V V V VI V V VI VI V VI V VI VI V VI VI VI I VI V VI VI V V VI V V VI VI 34 VI VI VI VI VI VI I VIVI VI VI VI VI I VIVI VIVI VIVI VI VI VI VI VI VI VI VII VI VI VI VVI I VI VI V I VI V I I I V IS SI SI SI V VI VI VI VI SI VV SI V SI I IS SI SI SI IS SI SI SI I V
I SI SI SI SI SI SI SI SI SI V SI SI SI SI SI SI SI SI SI IS SI SI SI
V SI SI SI
I SI SI SI IS SI SI SI IS SI SI SI VI V VI I SI SI VSI I VI VI VI VI VI IS SI SI SI IS SI SI V SI IS SI SI SI IS SI SI SI I I VI IS SI SI SI I SI V SI SI V IS SI SI SI V VI SI SI VI SI I I I IS SI SI SI IS SI SI SI I I I I VV V VI VI VI VI V VI V V V I V VI VI VI VI VI VI VIVI VIVI VI VIIVI VI VI VI VI VVI I VI VI VIVIIVI VIVI VIVI
VI VI VI VVI VIVI VI V VI VI VVI VI VI VI VI VI VI
VI VI V I
VI V I V V
V I I I V I V V V
VI V I VI VI VV V VI I 6
I V V I V V I V V I I I
V V I VI VI VI VV V V I VI
VI VI V I VI I VI I VI VI VI VI VI
I V I V V
I V V V V V
V I V V V
I V VI V
V V V V V
V 33 V
V
V
V V V V V V
V V V
V
VI V
V
VI V
V
V V V
V V
I V V V V
V V
V
V VI
I V
V V
V V V
V V V
I V V
V V
V
V
V VI
V
V
V V I V V V V V
V V V
VI V V
V I
V V
V SI SI ISI SI
V V V V V
I V SI SI
V SI SI ISI SI SI SISI SI ISI SI SI SISI SI ISI SI ISI SI V SI SI ISI SI ISI SI V SI SI
V
V SI SI ISI SI I V ISI SI
V SI SI
ISI SI ISI SI
V SI SI ISI SI
ISI SI ISI SI
VI V V
V V V
V V
I V V V
V V V V
V VI
V
V VI V V V
V V
V D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D
V D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D
V I V D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D V D D D D D D D D D D D D D D D D D D V D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D
D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D V
V D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D
D D D D D D D D D D D D D D D D D D I D D D D D D
D D D D D D D D D D D D D D D D D D D D D D D D V D D D D D D
D D D D D D V D D D D D D D D D D D D D D D D D D D D D D D D
D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D V
V V V
V V
VI V
V
V V
V I V V
V
VI V
V
V V V
V
V
I V
1 V 2 V
V V
V
V VI
V
V VI V V V
V V
IS SI SI V SI IS SI SI SI
V
V VI V
V
V VI V
V 3 V V V V V
VI V
V
V V
V VI V
I V
V V V V V
V V V
V
V VI V
V
V
V I V
V V V
I V V V
V V
V
V V VI V
V 4 V
V SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI IS IS IS SI SI SI SI SI SI SI
V V
5
Scale: NTS Scale: V
V SI SI ISI SI V
37
V 35 D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D
V V
ISI SI ISI SI 36 ISI SI V ISI SI ISI SI SI SISI SI ISI SI SI SISI SI ISI SI ISI SI ISI SI ISI SI ISI SI ISI SI A A A A A A A A ISI SI ISI SI A A A A A A A A A A A A ISI SI ISI SI A A A A A A A A A A A A ISI SI ISI SI ISI SI ISI SI A A A A
ISI SI ISI SI A A A A A A A A SI IS IS IS IS IS IS
A A A A SI IS IS IS IS IS IS A A A A let Lnmr niomna oslat Client: LandmarkEnvironmentalConsultants SI IS IS IS IS IS ISIS ISIS IS IS IS IS ISIS IS IS IS V IS IS IS IS SI IS IS IS IS IS IS SI IS IS IS IS IS IS Date: September2010 SI IS IS IS IS IS IS SI IS IS IS IS IS IS SI IS IS IS IS IS IS SI IS IS IS IS IS IS SI IS IS IS IS IS IS
PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE
Map 2Locationsof Anabats V V D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D
KEY D D D D D D D D D D D D D D D D D D D D D D D D VVVVVVV V VVVVVVV V VVVVVVV V V V VVVVVVV VVVVVVV VVVVVVV V V VVVVVVV VVVVVVV V S I VVVVVVV V I Polygon Lcat Lines Cat Point Pcat VVVVVVV V I I I VVVVVVV V I I I Pcat Polygon Lcat Lines Cat Point V V Lcat Lcat Lcat Lines Lines Lines Cat Cat Cat Point Point Point Pcat Pcat Pcat Polygon Polygon Polygon Lines Cat Point Pcat Polygon Lcat VVVVVVV V Lcat Lines Cat Point Pcat Polygon I Pcat Polygon Lcat Lines Cat Point I I Pcat Polygon Lcat Lines Cat Point I V Pcat Polygon Lcat Lines Cat Point Pcat Polygon Lcat Lines Cat Point I I V Pcat Polygon Lcat Lines Cat Point V V V V Pcat Polygon Lcat Lines Cat Point V V I V I V I I I V I I I V VVVVV V I I I I V I V V V V V V V I V I V I I I V I I I V ! V I ! I ! ! ! I ! ! ! I V 1 I ! V ! V V V ! V V V ! I ! V I V I I I 1 V I I I V LAND NORTH OF MARNELPARKOF NORTH LAND A V I I I I V I V V V V V V V I V I V I I I V I I I V V I I I I V I V V V V V V V I V I V I I I V I I I V V I I I I V I IS V V V V V V V I Tel: 01962866113email:[email protected] V I V I I I V I I I V V V I I I I I Phase 1 Habitat Survey Habitat 1 Phase
boundary site Assessment ISI SI
Defunct species-poor hedgerow species-poor Defunct hedgerow Species-rich trees with hedgerow Species-rich ditch Dry Arable grassland semi-improved Poor grassland semi-improved Species-rich, woodland plantation Mixed woodland plantation Coniferous woodland plantation Broadleaved trees broadleaved semi-natural Scattered woodland broadleaved Semi-natural (Appendix II) (Appendix Targetnote water Standing water Running J: Dry ditch Dry J: G: Running Water Running G: A: Broadleaved Semi-natural A:Broadleaved tlpPopley-OS1.dwg Polyline tlpPopley-OS1.dwg Water Standing G: J: Intact Hedge Native Speicies-rich Native Hedge Intact J: Species-rich Native Hedge/Trees J: Species-poor Hedge Defunct J: values> other A: Broadleaved Semi-natural A:Broadleaved tlpPopley-OS1.dwg Polyline tlpPopley-OS1.dwg Water Standing G: ditch Dry J: B: Poor semi-improved grassland semi-improved B:Poor Scattered A:Scrub Dense/Continuous A:Scrub Plantation A:Mixed Plantation A:Coniferous Plantation A:Broadleaved Semi-improved B:Neutral J: Arable values> other A: Broadleaved Semi-natural A:Broadleaved Water Running G: tlpPopley-OS1.dwg Polyline tlpPopley-OS1.dwg Water Standing G: B: Poor semi-improved grassland semi-improved B:Poor Scattered A:Scrub Dense/Continuous A:Scrub Plantation A:Mixed Plantation A:Coniferous Plantation A:Broadleaved Semi-improved B:Neutral J: Arable values> other J: Dry ditch Dry J: A: Broadleaved Semi-natural A:Broadleaved Water Running G: tlpPopley-OS1.dwg Polyline tlpPopley-OS1.dwg Water Standing G: B: Poor semi-improved grassland semi-improved B:Poor Scattered A:Scrub Dense/Continuous A:Scrub Plantation A:Mixed Plantation A:Coniferous Plantation A:Broadleaved Semi-improved B:Neutral J: Arable values> other J: Dry ditch Dry J: A: Broadleaved Semi-natural A:Broadleaved Water Running G: tlpPopley-OS1.dwg Polyline tlpPopley-OS1.dwg Water Standing G: B: Poor semi-improved grassland semi-improved B:Poor Scattered A:Scrub Dense/Continuous A:Scrub Plantation A:Mixed Plantation A:Coniferous Plantation A:Broadleaved Semi-improved B:Neutral J: Arable values> other SI IS IS IS IS IS IS SI SIS IS V IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS SI SIS IS IS IS V 1 BecksMews108StockbridgeRoad V V BASINGSTOKE V V V Winchester HampshireSO226RN V V Report Anabat Number, As Referencedin Development Boundary D D D D D D V D D D D D D D D D D D D D D D D D D A A A FIGURE 8 FIGURE V VVVVVVV V V I Pcat Polygon Lcat Lines Cat Point V I V V I V ! V I V V I V V I V V VI I V VI VI V www.ecosa.co.uk VI VI J: Dry ditch Dry J: A: Broadleaved Semi-natural A:Broadleaved Water Running G: G: Standing Water Standing G: B: Poor semi-improved grassland semi-improved B:Poor Scattered A:Scrub Dense/Continuous A:Scrub Plantation A:Mixed Plantation A:Coniferous Plantation A:Broadleaved Semi-improved B:Neutral J: Arable Speicies-rich Native Hedge Intact J: VIVI VI Species-rich Native Hedge/Trees J: V Species-poor Hedge Defunct J: values> other V IVIVI V V V V V Status: Draft V SI SI ISI SI V V D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D V V V V V V ISI SI ISI SI A A A A SI IS IS IS IS IS IS D D D D D D D D D D D D D D D D D D D D D D D D VVVVVVV V I Pcat Polygon Lcat Lines Cat Point V I V I ! V I V I V I V I J: Dry ditch Dry J: A: Broadleaved Semi-natural A:Broadleaved Water Running G: tlpPopley-OS1.dwg Polyline tlpPopley-OS1.dwg Water Standing G: B: Poor semi-improved grassland semi-improved B:Poor Scattered A:Scrub Dense/Continuous A:Scrub Plantation A:Mixed Plantation A:Coniferous Plantation A:Broadleaved Semi-improved B:Neutral J: Arable values> other 100 100 100 100 100 ETL ETL ETL ETL 100 ETL 100 ETL ETL ETL 50 5 Jan 12 Reproduced with the permission of the controller of Her Majesty’s Stationery Office. © Crown Copyright - Licence No. AR100017235 100 ETL 200 200 200 200 200 200 200 200 200 5 300 300 300 300 300 300 300 ETL ETL ETL ETL 300 ETL ETL ETL ETL 3 4 300 ETL 400 400 400 400 400 400 400 400 G Meters Meters Meters Meters Meters Meters Spier's Copse Spier's Spier's Copse Spier's Copse Spier's Copse Spier's Copse Spier's Meters Meters Spier's Copse Spier's Spier's Copse Spier's Spier's Copse Spier's Track Track Track Track Track Track Track Track G 6 Track 400 Track Track Track Track Track Track Track G Meters Spier's Copse Spier's G Track 2 Track 7 Track Track Track Track Track Track Track Track 78.6m 78.6m 78.6m 78.6m 78.6m 78.6m 78.6m 78.6m 8 G MARL'S LANE MARL'S MARL'S LANE MARL'S LANE MARL'S LANE MARL'S LANE MARL'S MARL'S LANE MARL'S MARL'S LANE MARL'S MARL'S LANE MARL'S Track Pond Pond Pond Pond Pond Pond Pond Pond 78.6m 1 78.6m 78.6m 78.6m 78.6m 78.6m 78.6m 78.6m 78.6m Marl's Marl's Copse Marl's Marl's Copse Marl's Copse Marl's Copse Marl's Copse Marl's Marl's Copse Marl's Marl's Copse Marl's Marl's Copse MARL'S LANE MARL'S G Pond 9 Track Track Track Track Track Track Track Track 78.6m Marl's Marl's Copse Barn Copse A Great Germans Marl's Lane Marl's Lane Marl's Lane Marl's Lane Marl's Lane Marl's Lane Marl's Lane Marl's Lane Copse (part) Track Seven Acre Piece Acre Seven Seven Acre Piece Acre Seven Piece Acre Seven Seven Acre Piece Acre Seven Piece Acre Seven Seven Acre Piece Acre Seven Marl's Lane Seven Acre Piece Acre Seven ISI SI ISI SI Seven Acre Piece Acre Seven ISI SI SI SI SI SI SI SI ISI SI SI SI SI SI SI SI ISI SI 15 ISI SI Barn CopseB 15 15 15 15 ISI SI ISI SI ISI SI 15 ISI SI 15 15 Path (um)Path (um) Path (um) Path (um) Path (um) Path (um) Path (um) Path (um) 13 16 13 13 13 13 16 16 16 16 13 16 13 16 13 16 V V V V V V 67 V V 67 67 67 31 67 31 31 31 31 67 31 V 67 V V V V 67 31 31 V V V CLOSE JERSEY JERSEY CLOSE JERSEY CLOSE JERSEY CLOSE JERSEY CLOSE JERSEY V V V V V JERSEY CLOSE JERSEY V CLOSE JERSEY 65 JERSEY CLOSE JERSEY V 65 65 65 65 V 65 V V V V V 65 65 V V 8 8 8 8 8 V V 8 El Sub Sta V V V El Sub Sta V El Sub Sta El Sub Sta El Sub Sta 8 V 8 El Sub Sta El Sub Sta V V El Sub Sta 23 23 23 23 23 V V V V V 23 V SI 23 SI SI SI SI V 23 V SI MARL'S LANE MARL'S Marl's Lane V SI MARL'S LANE MARL'S LANE MARL'S LANE MARL'S LANE MARL'S V V V SI V 37 LANE MARL'S V 37 37 37 37 MARL'S LANE MARL'S V Marl'sCopse MARL'S LANE MARL'S 37 V Marl'sCopse Marl'sCopse Marl'sCopse Marl'sCopse V 37 Marl'sCopse V V V 37 V Marl'sCopse V Marl'sCopse D D D D D D D D D D D D D D D D V D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D V D D D D D D D D D D D D D D D D Seven Acre Piece Acre Seven V 63 Track V V V V D D D D D D D D D D D D D D D D 63 63 63 63 Track Track Track D D D D Track D D D D D D D D D D D D V 63 Track V 63 ISI SI Track ISI SI V Track 63 Track Track Track Track Track V 15 V V V V Track V Track Track V V Path (um) V V V V V V V 13 16 V V V V V V V V V V 30 30 30 30 30 30 67 30 30 31 V 49 49 49 49 49 49 JERSEY CLOSE JERSEY 49 49 V 48 65 48 56 48 48 48 56 56 56 48 56 56 V 44 48 48 44 44 44 44 56 56 44 8 44 BasingForest BasingForest BasingForest 44 BasingForest BasingForest El Sub Sta V BasingForest BasingForest BasingForest 23 V SI MARL'S LANE MARL'S V 75.6m 75.6m 75.6m 75.6m 75.6m 37 75.6m 75.6m Marl'sCopse 75.6m Great Germans Copse Germans Great V Copse Germans Great Copse Germans Great Great Germans Copse Germans Great Copse Germans Great Barn Copse Barn Barn Copse Barn Copse Barn Copse Barn Copse Barn Great Germans Copse Germans Great D D D D D D D D D D D D D D D D Great Germans Copse Germans Great Barn Copse Barn Upper Parrott's Copse Parrott's Upper Great Germans Copse Germans Great Upper Parrott's Copse Parrott's Upper Copse Parrott's Upper Upper Parrott's Copse Parrott's Upper Copse Parrott's Upper Barn Copse Barn Barn Copse Barn V Upper Parrott's Copse Parrott's Upper 63 SI Track Upper Parrott's Copse Parrott's Upper 41 Copse Parrott's Upper 41 41 41 41 Track 41 V 50 41 41 50 50 50 50 50 50 50 V V 51 51 51 51 51 51 51 51 30 49 Track Track Track Track Track Track Track 48 Track 56 4 4 BasingF 75.6m Great Germans Copse Germans Great Barn Cops Barn Upper Parrott's Cops Parrott's Upper 41 50 Scale: NTS Scale: 51 Track Track ISI SI ISI SI Track Track Track Track ISI SI SI SI SI SI SI SI ISI SI Track SI SI SI SI SI SI ISI SI ISI SI Track ISI SI Track SI SI ISI SI ISI SI e orest e D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D D VVVVVVV VVVVVVV VVVVVVV VVVVVVV VVVVVVV VVVVVVV Survey_areas Lcat Lines Legend Pcat Polygon name VVVVVVV Polygon name Lcat Survey_areas name Lines Legend Lcat Survey_areas name Lines Lcat Survey_areas Legend Lines Lcat Legend Lines Legend Pcat Polygon Pcat Polygon Pcat name Polygon Pcat Survey_areas V Lines Legend Pcat Polygon name Survey_areas Lcat Polygon name Survey_areas Lcat Lines Legend Pcat Pcat Polygon name Survey_areas Lcat Lines Legend VVVV D D D D D D SI 1 LAND NORTH OF MARNELPARKOF NORTH LAND VV Track ISI SI ISI SI Woodland survey results survey Woodland D D Survey reference Survey hedgerow species-rich Native grassland semi-improved Poor scrub Scattered scrub continuous Dense woodland plantation Mixed woodland plantation Coniferous woodland plantation Broadleaved woodland broadleaved Semi-natural areas Survey spiers J: Intact Hedge Native Speicies-rich 1 1 8 8 2 2 3 3 5 Jan 12 Reproduced with the permission of the controller of Her Majesty’s Stationery Office. © Crown Copyright - Licence No. AR100017235 1 8 1 8 4 4 2 2 G 3 3 G G G 4 4 G G 5 5 5 5 Scale: NTS Scale: let adakEvrnetlCnutns Client: LandmarkEnvironmentalConsultants let adakEvrnetlCnutns Client: LandmarkEnvironmentalConsultants Date: January2012 Date: January2012 © © PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE Map 1LocationsofSurveyed Trees Map 1LocationsofSurveyed Trees let adakEvrnetlCnutns Client: LandmarkEnvironmentalConsultants KEY KEY Date: January2012 © PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE ECOSA Ltd2012 Map 1LocationsofSurveyed Trees ECOSA Ltd2012 Plan supplied by ECOSA by supplied Plan KEY 1 1 ECOSA Ltd2012 1 LAND NORTH OF MARNELPARKOF NORTH LAND let adakEvrnetlCnutns Client: LandmarkEnvironmentalConsultants Date: January2012 Tree survey for bat roost potential roost bat for Treesurvey © PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE Map 1LocationsofSurveyed Trees Tel: 01962866113email:[email protected] Tel: 01962866113email:[email protected] KEY Tel: 01962866113email:[email protected] ECOSA Ltd2012 Reserved. Licence No. Reserved. Licence AR 152684 the ControllerofMHSO.CrownCopyright with permissionof fromtheOrdnanceSurveyMap Contains datareproduced Revision H ‘Assessment SiteBoundaryPlan’,DrawingNo.5,19/12/2011, Basemap: ©BartonWillmore Reserved. Licence No. Reserved. Licence AR 152684 the Controller ofMHSO. Crown Copyright with permission of from the Ordnance Survey Map Contains data reproduced Revision H ‘Assessment Site Boundary Plan’,Drawing No. 5, 19/12/2011, Basemap: © BartonWillmore Reserved. Licence No. Reserved. Licence AR 152684 the Controller ofMHSO. Crown Copyright with permission of from theOrdnance Survey Map Contains data reproduced Revision H ‘Assessment Site Boundary Plan’, Drawing No. 5,19/12/2011, Basemap: ©Barton Willmore 1 1 BecksMews108StockbridgeRoad Woodland and hedgerow and Woodland potential roost bat high medium/ with trees of Location boundary site Assessment Winchester HampshireSO226RN Phase 2Level Number of Trees Surveyedto Hedgerow Woodland Development Boundary 1 BecksMews108StockbridgeRoad 1 BecksMews108StockbridgeRoad BASINGSTOKE Tel: 01962866113 email: [email protected] Winchester HampshireSO226RN Phase 2Level Number of Trees Surveyedto Winchester HampshireSO226RN Phase 2Level Number of Trees Surveyedto Hedgerow Woodland Development Boundary Hedgerow Woodland Development Boundary Reserved. Licence No. Reserved. Licence AR 152684 the ControllerofMHSO.CrownCopyright with permissionof fromtheOrdnanceSurveyMap Contains datareproduced Revision H ‘Assessment SiteBoundaryPlan’,DrawingNo.5,19/12/2011, Basemap: ©BartonWillmore FIGURE 10 FIGURE 1 Becks Mews 108 Stockbridge Road Winchester Hampshire SO22 6RN Phase 2Level Number of Trees Surveyedto Hedgerow Woodland Development Boundary www.ecosa.co.uk www.ecosa.co.uk www.ecosa.co.uk www.ecosa.co.uk Status: Final-Rev. 1 Status: Final-Rev. 1 Status: Final-Rev. 1 Status: Final-Rev. 1 5 Jan 12 Reproduced with the permission of the controller of Her Majesty’s Stationery Office. © Crown Copyright - Licence No. AR100017235 G G G G G G Scale: NTS Scale: let adakEvrnetlCnutns Client: LandmarkEnvironmentalConsultants Date: January2012 © PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE Map 3ResultsofPhase2 Transects let adakEvrnetlCnutns Client: LandmarkEnvironmentalConsultants let adakEvrnetlCnutns Client: LandmarkEnvironmentalConsultants Client: LandmarkEnvironmentalConsultants let adakEvrnetlCnutns Client: LandmarkEnvironmentalConsultants let adakEvrnetlCnutns Client: LandmarkEnvironmentalConsultants Date: January2012 Date: January2012 Date: January2012 Date: January2012 Date: January2012 © © © © © PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE Map 3ResultsofPhase2 Transects PHASE 1 AND 2ECOLOGICAL SURVEYS PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE MARNEL PARK, BASINGSTOKE PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE Map 3ResultsofPhase2 Transects Map 3ResultsofPhase2 Transects Map 3ResultsofPhase2 Transects Map 3ResultsofPhase2 Transects KEY KEY KEY KEY KEY KEY ECOSA Ltd2012 ECOSA Ltd2012 ECOSA Ltd2012 ECOSA Ltd2012 ECOSA Ltd2012 ECOSA Ltd2012 Plan supplied by ECOSA by supplied Plan LAND NORTH OF MARNELPARKOF NORTH LAND let adakEvrnetlCnutns Client: LandmarkEnvironmentalConsultants Date: January2012 © Tel: 01962866113email:[email protected] Tel: 01962866113email:[email protected] Tel: 01962866113email:[email protected] Tel: 01962866113email:[email protected] Tel: 01962866113email:[email protected] PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE Map 3ResultsofPhase2 Transects Reserved. Licence No. Reserved. Licence AR 152684 the ControllerofMHSO.CrownCopyright with permissionof fromtheOrdnanceSurveyMap Contains datareproduced Revision H ‘Assessment SiteBoundaryPlan’,DrawingNo.5,19/12/2011, Basemap: ©BartonWillmore Reserved. Licence No. Reserved. Licence AR 152684 No. Reserved. Licence AR 152684 the ControllerofMHSO.CrownCopyright with permissionof the ControllerofMHSO.CrownCopyright with permissionof fromtheOrdnanceSurveyMap Contains datareproduced fromtheOrdnanceSurveyMap Contains datareproduced Revision H Revision H ‘Assessment SiteBoundaryPlan’,DrawingNo.5,19/12/2011, ‘Assessment SiteBoundaryPlan’,DrawingNo.5,19/12/2011, Basemap: ©BartonWillmore Basemap: ©BartonWillmore Reserved. Licence No. Reserved. Licence AR 152684 the ControllerofMHSO.CrownCopyright with permissionof fromtheOrdnanceSurveyMap Contains datareproduced Revision H ‘Assessment SiteBoundaryPlan’,DrawingNo.5,19/12/2011, Basemap: ©BartonWillmore Reserved. Licence No. Reserved. Licence AR 152684 the ControllerofMHSO.CrownCopyright with permissionof fromtheOrdnanceSurveyMap Contains datareproduced Revision H ‘Assessment SiteBoundaryPlan’,DrawingNo.5,19/12/2011, Basemap: ©BartonWillmore Tel: 01962866113email:[email protected] KEY ECOSA Ltd2012 1 BecksMews108StockbridgeRoad 1 BecksMews108StockbridgeRoad 1 BecksMews108StockbridgeRoad 1 BecksMews108StockbridgeRoad 1 BecksMews108StockbridgeRoad Reserved. Licence No. Reserved. Licence AR 152684 the Controller of MHSO. Crown Copyright with permission of fromtheOrdnance Survey Map Contains datareproduced Revision H ‘Assessment SiteBoundaryPlan’, DrawingNo.5,19/12/2011, Basemap: ©BartonWillmore Winchester HampshireSO226RN Hedgerow Woodland Development Boundary Winchester HampshireSO226RN Winchester HampshireSO226RN Winchester HampshireSO226RN Winchester HampshireSO226RN Hedgerow Hedgerow Woodland Woodland Development Boundary Development Boundary Hedgerow Woodland Development Boundary Hedgerow Woodland Development Boundary Serotine Soprano Pipistrelle Common Pipistrelle Woodland and hedgerow and Woodland bat Whiskered/Brandt's bat Daubenton's Serotine pipistrelle Soprano pipistrelle Common boundary site Assessment Serotine Serotine Soprano Pipistrelle Soprano Pipistrelle Common Pipistrelle Common Pipistrelle Serotine Soprano Pipistrelle Common Pipistrelle Serotine Soprano Pipistrelle Common Pipistrelle Whiskered/Brandt’s Possible Daubenton’s Whiskered/Brandt’s Whiskered/Brandt’s Possible Daubenton’s Possible Daubenton’s Whiskered/Brandt’s Possible Daubenton’s Whiskered/Brandt’s Possible Daubenton’s 1 BecksMews108Stockbridge Road Bat survey results survey Bat BASINGSTOKE Winchester HampshireSO226RN Hedgerow Woodland Development Boundary Tel: 01962 866113email: [email protected] Serotine Soprano Pipistrelle Common Pipistrelle Whiskered/Brandt’s Possible Daubenton’s Reserved. Licence No. Reserved. Licence AR 152684 the ControllerofMHSO.CrownCopyright with permissionof fromtheOrdnanceSurveyMap Contains datareproduced Revision H ‘Assessment SiteBoundaryPlan’,DrawingNo.5,19/12/2011, Basemap: ©BartonWillmore FIGURE 11FIGURE 1 Becks Mews 108 Stockbridge Road www.ecosa.co.uk www.ecosa.co.uk www.ecosa.co.uk www.ecosa.co.uk www.ecosa.co.uk Winchester Hampshire SO22 6RN Hedgerow Woodland Development Boundary Serotine Soprano Pipistrelle Common Pipistrelle Whiskered/Brandt’s Possible Daubenton’s www.ecosa.co.uk www.ecosa.co.uk let adcp niomna oslat Client: LandscapeEnvironmentalConsultants Date: September2010 PHASE 1 AND 2ECOLOGICAL SURVEYS MARNEL PARK, BASINGSTOKE Map 3ResultsofPhase2 Transects KEY Status: Final-Rev. 1 Status: Final-Rev. 1 Status: Final-Rev. 1 Status: Final-Rev. 1 Status: Final-Rev. 1 Tel: 01962866113 email:[email protected] 1 BecksMews108Stockbridge Road Winchester Hampshire SO226RN Development Boundary Serotine Soprano Pipistrelle Common Pipistrelle Status: Final-Rev. 1 Whiskered/Brandt’s Bat Daubenton’s Bat Status: Final-Rev. 1 www.ecosa.co.uk Status: Draft 0 0 0 0 0 0 0 0 0 ,0 ,0 1,200 1,100 1,000 900 800 700 600 500 400 300 200 100 0 0 0 0 0 0 50 50 50 50 50 50 100 100 100 100 100 L L L L L L L L L L 200 200 200 200 200 0 ! ! ! ! ! 5 Jan 12 Reproduced with the permission of the controller of Her Majesty’s Stationery Office. © Crown Copyright - Licence No. AR100017235 300 300 300 300 300 50 100 L 400 400 400 400 400 L 200 G G ! G 500 500 500 500 500 300 G Meters Meters Meters Meters Meters ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! 400 Meters G ! ! ! ! 500 ! Meters G ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! Scale: NTS Scale: type, date_ type, 2166_badger_survey type, date_ type, 2166_badger_survey type, date_ type, date_ type, 2166_badger_survey 2166_badger_survey type, date_ type, 2166_badger_survey ! ! ! ! ! ! ! ! ! ! ! ! L ! ! L ! L L ! L ! ! ! ! LAND NORTH OF MARNELPARKOF NORTH LAND predated by badgers (16/7/10) badgers by predated probably nest wasps out Dug Badger snuffle holes (27/5/10) holes snuffle Badger (27/9/10) latrine Badger (5/5/10) badger a by predated probably skin, Hedgehog (27/9/10) badger a by predated probably skin, Hedgehog Assessment site boundary site Assessment Badger survey results survey Badger 2166_dormouse_surveyarea Boundary_Site wasp nest, 16/7/10 nest, wasp 27/5/10 snuffle, 27/9/10 latrine, 27/9/10 skin, hedgehog 5/5/10 skin, Hedgehog values> other wasp nest, 16/7/10 nest, wasp 27/5/10 snuffle, 27/9/10 latrine, 27/9/10 skin, hedgehog 5/5/10 skin, Hedgehog values> other G WW G S BC S Y G G CC WR BC CH G S Y S GS G WH MA R Scale: NTS Scale: Green listed Green Amber listed Amber Red listed Red WW WW WW WW WW WW WW WW WW WW WW WW WH WR MA WH WH WH WH WH WH WH WH WH WH WH WR WR WR WR WR WR WR WR WR WR WR MA MA MA MA MA MA MA MA MA MA MA CH BC GS CC CH CH CH CH CH CH CH CH CH CH CH BC BC BC BC BC BC BC BC BC BC BC GS GS GS GS GS GS GS GS GS GS GS CC CC CC CC CC CC CC CC CC CC CC LI LI LI LI LI LI LI LI LI LI LI LI LAND NORTH OF MARNELPARKOF NORTH LAND R S Y S S S S S S S S S S R R R R R R R R S R R R Y Y Y Y Y Y Y Y Y Y Y Assessment site boundary site Assessment Skylark Linnet Willow warbler Willow Mallard Whitethroat Robin woodpecker spotted Great Chaffinch Chiffchaff Blackcap Yellowhammer Wren Breeding birds survey birds Breeding BASINGSTOKE FIGURE 13 FIGURE David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX I DATA SEARCH INFORMATION The Landmark Practice Appendix I David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Appendix I: Summary of records of some of the notable species within 1km of the site (excluding bats) Common name Scientific name Date recorded and Status: local, national and location international Mammals West European Erinaceus 1997, Oakridge, Lychpit UK BAP / NERC Act (Section 41) Hedgehog europaeus 1999-2007, Spier's Copse, UK BAP / Hampshire BAP / NERC Act Brown Hare Lepus europaeus Vyne Farm Area, Popley (Section 41) UK BAP / Hampshire BAP / NERC Act Harvest Mouse Micromys minutus 2007, Location not supplied (Section 41) EU Habitats Directive Annex IV / UK BAP / Hampshire BAP / WCA Muscardinus Dormouse 2004, Location not supplied (Schedule 5) / European Protected avellanarius Species /NERC Act (Section 41) /County Interest Birds Northern 2000-2004, Location not Accipiter gentilis WCA Schedule 1 / Nationally Rare Goshawk supplied Acrocephalus 2005-2008, Vyne Water Reed Warbler Hampshire BAP scirpaceus Meadows BOCC Red List / UK BAP / Hampshire Skylark Alauda arvensis 2007, Vyne Water Meadows BAP / NERC Act (Section 41) 2000-2008, Sherborne St Kingfisher Alcedo atthis John, Vyne Lake & WCA Schedule 1 Meadows 2001-2002, The Vyne Water Garganey Anas querquedula WCA Schedule 1 / Nationally Rare Meadows 2000-2008, Vyne Lake & Gadwall Anas strepera Hampshire BAP Meadows, Basing Forest 1996-2002, Basingstoke, Vyne Water Meadows, Tree Pipit Anthus trivialis UK BAP / NERC Act (Section 41) Basing Forest, Carpenter’s Down Wood 2002-2006, Vyne Lake & Pochard Aythya ferina Hampshire BAP Meadows 2002-2008, Vyne Water Dunlin Calidris alpina Hampshire BAP Meadows Caprimulgus 2003-2008, Location not BOCC Red List /UK BAP / Hampshire Nightjar europaeus supplied BAP /NERC Act (Section 41) 2002-2006, Sherborne St Lesser Redpoll Carduelis cabaret UK BAP / NERC Act (Section 41) John, Morgaston Wood 1997-2004, Houndmills BOCC Red List / UKBAP Carduelis Linnet Basingstoke, Vyne Water / Hampshire BAP /NERC Act (Section cannabina Meadows 41) Little Ringed 2002-2008, Location not Charadrius dubius WCA Schedule 1 Plover supplied Black Tern Chlidonias niger 2002, Vyne Water Meadows WCA Schedule 1 Circus Marsh Harrier 2004, Vyne Water Meadows Nationally Rare aeruginosus UKBAP Coccothraustes Hawfinch 2001, Vyne Water Meadows Hampshire BAP coccothraustes NERC Act (Section 41) 2001-2009, Sherborne St Common UKBAP Cuculus canorus John, Vyne Water Meadow, Cuckoo NERC Act (Section 41) Basing Forest The Landmark Practice Appendix I David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Common name Scientific name Date recorded and Status: local, national and location international 1996-2006, Vyne Lake & BOCC Red List / UK BAP / Hampshire Lesser Spotted Dendrocopos Meadows, Carpenter’s BAP Woodpecker minor Down Wood NERC Act (Section 41) 2003-2008, Sherborne St Little Egret Egretta garzetta Hampshire BAP / Nationally Rare John, Vyne Water Meadows BOCC Red List / UK BAP / Hampshire Emberiza Corn bunting 1999, Sherborne St John BAP calandra NERC Act (Section 41) Emberiza 2007, Sherborne St John, BOCC Red List / UK BAP /NERC Act Yellowhammer citrinella Vyne Water Meadows (Section 41) Merlin Falco columbarius 2004, Sherborne St John Hampshire BAP /WCA Schedule 1 1999-2006, Location not Peregrine Falcon Falco peregrinus WCA Schedule 1 supplied 2000-2005, Location not Hobby Falco subbuteo Hampshire BAP / WCA Schedule 1 supplied 1996-2006, Sherborne St Fringilla John, Queen Marys Brambling WCA Schedule 1 montifringilla College, Vyne Lake & Meadows, Chineham Gallinago 2002-2008, Vyne Lake & Snipe Hampshire BAP gallinago Meadows BOCC Red List / UK BAP / Hampshire Black-Tailed 2000-2005, Vyne Water BAP Limosa limosa Godwit Meadows WCA Schedule 1 / NERC Act (Section 41) BOCC Red List / UK BAP / Hampshire BAP 2002-2006, Location not Woodlark Lullula arborea WCA Schedule 1 / NERC Act (Section supplied 41) Luscinia 1999-2001, Carpenter’s Hampshire BAP Nightingale megarhynchos Down Wood Mergus Hampshire BAP Goosander 2008, The Vyne Lake merganser 2002-2008, Location not Hampshire BAP / WCA Schedule 1 / Red Kite Milvus milvus supplied Nationally Rare 2002-2006, Sherborne St Hampshire BAP Yellow Wagtail Motacilla flava John, Vyne Lake & Meadows 2000-2008, Sherborne St BOCC Red List / UK BAP / Hampshire Spotted Muscicapa striata John, Vyne Lake & BAP Flycatcher Meadows NERC Act (Section 41) Numenius 2005, The Vyne Water Eurasian Curlew UK BAP / NERC Act (Section 41) arquata Meadows Passer 200-2009, Sherborne St BOCC Red List / UK BAP / NERC Act House Sparrow domesticus John, Basing Forest (Section 41) Philomachus 2001-2007, Vyne Lake & Ruff WCA Schedule 1 pugnax Meadows Phoenicurus 2000-2005, Location not Black Redstart WCA Schedule 1 / NR ochruros supplied Phylloscopus Wood Warbler 1998, Queen Marys College UK BAP / NERC Act (Section 41) sibilatrix 1994-2005, Houndmills, Golden Plover Pluvialis apricaria Sherborne St John, Popley, Hampshire BAP Vyne Lake & Meadows The Landmark Practice Appendix I David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Common name Scientific name Date recorded and Status: local, national and location international 2001-2006, Morgaston Wood, Vyne Water BOCC Red List / UKBAP Willow Tit Poecile montanus Meadows, Carpenter’s NERC Act (Section 41) Down Wood 2001-2006 ,Sherborne St John, Morgaston Wood, Marsh Tit Poecile palustris Vyne Lake & Meadows, BOCC Red List / UKBAP Carpenter’s Down Wood, Chineham 2006-2009, Sherborne St Prunella Hedge Accentor John, Basing Forest, Vyne UK BAP / NERC Act (Section 41) modularis Water Meadows BOCC Red List / UK BAP / Hampshire 2007-2009, Basing Forest, Bullfinch Pyrrhula pyrrhula BAP Spier's Copse, Chineham NERC Act (Section 41) Recurvirostra Pied Avocet 2008, Vyne Water Meadows WCA Schedule 1 avosetta BOCC Red List / UK BAP / Hampshire 1999-2006, Vyne Lake, Turtle Dove Streptopelia turtur BAP Carpenter’s Down Wood NERC Act (Section 41) 2005-2009, Basing Forest, BOCC Red List / UKBAP Starling Sturnus vulgaris Popley NERC Act (Section 41) 2004-2005, Vyne Water Wood Sandpiper Tringa glareola WCA Schedule 1 Meadows GreeNationally 2002-2008, Vyne Lake & Tringa nebularia WCA Schedule 1 Scarcehank Meadows 2000-2008, Vyne Lake & Green Sandpiper Tringa ochropus WCA Schedule 1 Meadows 2000-2008, Vyne Lake & Redshank Tringa totanus Hampshire BAP Meadows 2002-2006, Vyne Lake & Redwing Turdus iliacus WCA Schedule 1 Meadows BOCC Red List /UKBAP Turdus 2009, Basing Forest Main Song Thrush Hampshire BAP /NERC Act (Section philomelos Site 41) 1997-2008, Sherborne St Fieldfare Turdus pilaris John, Popley, Vyne Lake & WCA Schedule 1 Meadows 2005, The Vyne Water BOCC Red List / UKBAP Ring Ouzel Turdus torquatus Meadows NERC Act (Section 41) 1994-2008, Houndmills, Northern UK BAP / Hampshire BAP Vanellus vanellus Popley, Sherborne St John, Lapwing NERC Act (Section 41) Vyne Lake & Meadows Amphibians and reptiles UK BAP / WCA (Schedule 5) Slow-worm Anguis fragilis 2008, Basing Forest / NERC Act (Section 41) 1997, Grove Farm, Popley Common Toad Bufo bufo UK BAP /NERC Act (Section 41) Swale & Gcn Underpasses 2003-2006, Popley Ponds, UK BAP / WCA (Schedule 5)/NERC Act Grass Snake Natrix natrix Carpenter's Down Wood (Section 41) EU Habitats Directive Annex IV / 2002-2009, Kiln Farm UK BAP / Hampshire BAP / WCA Great Crested Cottage, Popley ponds Triturus cristatus (Schedule 5) / European Protected Newt (various), Basing Forest Species / County Interest / NERC Act (various ponds) (Section 41) / County Interest The Landmark Practice Appendix I David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Common name Scientific name Date recorded and Status: local, national and location international 2008, Popley Swale & Gcn UK BAP / WCA (Schedule 5) / NERC Common Lizard Zootoca vivipara Underpasses Act (Section 41) Invertebrates (Lepidoptera) Knot Grass Acronicta rumicis 2007, Sherborne St John, UK BAP / NERC Act (Section 41) Agriopis 2007, Morgaston Wood, Spring Usher North Hampshire Scarce (VC12) leucophaearia Sherborne St John Angerona 2000-2007, 1-km Square Orange Moth County Scarce prunaria Su6356, Sherborne St John UK BAP / NERC Act (Section 41) / Large Nutmeg Apamea anceps 2007, Sherborne St John County Scarce Small Clouded Apamea unanimis 2007, Sherborne St John County Scarce Brindle Purple Emperor Apatura iris 2005-2006, Basing Forest Hampshire BAP / County Scarce Small Brindled Apocheima 2007, Sherborne St John North Hampshire Scarce (VC12) Beauty hispidaria festoon Apoda limacodes 2007, Sherborne St John Hampshire BAP / Nationally Scarce 2005-2007, Morgaston Orange Archiearis Wood, Carpenter's Down North Hampshire Scarce (VC12) Underwing parthenias Wood Dark Green 1997, Carpenter's Down Argynnis aglaja County Scarce Fritillary Wood 1996-2007, Sherbourne St Silver-washed Argynnis paphia John, Basing Forest, Hampshire BAP / County Interest fritillary Carpenter's Down Wood Argyresthia 2007, Sherborne St John County Rare curvella Red-necked Atolmis rubricollis 2007, Sherborne St John County Scarce Footman Caradrina Mottled Rustic 2007, Sherborne St John UK BAP / NERC Act (Section 41) morpheus Cerastis White-marked 2007, Sherborne St John Nationally Scarce leucographa Dark Chestnut Conistra ligula 2007, Sherborne St John North Hampshire Scarce (VC12) Depressaria 2007, Sherborne St John County Rare chaerophylli Small Square- 2007, Sherborne St John Diarsia rubi UK BAP / NERC Act (Section 41) spot Dicallomera Dark Tussock 2004, Basingstoke County Scarce fascelina Ectoedemia 2007, Sherborne St John County Rare decentella Orange footman Eilema sororcula 2007, Sherborne St John Hampshire BAP Ephestia 2007, Sherborne St John County Rare parasitella Sharp-angled Euphyia 2007, Sherborne St John County Scarce Carpet unangulata Eupithecia Plain Pug 2004, Basingstoke County Scarce simpliciata Eupithecia 2007, Sherborne St John Slender Pug North Hampshire Scarce (VC12) tenuiata Varied compta Hadena compta 2007, Sherborne St John North Hampshire Scarce (VC12) Campion Hadena rivularis 2007, Sherborne St John North Hampshire Scarce (VC12) The Landmark Practice Appendix I David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Common name Scientific name Date recorded and Status: local, national and location international Hemistola 2007, Sherborne St John Small Emerald UK BAP / NERC Act (Section 41) chrysoprasaria The Rustic Hoplodrina blanda 2007, Sherborne St John UK BAP / NERC Act (Section 41) Lampropteryx 2007, Sherborne St John Water Carpet County Scarce suffumata 1996-2006, Morgaston White Admiral Limenitis camilla Wood, Basing Forest, UK BAP / NERC Act (Section 41) Carpenter's Down Wood Lithophane 2007, Sherborne St John Pale Pinion North Hampshire Scarce (VC12) hepatica Lobophora 2007, Sherborne St John Seraphim North Hampshire Scarce (VC12) halterata 2004-2007, Sherborne St Brindled Beauty Lycia hirtaria UK BAP / NERC Act (Section 41) John, Basingstoke Melanchra Dot Moth 2007, Sherborne St John UK BAP / NERC Act (Section 41) persicariae Metriotes lutarea 2005, Morgaston Wood Nationally Scarce UK BAP / Hampshire BAP 2006-2007, Morgaston Drab looper Minoa murinata NERC Act (Section 41) / Nationally Wood Scarce Mompha 2007, Sherborne St John County Rare ochraceella Monopis obviella 2007, Sherborne St John County Rare Mythimna 2007, Sherborne St John White-point North Hampshire Scarce (VC12) albipuncta Shoulder-striped 2007, Sherborne St John Mythimna comma UK BAP / NERC Act (Section 41) Wainscot Gothic Naenia typica 2007, Sherborne St John North Hampshire Scarce (VC12) Nephopterix 2007, Sherborne St John Nationally Scarce angustella Bulrush Nonagria typhae 2003, Basingstoke North Hampshire Scarce (VC12) Wainscot Powdered 2007, Sherborne St John Orthosia gracilis UK BAP / NERC Act (Section 41) Quaker Lead-coloured 2007, Sherborne St John Orthosia populeti County Scarce Drab Pine Beauty Panolis flammea 2007, Sherborne St John North Hampshire Scarce (VC12) Perizoma 2007, Sherborne St John Maple Pug County Scarce inturbata Philereme 2007, Sherborne St John Brown Scallop North Hampshire Scarce (VC12) vetulata Ptilodontella 2007, Sherborne St John Maple Prominent County Scarce cucullina 1976-1998, Basing Forest, UK BAP / NERC Act (Section 41) / Grizzled Skipper Pyrgus malvae Carpenter's Down Wood County Interest White Letter 1996-2006, Morgaston UK BAP / Hampshire BAP / NERC Act Satyrium w-album Hairstreak Wood, Basing Forest (Section 41) / County Scarce 2007, Sherborne St John Nationally Notable Sitochroa palealis Nationally Scarce Spilosoma 2007, Sherborne St John White Ermine UK BAP / NERC Act (Section 41) lubricipeda 2000-2007, 1-km Square Buff Ermine Spilosoma luteum UK BAP / NERC Act (Section 41) Su6356, Sherborne St John The Landmark Practice Appendix I David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Common name Scientific name Date recorded and Status: local, national and location international Early Moth Theria primaria 2007, Sherborne St John North Hampshire Scarce (VC12) Blood-vein Timandra comae 2007, Sherborne St John UK BAP / NERC Act (Section 41) 2007, Sherborne St John, The Cinnabar Tyria jacobaeae UK BAP / NERC Act (Section 41) Chineham Watsonalla 2003-2007, Sherborne St Oak Hook-tip UK BAP / NERC Act (Section 41) binaria John, Basingstoke Higher plants (Flowering Plants) Narrow-leaved Alisma 2009, Popley County Rare Water-plantain lanceolatum 2007, Chineham, Nationally Scarce / Hampshire BAP / Marsh-mallow Althaea officinalis Basingstoke County Scarce Green-Flowered Epipactis 2001, Basing Forest, Nationally Scarce / Hampshire BAP / Helleborine phyllanthes Carpenter’s Down Wood County Scarce Stinking Helleborus Nationally Scarce / Hampshire BAP / 2008 ,Sherborne St John Hellebore foetidus County Scarce 2000-2009, Morgaston Hyacinthoides Wood, Sherborne St John, Bluebell WCA Schedule 8 non-scripta Basing Forest, Chineham Business Park Narrow-leaved 2003, Basing Forest, Lotus glaber North Hampshire Rare (VC12) Bird's-foot-trefoil Carpenter’s Down Wood Hybrid Cinquefoil Potentilla x mixta 2006, Sherborne St John North Hampshire Rare (VC12) Common Water- Ranunculus 1996-2006, Popley Pond County Scarce crowfoot aquatilis Thread-leaved Ranunculus 2009, Popley County Rare Water-crowfoot trichophyllus Sanguisorba Great Burnet 2009, Popley County Scarce officinalis Common Thalictrum flavum 1996-2009, Popley Pond North Hampshire Scarce (VC12) Meadow-rue Strawberry Trifolium 1996, Popley Pond North Hampshire Rare (VC12) Clover fragiferum Blue Water- Veronica 2008, Sherborne St John County Interest Speedwell anagallis-aquatica The Landmark Practice Appendix I David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX II PHASE 1 HABITAT SURVEY TARGET NOTES AND SPECIES LISTS The Landmark Practice Appendix II David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX II: PHASE 1 HABITAT SURVEY TARGET NOTES 5 May 2010 1. Section of hedgerow with trees, which reaches a width of at least ten metres at the gap described in Target Note 2 below. A subsequent hedgerow survey suggests this may be two hedgerows and an overgrown lane in between. Please see table below for a species list. English Name Scientific Name Trees/Understorey Hawthorn Crataegus monogyna Dog Rose Rosa canina Blackthorn Prunus spinosa Bramble Rubus fruticosus Pedunculate Oak Quercus robur Hazel Corylus avellana Ground Flora Ivy Hedera helix Cleavers Galium aparine Couch grass Elymus repens Dandelion Taraxacum agg False Oat Grass Arrhenatherum elatius 2. A large gap in hedgerow in excess of ten metres in width (Photograph 3 refers) rendering the hedgerow defunct. The gap has been very recently re-planted with hazel (Corylus avellana), blackthorn (Prunus spinosa) and hawthorn (Crataegus monogyna) to re-connect the established hedgerow on either side. There is a mature pedunculate oak in the gap, the upper branches of which are not connected to the trees to the south of the gap. Garden waste has been deposited in the woodland margin on either side of the gap, effectively forming two compost heaps. The ground comprises areas of bare soil, grass and the species recorded are listed below. The grass is recently sown and newly germinated. English Name Scientific Name Ground Flora Bluebell Hyacinthoides non-scripta Lords and ladies Arum maculatum Tansy Tanacetum vulgare Greater plantain Plantago major Spear thistle Cirsium arvense Dandelion Taraxacum agg Cleavers Galium aparine Lesser celandine Ficaria verna Creeping buttercup Ranunculus repens Common field speedwell Veronica persica Annual meadow grass Poa annua Red dead-nettle Lamium purpureum 3. Hedgerow with trees, which grades into the edge of Basing Forest at its northern end. Please see table below for species list: English Name Scientific Name Trees/Understorey The Landmark Practice Appendix II David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Hawthorn Crataegus monogyna Blackthorn Prunus spinosa Pedunculate oak Quercus robur Bramble Rubus fruticosus Ground Flora Broad-leaved dock Rumex obtusifolius Greater stitchwort Stellaria holostea Cleavers Galium aparine Ivy Hedera helix Common bent Agrostis capillaris Red fescue Festuca rubra Dandelion Taraxacum agg Tufted vetch Vicia cracca Creeping bent Agrostis stolonifera Common field speedwell Veronica persica Common nettle Urtica dioica 4. Radio Transmitter with a metal fence surround. Hawthorn has been planted on the field margin along the fence. Please see table below for other species: English Name Scientific Name Ground Flora Bramble Rubus fruticosus Wood dock Rumex sanguineus Ivy Hedera helix False oat grass Arrhenatherum elatius Wild angelica Angelica sylvestris Creeping thistle Cirsium arvense Common nettle Urtica dioica 5. A four to five metre margin along the woodland edge with a canopy of ash (Fraxinus excelsior), mature oak (Quercus sp.) and an apple species (Malus sp.) with good aerial connectivity. The understorey comprises holly (Ilex aquifolium), blackthorn, hawthorn, sycamore (Acer pseudoplatanus), hazel, field maple (Acer campestre), field rose (Rosa arvensis), black bryony (Tamus communis) and elder (Sambucus nigra). The groundflora comprises greater stitchwort, cleavers, bramble, ground ivy (Glechoma hederacea), herb Robert (Geranium robertianum), wood false-brome (Brachypodium sylvaticum), wood dock, Lords and Ladies, bush vetch (Vicia sepium) and early dog violet (Viola reichenbachiana) and common dog violet (Viola riviana). 6. The north-eastern margin of the Phase Two field comprises a three metre wide and approximately fifty metre long strip of tall ruderal, ephemeral/short perennial species and grasses (Photograph 4 refers). There is a defunct hedgerow at the western end of the habitat and this habitat may have been a hedgerow previously. To the east is Basing Forest and to the north is a field of rough, species-poor grassland and the species present include tufted hair grass and cocks foot. Please see below for species recorded in the ruderal habitat: Ground Flora Field pansy Viola arvensis Wood dock Rumexsanguineus Cut-leaved cranesbill Geranium dissectum The Landmark Practice Appendix II David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Cow parsley Anthriscus sylvestris Cleavers Galium aparine Ground ivy Glechoma hederacea Common bent Agrostis capillaris Shepherds purse Capsella bursa-pastoris Dandelion Taraxacum agg Annual meadow grass Poa annua Creeping bent Agrostis stolonifera Common field speedwell Veronica persica Fennel Foeniculum vulgare Meadow fox-tail Alopecurus pratensis Cock’s foot Dactylis glomerata Tansy Tanacetum vulgare Red dead nettle Lamium purpureum Creeping thistle Cirsiuim arvense Common nettle Urtica dioica Euphorbia sp. Euphorbia sp. 7. A defunct hedgerow which may previously have continued in an easterly direction towards Basing Forest. Please see the table below for the species list: Hedgerow Apple species Malus sp. Blackthorn Prunus spinosa Elder Sambucus nigra Dogwood Cornus sanguinea Dog Rose Rosa canina Ground Flora Hawthorn Crataegus monogyna False oat grass Arrhenatherum elatius Wood dock Rumexsanguineus Cow parsley Anthriscus sylvestris Cleavers Galium aparine Ground ivy Glechoma hederacea Hogweed Heracleum sphondylium Red fescue Festuca rubra Annual meadow grass Poa annua Creeping bent Agrostis stolonifera Garlic mustard Alliaria petiolata Soft brome Bromus mollis Brome sp. (poss. barren) Bromus sp. Bindweed sp. Convolvulaceae 8. A mature pedunculate oak, marks the start of Spier’s Copse, a broad-leaved woodland which marks the central portion of the northern site boundary . The woodland edge of this part of Spier’s Copse comprises ash in the east and oak in the west (Photograph 6 refers). 9. A dry ditch runs along the southern edge of this section of Spier’s Copse. It is up to fifty centimetres deep in places and between one and two metres wide. There was evidence that standing water collects in the ditch at times (a tide mark of leaves plus mud which settled out from suspension). The ground level in the woodland is lower than that of the adjacent arable field to the south and the eastern part of the ditch is more of a step feature marking the transition between ground levels. Please see the table below for the ground flora species recorded in the ditch and woodland edge between Target Notes 9 and 13: The Landmark Practice Appendix II David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Ground Flora Hogweed Heracleum sphondylium False oat grass Arrhenatherum elatius Wood dock Rumexsanguineus Cow parsley Anthriscus sylvestris Cleavers Galium aparine Ground ivy Glechoma hederacea Lords and ladies Arum maculatum Annual meadow grass Poa annua Bramble Rubus fruticosus Meadow buttercup Ranunculus acris Common nettle Urtica dioica Greater stitchwort Stellaria holostea Common ragwort Senecio jacobaea Spear thistle Cirsium Wood avens Geum urbanum Herb robert Geranium robertianum Yorkshire fog Holcus lanatus Ivy Hedera helix Common field speedwell Veronica persica Wood false brome Brachypodium sylvaticum 10. A mature, ivy-clad pedunculate oak on the woodland edge of Spier’s Copse. Woodland edge forms this portion of the northern site boundary and adjacent trees to the west are oaks and to the east are ash. The understorey includes field maple (Acer campestre), hawthorn, and a rose species (Rosa sp.). To the north is broadleaved woodland described in TN 38. 11. A mature pedunculate oak with a hole in the trunk which could offer bat roosting potential. There is a stain running from the bottom lip of the hole. The woodland behind has frequent common dog violets (Viola riviana). Additional ground flora include lesser burdock (Arctium minus), lesser celandine, cock’s foot, perennial rye grass (Lolium Perenne) and Yorkshire fog (Holcus lanatus). 12. A young English elm (Ulmus procera) situated to the left of a mature pedunculate oak with a large section of bark missing at it’s base. A narrow footpath runs into the wood at this point. 13. This section of woodland edge comprises primarily young English elm saplings, remnant lying dead trunks, several standing dead trunks and ash saplings. There are many gaps in the woodland edge although connectivity is maintained above. There is a dry ditch in front of the trees and a woodland ride behind. 14. Woodland edge dominated by ash with rare pedunculate oak. The understorey is dominated by blackthorn and the ground flora by perennial rye grass. The woodland behind is a mixed plantation of pine (Pinus sp.) and species such as ash. 15. An un-cultivated, disturbed field corner with tall ruderal and ephemeral/short perennial vegetation (Photograph 5 refers). The species present include common figwort (Scrophularia nodosa), creeping thistle, greater plantain, spear thistle, hoary willowherb (Epilobium parviflorum), and an unidentified willowherb species (Epilobium sp.). The Landmark Practice Appendix II David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report 16. A wooden fence marks the western site boundary (Photograph 5 refers). To the west of the fence and adjacent to the site is an approximately twenty five metre width of immature plantation woodland and the species present comprise: Scrub Field maple Acer campestre Silver birch Betula pendula Ash Fraxinus excelsior Wild cherry Prunus avium Pedunculate oak Quercus robur Rowan Sorbus aucuparia Hazel Corylus avellana Hawthorn Crataegus monogyna Holly Ilex aquifolium Blackthorn Prunus spinosa Spindle Euonymus europaeus Buckthorn Rhamnus catharticus Guelder rose Viburnum opulus The ground flora along the fence line comprises tall ruderal and ephemeral/short perennial vegetation and the species present include the following: Ground Flora Common ragwort Senecio jacobaea Willowherb sp. Epilobium sp. Cut-leaved cranesbill Geranium dissectum Dandelion Taraxacum agg. Fennel Foeniculum vulgare Hoary willowherb Epilobium parviflorum Spear thistle Cirsium vulgare Meadow buttercup Ranunculus acris False oat-grass Arrhenatherum elatius Tansy Tanacetum vulgare Common field speedwell Veronica persica Yorkshire fog Holcus lanatus Curled dock Rumex crispus Meadow foxtail Alopecurus pratensis Hedge woundwort Stachys sylvatica Smooth meadow-grass Poa pratensis Cabbage sp. Brassica sp. 17. A wooden fence marks the southern site boundary. To the south of the fence and adjacent to the site is an approximately fifteen metre wide habitat comprising immature woodland and scrub species. This habitat forms a buffer between the site and the Marnel Park development. The vegetation is less than five metres in height and comprise the same species as listed in Target Note 16 above plus the following: Ground Flora Cock’s foot Dactylis glomerata Bristly oxtongue Helminthotheca echioides Great willowherb Epilobium hirsutum Horsetail sp. Equisetum sp. Red fescue Festuca rubra The Landmark Practice Appendix II David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report 18. A six to eight metre wide area with no wood/scrub planting. This is likely to be a future access point between the Marnel Park development and the site. 19. The Phase Two field comprising an arable crop of beans (Photograph 1 refers). 20. An arable crop of cereal (Photograph 2refers). Arable flora interest The following species were recorded throughout the field of beans. They were also recorded scattered around the margins of the cereal field. This difference between the two probably reflects differences in the management of the two fields: English Name Scientific Name IAPA score1 Hampshire Status2 Field pansy Viola arvensis 0 Sharp-leaved fluellen Kickxia spuria 2 Locally frequent Round-leaved fluellen Kickxia elatine 3 Locally common Fool’s parsley Aethusa cynapium 0 Common field- Veronica persica 0 speedwell Field bindweed Convolvulus arvensis 0 Knotgrass Polygonum aviculare 0 Shepherd’s purse Capsella bursa-pastoris 0 Black-bindweed Fallopia convolvulus 0 Cleavers Galium aparine 0 Scarlet pimpernel Anagallis arvensis 0 Dwarf spurge Euphorbia exigua 6 Locally common Sun spurge Euphorbia helioscopia 0 Broad-leaved spurge Euphorbia platyphyllos 3 Rare Red dead-nettle Lamium rubrum 0 Stinking chamomile Anthemis cotula 7 Locally common/common on chalk and clay soils in N. Common fumitory Fumaria officinalis 0 Redshank Persicaria maculosa 0 Groundsel Senecio vulgaris 0 Small toadflax Chaenorhinum minus 1 Locally common Cut-leaved crane’s-bill Geranium dissectum 0 A willowherb Epilobium sp. 0 Sterile brome Anisantha sterilis 0 Fat hen (?) Chenopodium album (?) 0 Field horsetail Equisetum arvense 0 Black-grass Alopecurus myosuroides 2 Locally common Field forget-me-not Myosotis arvensis 0 Marsh cudweed Gnaphalium uliginosum 0 Common poppy Papaver rhoeas 0 Soft-brome Bromus hordeaceus 0 Total IAPA Score 243 1 Byfield, A. and Wilson, P.J. (2005) Important Arable Plant Areas: identifying priority sites for arable plant conservation in the United Kingdom. Plantlife International, Salisbury, UK. 2 Hampshire Flora 3 For clay soils, a score of 20-29 is considered to represent a site of County Importance (Byfield and Wilson, 2005). The Landmark Practice Appendix II David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report 21. A mature pedunculate oak with some bat roost potential on the bank of a ditch. 22. An isolated mature pedunculate oak in the grain arable field 23. An isolated mature pedunculate oak in grain arable field 24. Small ditch around the western balancing lagoon, continuing between the two arable fields supporting shallow water at the time of survey and flowing towards the north-west. The banks support poor semi-improved grassland and are approximately five metres wide and the species present include cowslip, meadowsweet (Filipendula ulmaria), cow parsley, water- cress (Rorippa nasturtium-aquaticum), bramble, cleavers, field horsetail (Equisetum arvense), false oat-grass, tufted vetch, bristly ox-tongue, curled dock, common knapweed, hedge woundwort, common nettle, dog’s mercury, greater stitchwort, tufted hair-grass, cleavers, beaked hawks-beard (Crepis vesicaria) , hedge mustard, false wood-brome, hogweed, hedge bedstraw (Galium album), meadow vetchling, cut-leaved crane’s-bill, great willowherb, red fescue, dogwood, lord’s-and-ladies, elder, rose, creeping bent and meadow foxtail. 25. The western balancing pond has poor semi-improved grassland in the base dominated by creeping bent plus curled dock, creeping buttercup, ragwort, dandelion and white clover (Trifolium repens) (Photograph 2 refers). 26. The banks of the balancing pond support rough grassland with false oat-grass, curled dock, dandelion, creeping thistle, creeping buttercup, ragwort, a crucifer, hedge woundwort, bristly ox-tongue and creeping cinquefoil (Potentilla reptans). The outflow to the pond supports creeping bent, creeping buttercup, great willowherb, field horsetail and ox-eye daisy (Leucanthemum vulgare). 27. An uncultivated disturbed area supporting creeping buttercup, curled dock, tufted vetch, common couch (Elymus repens), cut-leaved crane’s-bill and black grass. 28. The Phase One field is cropped almost up to the edge of the screening planting. Immediately adjacent to the eastern field boundary is a planted area with bark mulch and ruderal species including cut-leaved crane’s-bill, curled dock, black-grass and willowherbs. 29. An uncultivated two metre margin running inside the southern boundary of the Phase One field which is very disturbed and supports docks, false oat-grass, dandelion, common mouse-ear (Cerastium fontanum) and cut-leaved crane’s-bill. This margin widens out in the south-eastern corner and supports willowherbs, docks, cut-leaved crane’s-bill, black-grass and common ragwort. 30. A small grassland area within the area of plantation bordering the site. The species present include meadow vetchling, bird’s-foot trefoil (Lotus corniculatus), common knapweed and ribwort plantain (Plantago lanceolata). 31. To the south of the fence and adjacent to the site is an area of young woodland planting comprising similar species to those listed in TN 16. The ground flora comprises Yorkshire fog (Holcus lanatus), field horsetail, dandelion, false oat-grass, ragwort, willowherbs, creeping thistle, bristly ox-tongue and hedge woundwort. The Landmark Practice Appendix II David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report 32. A four to five metre wide rough, grassy margin is located on the western side of the eastern balancing pond and along the southern boundary of the Phase Two field. The species present include cut-leaved crane’s-bill, broad-leaved dock, dandelion, spear thistle, curled dock, common vetch, common knapweed, black grass, cleavers, field horsetail, wood avens, bristly ox-tongue and creeping thistle. 33. A two metre wide rough grass margin along the northern side of the easternmost balancing lagoon comprising false oat-grass, common bent, common couch, ground ivy, hoary ragwort (Senecio erucifolius), hoary willowherb, a willowherb species and common field speedwell (Veronica persica). 34. The eastern balancing pond with supports a known population of great-crested newts (Triturus cristatus). The pond is surrounded by species-rich grassland comprising red fescue, meadow fescue, sweet vernal grass (Anthoxanthum odoratum), Yorkshire Fog, common knapweed (Centaurea nigra), burnet saxifrage (Pimpinella saxifraga), cowslip (Primula vulgaris), field scabious (Knautia arvensis), greater knapweed (Centaurea scabiosa), lady’s bedstraw (Galium verum), lesser trefoil (Trifolium dubium), perforate St John’s Wort (Hypericum perforatum), agrimony (Agrimonia eupatria), meadow vetchling (Lathyrus pratensis) and tufted vetch (Vicia cracca). Surrounding Habitats Woodland survey 5. A four or five metre wide margin on the woodland (Basing Forest) edge along the eastern site boundary with a canopy of ash, mature oak and apple with good aerial connectivity (Photograph 4 refers). The understorey comprises holly, blackthorn, hawthorn, sycamore (Acer pseudoplatanus), hazel, field maple (Acer campestre), field rose (Rosa arvense), black bryony (Tamus communis) and elder. The groundflora comprises greater stitchwort, cleavers, bramble, ground ivy, herb Robert, wood false-brome, bush vetch and early and common dog violets. 35. The main Basing Forest woodland beyond the marginal area comprises a canopy of young sycamore, ash and oak to approximately twenty metres in height and provides around eighty percent ground cover. There is a limited understorey comprising hawthorn, blackthorn and some hazel, but connectivity is poor. The ground flora is also sparse and supports greater stitchwort, wood false-brome, hedge mustard, ground-ivy, wood avens (Geum urbanum), lord’s-and-ladies and common nettle. 36. To the east of TN35 the woodland composition changes and comprises an area of pine (Pinus sp.) plantation. 37. North of TN35 and north of the site is an area of young, coppiced sycamore with young pine plantation beyond. 38. A woodland (Spier’s Copse) with a canopy approximately fifteen metres in height and providing approximately seventy percent ground cover and moderate aerial connectivity. It is is dominated by even aged young ash trees, indicating human intervention. The under storey The Landmark Practice Appendix II David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report is very sparse and comprises occasional hawthorn, blackthorn (local thicket), hazel, elder, and variable cover young ash regrowth. The ground flora comprises the following species: English Name Scientific Name Frequency Wood false-brome Brachypodium sylvaticum Abundant Cow parsley Anthriscus sylvestris Occasional Hedge mustard Alliaria petiolata Occasional False oat-grass Arrhenatherum elatius Locally Occasional Germander speedwell Veronica chamaedrys Common dog violet Viola riviniana Wood avens Geum urbanum Bramble Rubus fruticosus agg. Solomon’s-seal Polygonatum Ground ivy Glechoma hederacea Occasional Hedge woundwort Stachys sylvatica Greater stitchwort Stellaria graminea Frequent Field rose Rosa arvensis Cowslip Primula veris Rare Bush vetch? Vicia sepium Wood sedge Carex sylvatica Wood/curled dock Rumex sanguineus/crispus Dog’s-mercury Mercurialis perennis Lord’s-and-ladies Arum maculatum Early purple orchid Orchis mascula Bluebell Hyacinthoides non-scripta Rare An orange tip butterfly (Anthocharis cardamines) recorded. 39. A pine plantation with young ash and rare birch (Betula sp.) and oak. The canopy is approximately fifteen metres in height and provides sixty percent ground cover. The understorey has poor aerial connectivity and comprises scattered (locally denser) hawthorn, rose, blackthorn and rare grey willow (Salix cinerea). The ground flora is sparse providing less than fifty percent ground cover and comprises much bramble with false wood-brome, hairy St. John’s-wort (Hypericum hirsutum), cowslip (Primula veris), cleavers, tufted vetch, dog’s mercury, black bryony, soft rush (Juncus effusus) and wood dock. 40. Several willows form the original woodland margin (Spier’s Copse) adjacent to the woodland plantation to the east and were identified provisionally as crack willow (Salix fragilis). The ground flora includes the following species: Ground Flora Tufted hair-grass Deschampsia cespitosa Soft rush Juncus effusus Hard rush Juncus inflexus Square stalked St John’s wort Hypericum tetrapterum Wood sedge Carex sylvatica Sedge sp. (remote?) Carex sp. (remota) Wood avens Geum urbanum Goat willow Salix caprea 41. A scrubby block of Spier’s Copse with occasional ash and pine in canopy. The understorey comprises dense blackthorn with grey willow and rarely hazel. The Landmark Practice Appendix II David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report 42. The canopy of the southern part of the western section of Spier’s Copse comprises oak, pine, field maple and Norway maple (Acer platanoides). The under storey is much more open than the habitat described at TN41 and comprises blackthorn, hawthorn, dog rose and bramble. The ground flora is sparse with common nettle, ground ivy, hedge mustard and locally frequent wood false-brome. 43. A mature pedunculate oak next to a stile which provides access to a field of semi- improved grassland. The boundary between the grassland and the woodland plantation to the east comprises wooden post and wire fencing. The edge of Spier’s Copse is situated to the north and the boundary between the grassland and Spier’s Copse consists of wooden post and wire fencing. 44. Two mature pedunculate oaks. 45. A two metre wide strip of grassland between the fence and plantation woodland comprising the following species: Ground Flora Teasel Dipsacus fullonum Cock’s foot Dactylus glomerata Bramble Rubus fruticosus Tufted vetch Vicia cracca Ground ivy Glechoma hederacea Greater plantain Plantago major Creeping thistle Cirsium arvense False oat-grass Arrhenatherum elatius Timothy Pleum pratense Curled dock Rumex crispus The Landmark Practice Appendix II David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX III PHASE 1 HABITAT SURVEY PHOTOGRAPHS The Landmark Practice Appendix III David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX III: SURVEY PHOTOGRAPHS Photograph 1: A view of the western part of the site, taken outside the southern boundary within the central great crested newt habitat corridor within the Marnel Park development looking northwards. The Phase One field is in the middle of the view, the Phase Two field and Spier’s Copse are to the rear. Photograph 2: Looking south across the western balancing pond with the Phase One field beyond. To the south and east lies the Marnel Park development. Photograph 3: The gap in the defunct hedgerow on the eastern boundary of the site. The Landmark Practice Appendix III David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Photograph 4: Defunct hedgerow and tall ruderal/short perennial habitat on the north- eastern boundary of the site. To the rear is Basing Forest. Photograph 5: A view westward from edge of Basing Forest in the north-eastern corner of the site. Spier’s Copse is to the rear, the Phase Two field to the left and the species-poor grassland adjacent to the site is to the right. Photograph 6: Spier’s Copse SINC, adjacent to the Phase Two field in the central portion of the northern site boundary. The Landmark Practice Appendix III David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Photograph 7: The woodland inside the central portion of Spier’s Copse The Landmark Practice Appendix III David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX IV HEDGEROW SURVEY RESULTS The Landmark Practice Appendix IV David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX IV: Hedgerow Survey Results The Hedgerow Regulations apply to hedgerows that are 20 m or more long and hedgerows that are less that 20 m long if they are continuous with hedgerows at each end. Ecologically important hedgerows are those that fall into the following categories relevant to the site (Hedgerow Regulations 1997 survey criteria): • The hedgerow contains species in part I of Schedule 1, Schedule 5, or Schedule 8 of the Wildlife & Countryside Act 1981, or various other defined species including certain Red Data Book species; • The hedgerow is adjacent to a public right of way (not including an adopted highway) and contains at least four woody species as defined in Schedule 3 of the regulations, plus at least two Associated Features*; • The hedgerow includes one or more of the following: - At least 7 woody species, - At least 6 woody species plus at least three Associated Features*, - At least 6 woody species including either black poplar (Populus nigra); large-leaved lime (Tilia platyphyllos), small-leaved lime (Tilia cordata) or wild service tree (Sorbus domestica) - At least 5 woody species and at least four Associated Features*. *Associated Features are as follows: • A bank or wall for at least half the length; • A ditch for at least half the length; • Gaps over no more than 10% of the length; • At least one standard tree per 50m; • At least three ground flora woodland species as defined in Schedule 2 of the Regulations within 1 m of the hedgerow; • Connections scoring four or more points (where connection with a hedgerow counts as one, a broad-leaved woodland or pond counts as two); • A parallel hedge within 15 m. NB The last two features do not apply if a public right of way is being included in the criteria. If hedgerows are 30 m or less in length then the whole hedge will be surveyed. If the hedgerow is between 30-100 m in length, the central 30 m section will be surveyed. Hedgerows between 100-200 m long will be divided in two and the central 30 m of the two sections will be surveyed. Hedgerows over 200m will be divided into three sections and the central 30 m of each third will be surveyed. The Landmark Practice Appendix IV David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Hedgerow N. hedgerow (TN7, Figure 8 refers) E. hedgerow A (TNs 1-3, Figure 8 refer) E. hedgerow B (TNs 1-3, Figure 8 refer) Hedgerow length, height and 90 m 120 m 120 m width (approximate) Legally protected / rare species No No No present (as defined in the Hedgerow Regulations) Adjacent to public right of way? No Yes Yes Woody species present / 30m Blackthorn (Prunus spinosa) Blackthorn (Prunus spinosa) Blackthorn (Prunus spinosa) (Schedule 3 species, Hedgerow Hawthorn (Crataegus monogyna) Hawthorn (Crataegus monogyna) Hawthorn (Crataegus monogyna) Regulations, in bold) Dog rose (Rosa canina) Dog rose (Rosa canina) Dog rose (Rosa canina) Bramble (Rubus fruticosus agg.) Bramble (Rubus fruticosus agg.) Bramble (Rubus fruticosus agg.) Elder (Sambucus nigra) Dogwood (Cornus sanguina) Dogwood (Cornus sanguina) Field maple (Acer campestre) Hazel (Corylus avellana) Hazel (Corylus avellana) Pedunculate oak (Quercus robur) Pedunculate oak (Quercus robur) Wild privet (Ligustrum vulgare) Wild privet (Ligustrum vulgare) Turkey oak (Quercus cerris) 4 qualifying species 8 qualifying species 7 qualifying species Associated Features Bank/wall present Slight bank? Slight bank? Slight bank? Ditch present No No No Percentage of gaps present < 10% but peters out part way across field c. 10% (whole hedgerow). C. 14 m gap, part c. 10% (whole hedgerow) boundary replanted with blackthorn, field maple and hawthorn (construction access for mast?) Standard trees present No Yes (1 Quercus robur & 1 Acer campestre) Yes (6 Quercus robur) Woodland ground flora present Common nettle (Urtica dioica) Ivy (Hedera helix) Cleavers (Galium aparine) (Schedule 2 species, Hedgerow Cleavers (Galium aparine) Cleavers (Galium aparine) Cow parsley (Anthriscus sylvestris) Regulations, in bold) Soft brome (Bromus hordeaceus) Cow parsley (Anthriscus sylvestris) False oat grass (Arrhenatherum elatius) White bryony (Bryonia dioica) False oat grass (Arrhenatherum elatius) Rough-stalked meadow grass (Poa trivialis) Cow parsley (Anthriscus sylvestris) Rough-stalked meadow grass (Poa trivialis) Wood dock (Rumex sanguineus) False oat grass (Arrhenatherum elatius) Lord’s-and-ladies (Arum maculatum) Bittersweet (Solanum dulcamara) Rough-stalked meadow grass (Poa trivialis) Wood dock (Rumex sanguineus) Ivy (Hedera helix) Barren brome (Anisantha sterilis) Bittersweet (Solanum dulcamara) Lord’s-and-ladies (Arum maculatum) Appendix IV The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Hedgerow N. hedgerow (TN7, Figure 8 refers) E. hedgerow A (TNs 1-3, Figure 8 refer) E. hedgerow B (TNs 1-3, Figure 8 refer) Garlic mustard (Alliaria petiolata) Wood avens (Geum urbanum) Creeping thistle (Cirsium arvense) Black bryony (Tamus communis) Wood dock (Rumex sanguina) Wood false-brome (Brachypodium Forget-me-not (Myosotis sp.) sylvaticum) Hedge woundwort (Stachys sylvatica) Greater stitchwort (Stellaria holostea) Bittersweet (Solanum dulcamara) 0 qualifying species 1 qualifying species 3 qualifying species Connections with other features X1 X4 X4 Parallel hedge No Yes Yes Other information Other species recorded outside surveyed sections (Hedgerows 2a and 2b): Spindle (Euonymus europaeus) Tufted vetch (Vicia cracca) Elder (Sambucus nigra) Hogweed (Heracleum sphondylium) Summary > 20m long > 20m long > 20m long No legally protected/rare species present No legally protected/rare species present No legally protected/rare species present No parallel hedge Parallel hedge Parallel hedge 4 qualifying woody species 8 qualifying woody species 7 qualifying woody species 1or 2 associated features 4 or 5 associated features 5 or 6 associated features Ecologically important under No Yes Yes Hedgerow Regulations 1997? Appendix IV The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX V WOODLAND SURVEY RESULTS The Landmark Practice Appendix V David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX V: WOODLAND SURVEY RESULTS TABLE 1: Main woodland areas surveyed (Figures 2 and 9 refer) Great Marl's Barn Barn Germans Spier's Spier's Spier's Spier's English Name Scientific Name Lane copse A copse B Copse Copse 1 Copse 2 Copse 3 Copse 4 (pt) Canopy species Field maple* Acer campestre R/O R Norway maple Acer platanoides D R Sycamore Acer pseudoplatanus R Silver birch Betula pendula LO R/O R/O Hawthorn Crataegus monogyna O/LF Cypress sp. Cupressus sp. R/LO Ash Fraxinus excelsior R/O O/F R/O D O/F O A Crab apple* Malus sylvestris R/O Spruce Picea sp. R Pine sp. Pinus sp. D LO/F F/A F/LD R Pedunculate oak Quercus robur D R LO R/O R/O(LD) LO Grey willow Salix cinerea R R/O Total (total AWI) 2(0) 3(0) 1(0) 4(1) 3(0) 6(0) 7(1) 6(1) Understorey species Field maple* Acer campestre R/O LO R/O LO R/O Norway maple Acer platanoides O O LF Sycamore Acer pseudoplatanus R Alder Alnus glutinosa R R/O Silver birch Betula pendula R LO/F Dogwood Cornus sanguinea R/O R R Hazel Corylus avellana O F LO LO O/LF O/LF Hawthorn Crataegus monogyna O/F O O O O R/O O Appendix V The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Great Marl's Barn Barn Germans Spier's Spier's Spier's Spier's English Name Scientific Name Lane copse A copse B Copse Copse 1 Copse 2 Copse 3 Copse 4 (pt) Spindle Euonymus europaeus R/O R/O Ash Fraxinus excelsior R/O R/O R/O O/LF F O O Holly* Ilex aquifolium R R R R/O Honeysuckle Lonicera periclymenum R/O O/F O R/O R/O R/O O Crab apple* Malus sylvestris LO Spruce Picea sp. R/O Blackthorn Prunus spinosa O LO/F R/O O LO O/LD Pedunculate oak Quercus robur R R/O R/O Field rose* Rosa arvensis R Dog rose Rosa canina R/O R R/O LO R/O R/O Bramble Rubus fruticosus agg F O/LF A/D O/F O/LF F F/LD F Grey willow Salix cinerea LO/F R R/O Willow sp. Salix sp. R Elder Sambucus nigra R R/O R/O Black bryony Tamus communis R/O R/O R/O English elm Ulmus procera LO Guelder rose* Viburnum opulus R Total (total AWI) 14(3) 8(1) 10(0) 14(0) 14(1) 9(1) 10(2) 9(0) Ground flora species Ferns Broad buckler fern Dryopteris dilatata O R R Male fern Dryopteris filix-mas O/LF LO R R Soft shield fern* Polystichum setiferum R Bracken Pteridium aquilinum LO LF R/LF Total (total AWI) 0(0) 2(1) 2(0) 1(0) 2(0) 3(0) 0(0) 1(0) Appendix V The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Great Marl's Barn Barn Germans Spier's Spier's Spier's Spier's English Name Scientific Name Lane copse A copse B Copse Copse 1 Copse 2 Copse 3 Copse 4 (pt) Grasses, sedges and rushes Creeping bent Agrostis stolonifera LF Sweet vernal-grass Anthoxanthum odoratum VLF/A False oat-grass Arrhenatherum elatius LO/F LF/A LO False brome Brachypodium sylvaticum F F R/LO F/A F/A O(LF/A) F/A Hairy-brome* Bromopsis ramosa R Cock's-foot Dactylis glomerata R/O R/O R/O R Tufted hair-grass Deschampsia caespitosa R/O R/O R/LO LO R/LO LO Red fescue Festuca rubra LO Sweet-grass Glyceria sp. LF Yorkshire fog Holcus lanatus LF R/LO LF Creeping soft-grass* Holcus mollis LF/A LF Wood melic* Melica uniflora LF Rough meadow-grass Poa trivialis O O/F LF LO False fox-sedge Carex otrubae LO LO Remote sedge* Carex remota R/O R LO LO R/O Sedge Carex sp. R Wood-sedge* Carex sylvatica O R/O R/O R LO LF/A R/O O/LF Soft-rush Juncus effusus R R/O R R R LO Hard rush Juncus inflexus R R Total (total AWI) 6(1) 5(2) 5(1) 9(3) 10(3) 10(2) 3(1) 11(4) Dicots Field maple* Acer campestre R/O Norway maple Acer platanoides R/O F Bugle Ajuga reptans LO LO O LF LO Garlic mustard Alliaria petiolata LO LO LO Wild angelica Angelica sylvestris LO R LO Cow parsley Anthriscus sylvestris O/F R/LO R/LO Appendix V The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Great Marl's Barn Barn Germans Spier's Spier's Spier's Spier's English Name Scientific Name Lane copse A copse B Copse Copse 1 Copse 2 Copse 3 Copse 4 (pt) Burdock Arctium sp. R R/O LO/F R R/O R/O R/LO Lord's-and-ladies Arum maculatum R R R R R/O Common mouse-ear Cerastium fontanum R Enchanter's-nightshade Circaea lutetiana LO LO Creeping thistle Cirsium arvense LF LO Marsh thistle Cirsium palustre LO LO R Pignut* Conopodium majus LF Dogwood Cornus sanguinea R Hawthorn Crataegus monogyna R/O R Common spotted orchid Dactylorhiza fuchsii LO R Foxglove Digitalis purpurea R Meadowsweet Filipendula ulmaria R Wild strawberry Fragaria vesca R Ash Fraxinus excelsior O F O/LF LF Common hemp-nettle Galeopsis tetrahit LO Cleavers Galium aparine F F O/F F F R/O(LF) F Herb Robert Geranium robertianum F O/F R/O O/F F O/F Wood avens Geum urbanum F R/O O/F Ground-ivy Glechoma hederacea LO O/LA R O/F O/F F LO/F F Common ivy Hedera helix R/O R/O R/O Hogweed Heracleum sphondylium R Hairy St. John's-wort Hypericum hirsutum LF O/LF LO LO Square-stalked St. John's- wort Hypericum tetrapterum R Yellow archangel* Lamiastrum galeobdolon R LO LO Nipplewort Lapsana communis LO Wild privet Ligustrum vulgare LO Yellow pimpernel* Lysimachia nemorum LO Creeping-Jenny Lysimachia nummularia Dog's mercury Mercurialis perennis R R R/LF LF LO/F LO/F Appendix V The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Great Marl's Barn Barn Germans Spier's Spier's Spier's Spier's English Name Scientific Name Lane copse A copse B Copse Copse 1 Copse 2 Copse 3 Copse 4 (pt) Three-nerved sandwort* Moehringia trinervia R/O Field forget-me-not Myosotis arvensis LO Common twayblade Neottia ovata R Cowslip Primula veris LO Primrose* Primula vulgaris R LO R Blackthorn Prunus spinosa LO/R R/O Creeping buttercup Ranunculus repens LO LO/F LO LO Wood dock Rumex sanguineus R/O O O O/F LO O Sanicle* Sanicula europaea R Common figwort Scrophularia nodosa R R R Bittersweet Solanum dulcamara R R Hedge woundwort Stachys sylvatica R/O R/O LO LO LO LO Lesser stitchwort Stellaria graminea R R/LO R/LO Greater stitchwort Stellaria holostea F LF/A O(LF/A) F/LA LF R/LF LO/F Black bryony* Tamus communis R R R/O R/O Common nettle Urtica dioica LO/F LO LO LO LO Germander speedwell Veronica chamaedrys O R O LO R/O Tufted vetch Vicia cracca R R LO LO Bush vetch* Vicia sepium O LO R LO LO Dog-violet Viola sp. O R O/LF LF R/LO Total (total AWI) 22(3) 19(3) 3(0) 18(2) 32(4) 29(3) 16(1) 26(4) Grand total AWI 7 7 1 7 8 6 4 8 D - dominant, A - abundant, F - frequent, O - occasional, R - rare L - locally * Ancient woodland indicator (AWI) species Appendix V The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report TABLE 2: 5 m areas woodland margin surveyed north of public footpath Marl’s Lane to Sherborne St John Spier's Spier's Spier's Spier's Spier's English Name Scientific Name Copse Copse Copse Copse Copse 5 6 7 8 9 Canopy species Field maple* Acer campestre R Silver birch Betula pendula R/O Cypress sp. Cupressus sp. O Ash Fraxinus excelsior D D R D D Pine sp. Pinus sp. D Wild cherry* Prunus avium R Pedunculate oak Quercus robur R/O R Grey willow Salix cinerea R/O Total (total AWI) 2(0) 1(0) 3(1) 2(0) 5(1) Understorey species Field maple* Acer campestre R R R/O R Silver birch Betula pendula R/O Dogwood Cornus sanguinea R/O Hazel Corylus avellana F O O O O/F Hawthorn Crataegus monogyna R/O O O R/O O Cypress sp. Cupressus sp. R Spindle Euonymus europaeus R Ash Fraxinus excelsior O Holly* Ilex aquifolium R Wild privet Ligustrum vulgare R Honeysuckle Lonicera periclymenum O O/F Blackthorn Prunus spinosa R R/O Pedunculate oak Quercus robur R/O Field rose* Rosa arvensis R Dog rose Rosa canina R/O Bramble Rubus fruticosus agg O O D O Grey willow Salix cinerea R R/O Total (total AWI) 5(1) 7(2) 7(0) 7(1) 8(2) Ground flora species Ferns Broad buckler fern Dryopteris dilatata R R/O Male fern Dryopteris filix-mas R R R R/O Total (total AWI) 1(0) 2(0) 1(0) 1(0) 1(0) Grasses, sedges and rushes False brome Brachypodium sylvaticum A F/A O O/F O/F Cock's-foot Dactylis glomerata R/O Tufted hair-grass Deschampsia caespitosa R/O R/O R Wood melic* Melica uniflora LF False fox-sedge Carex otrubae O/F Remote sedge* Carex remota O/F Thin-spiked wood-sedge* Carex strigosa R The Landmark Practice Appendix V David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Spier's Spier's Spier's Spier's Spier's English Name Scientific Name Copse Copse Copse Copse Copse 5 6 7 8 9 Wood-sedge* Carex sylvatica O O O Hard rush Juncus inflexus R Total (total AWI) 4(2) 3(1) 1(0) 2(0) 7(3) Forbs Field maple* Acer campestre R R/O R Bugle Ajuga reptans R O/LF Garlic mustard Alliaria petiolata LO Wood anemone* Anemone nemorosa R Cow parsley Anthriscus sylvestris O/F R/O Burdock Arctium sp. R R/O R/O Lord's-and-ladies Arum maculatum R R Common spotted orchid Dactylorhiza fuchsii O Ash Fraxinus excelsior R/O Cleavers Galium aparine O/F F O/F Herb Robert Geranium robertianum O O O O Wood avens Geum urbanum O/F O/F O O Ground-ivy Glechoma hederacea O/LF R/O R/O O Common ivy Hedera helix R/O R/O Bluebell* Hyacinthoides non-scripta LF Hairy St. John's-wort Hypericum hirsutum R R/O R LO Yellow archangel* Lamiastrum galeobdolon LO LO Creeping-Jenny Lysimachia nummularia R LF Dog's mercury Mercurialis perennis LO/F LF LO Primrose* Primula vulgaris R Blackthorn Prunus spinosa LO R Wood dock Rumex sanguineus R/O Wood dock Rumex sanguineus R/O Hedge woundwort Stachys sylvatica R/O O O Lesser stitchwort Stellaria graminea R Greater stitchwort Stellaria holostea O/F LF O O/LF Black bryony* Tamus communis R/O R/O O Common nettle Urtica dioica LO Germander speedwell Veronica chamaedrys O LO R/O Bush vetch* Vicia sepium LO R Dog-violet Viola sp. O/F O O O Early dog-violet* Viola reichenbachiana R? Total (total AWI) 23(6) 16(2) 1(0) 14(3) 17(2) Grand total AWI 13 4 1 3 7 D - dominant, A - abundant, F - frequent, O - occasional, R - rare L - locally * Ancient woodland indicator (AWI) species The Landmark Practice Appendix V David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX VI WOODLAND SURVEY PHOTOGRAPHS The Landmark Practice Appendix VI David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX VI: WOODLAND SURVEY PHOTOGRAPHS Photograph 1 (left): Oak woodland along Marl’s Lane with recently coppiced hedgerow to left. Photograph 2 (centre): Informal path from Marl’s Lane leading out into adjacent field Photograph 3 (right): Mown grassy strip beneath overhead cables south of Barn Copse Appendix VI The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Photograph 4 (left): Barn Copse A – Norway maple plantation Photograph 5 (centre): mown ride north of Barn Copse with banks to either side. Photograph 6 (left): Great Germans Copse – Norway maple coppice Appendix VI The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Photograph 7 (right): Great Germans Copse – Ash plantation with grass-dominated ground flora Photograph 8 (right): mown ride north of Great Germans Copse (part) Appendix VI The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Photograph 9: Clearing in north-eastern corner of Great Germans Copse (part) Photograph 10: Spier’s Copse Area 1, typical ash woodland with lush ground flora Appendix VI The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Photograph 11 (left): informal footpath leading from between Spier’s Copse Areas 1 and to Phase Two field of assessment site Photograph 12 (centre): informal, well used footpath to south of Spier’s Copse Area 1 within Phase Two field Photograph 13 (right): mature pine plantation with frequent bramble Appendix VI The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Photograph 14 (left): Spier’s Copse Area 3, mature oak woodland to south. Photograph 15 (centre): public footpath to north of Spier’s Copse Area 4. Photograph 16 (right): lush vegetation along ride between Spier’s Copse Areas 2 and 4 with frequent thin-spiked wood-sedge and informal footpath Appendix VI The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report Photograph 17: Southern end broad ride east of Spier’s Copse Area 2 with broad uncut margin The Landmark Practice Appendix VI David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX VII BREEDING BIRDS SURVEY RESULTS The Landmark Practice Appendix VII David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX VII: BREEDING BIRDS SURVEY RESULTS 2010 surveys English Name Scientific Name 05.05.10 27.05.10 15.06.10 28.06.10 Notes Turdus merula Likely to have bred adjacent Blackbird Y Y Y Y woodland/hedgerow habitats Approx. two pairs likely to have bred in Blackcap Sylvia atricapilla Y Y Y adjacent woodland habitat (Spier’s copse) Likely to have bred in adjacent woodland and Blue tit Cyanistes caeruleus Y Y Y Y hedgerow habitats (family group observed). Buzzard Buteo buteo O/H Observed circling overhead on one occasion Approx. three pairs likely to have bred in Chaffinch Fringilla coelebs Y Y Y adjacent woodland and hedgerow habitats Approx. two pairs bred in adjacent woodland Chiffchaff Phylloscopus collybita Y Y Y Y habitat (Spier’s copse). Recorded within the northern buffer planting, eastern balancing lagoon area to SE of site Dunnock Prunella modularis Y Y Y Y and hedgerow bordering east of site. May have bred. Recorded in northern landscape buffer to Marnel Park development, presumably Goldfinch Carduelis carduelis Y Y attracted by abundant weed seeds. One bird recorded in song on 5 May 2010. One pair may have bred in Spier’s copse to the north. A bird was alarm calling along the Great spotted Dendrocopos major Y ? Y northern site boundary in May and June. A woodpecker woodpecker hole was also observed along the northern site boundary. Likely to have bred in adjacent woodland Great tit Parus major Y Y habitat Green woodpecker Picus viridis Off site Y Off site Off site Regularly recorded in vicinity. Grey heron Ardea cinerea O/H Observed flying overhead on one occasion Two birds recorded on one occasion in Grey partridge Perdix perdix Y landscape buffer to west of site. Regularly recorded to SE of site within hedgerow along northern boundary of Marnel House sparrow Passer domesticus Y Y Y Park development. Probably bred (adult observed carrying food) Appendix VII The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report English Name Scientific Name 05.05.10 27.05.10 15.06.10 28.06.10 Notes Lapwing Vanellus vanellus Y A solitary bird observed on one occasion. Linnet Carduelis cannabina Y Y Y May have bred Likely to have bred in adjacent woodland Long-tailed tit Aegithalos caudatus Y Y habitat (Spier’s copse). Family groups observed. Magpie Pica pica Off site Y Y Mallard Anas platyrhynchos Y Y One pair bred on eastern balancing pond Mistle thrush Turdus viscivorus Y Y May have bred in adjacent woodland habitat Seen on one occasion in hedgerow along Nuthatch Sitta europaea Y eastern boundary of site At least one pair likely to have bred in adjacent Robin Erithacus rubecula Y Y woodland/hedgerow habitat At least three or four pairs likely to have bred Skylark Alauda arvensis Y Y Y Y (max. 9 birds recorded in song on 27 May 2010). Song thrush Turdus philomelos Off site Off site? Y Y Probably bred in adjacent woodland. Likely to have bred in Marnel Park development – a bird seen entering eaves of Starling Sturnus vulgaris Off site Y house on 5 May 2010. Flock of 10 observed in hedgerow between eastern balancing lagoon and Marl Lane on 15 June 2010. Two birds seen on one occasion by western Stock dove Columba oenas Y balancing lagoon Regularly observed (up to 20 birds) feeding Swift Apus apus O/H O/H O\H over the site. Approx. two pairs likely to have bred within Whitethroat Sylvia communis Y Y Y Y peripheral hedgerow habitats One pair likely to have bred in adjacent Willow warbler Phylloscopus trochilus Y Y woodland habitat (Spier’s copse) Woodpigeon Columba palumbus Off site? Y Y Probably bred in adjacent woodland. Troglodytes At least one pair likely to have bred in adjacent Wren Y Y Y troglodytes woodland/hedgerow habitat Approx. two pairs likely to have bred within Yellowhammer Emberiza citrinella Y Y Y Y site. Y = recorded within/bordering the site; O/H = recorded overhead; off site = recorded offsite Appendix VII The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report 2011 surveys English Name Scientific Name 09.03.11 05.04.11 Notes Likely to have bred adjacent Turdus merula Blackbird Y Off site woodland/hedgerow habitats. Three males recorded in song in April. Four singing males recorded in adjacent Blackcap Sylvia atricapilla Y habitats Pair recorded in landscape screening to west Blue tit Cyanistes caeruleus Y of site Carrion crow Corvus corone Y Recorded feeding within the site One singing male along eastern boundary of Chaffinch Fringilla coelebs Y site Two singing males along northern and eastern Chiffchaff Phylloscopus collybita Y boundaries of site Collared dove Streptopelia decaocto Off site Two singing males along southern and eastern Dunnock Prunella modularis Y boundaries of site Goldfinch Carduelis carduelis Y Off site Four individuals along western site boundary Great spotted One individual drumming along northern Dendrocopos major Y woodpecker boundary of site Several individuals recorded around site Great tit Parus major Y Y boundaries. Two males in song in April. Three individuals observed along southern House sparrow Passer domesticus Off site Y and eastern site boundaries, two in song and one carrying nest material Jay Garrulus glandarius Off site Single birds recorded in song on eastern and Linnet Carduelis cannabina Y southern site boundaries Long-tailed tit Aegithalos caudatus Off site Magpie Pica pica Y Y Pair recorded in balancing pond to south-east Mallard Anas platyrhynchos Off site Off site of site Recorded around boundaries of site. Two Robin Erithacus rubecula Y Y males recorded in song in April. Two singing males recorded in April (three, Skylark Alauda arvensis Y Y possibly four pairs present). Sparrowhawk Accipiter nisus Y Hunting low over the site Starling Sturnus vulgaris Off site Recorded along northern boundary of existing Appendix VII The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report English Name Scientific Name 09.03.11 05.04.11 Notes development (incl. flock 15 birds) Single bird recorded in song along northern Whitethroat Sylvia communis Y boundary Three individuals recorded in song around site Willow warbler Phylloscopus trochilus Y boundaries Single bird recorded in Spier’s Copse to the Woodcock Scolopax rusticola Off site north of the site Woodpigeon Columba palumbus Y Five birds recorded within/adjacent to the site Troglodytes Single bird recorded in song along northern Wren Y troglodytes boundary of the site Six birds recorded during March along western boundary and in Phase One field. Three birds recorded along western, southern and Yellowhammer Emberiza citrinella Y Y northern boundaries in April, two of which were in song (north-easter hedgerow and southern boundary Phase Two field. Y = recorded within/bordering the site; O/H = recorded overhead; off site = recorded off site Appendix VII The Landmark Practice David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX VIII ECOLOGICAL EVALUATION TECHNIQUES The Landmark Practice Appendix VIII David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX VIII: EVALUATION TECHNIQUES 1.0 Introduction A number of systems and criteria are available to assess the nature and extent of ecological interest found at any site. Guidelines for Ecological Impact Assessment have been prepared by the Institute of Ecology and Environmental Management (2006), which have been employed below. The IEEM guidelines detail a recommended approach to the valuation of ecological receptors on the following scale: • International importance • UK importance • National importance (England/Northern Ireland/Scotland/Wales) • Regional importance • County (or Metropolitan) • District (or Unitary Authority, City or Borough) • Local or Parish; and/or • Within immediate zone of influence only 2.0 Habitats and features Internationally important habitats are considered to be those listed on Annex I of the Habitats Directive. All internationally important examples, however, should have been designated within Special Areas for Conservation (SACs). Other examples should be considered to be of value at the level for which they are designated (see below). There are published guidelines for the selection of SACs (see Brown et al, 1997) and SPAs and Ramsar Sites (Stroud et al, 1990). There are similar published criteria for the selection of nationally important Sites of Special Scientific Interest (SSSIs) (NCC, 1989) which give criteria for both habitats and species. The majority of Local Authorities have a system of 'second tier' sites which do not wholly fulfil SSSI designation criteria, but which are, nonetheless, of local to regional value. Policies, encouraged by Government advice, recognise that protection should be extended beyond the statutory sites to include the best examples of wildlife habitats, populations of rare species and geological features remaining in the District and are particularly valuable in supplementing and supporting the national framework for SSSIs. DEFRA (2006) has published Guidance on their Identification, Selection and Management of such sites. The Hedgerow Regulations (1997) provide a useful framework for the assessment of the ecological importance of hedgerows. It is possible that there may be habitats that do not fall within designated sites but are considered to meet the published selection criteria. Similarly it is possible that habitats within designated sites may not fulfil the criteria for designation in their own right. This may be due to the site having deteriorated or that they have been included The Landmark Practice Appendix VIII David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report for other reasons such as secondary or supporting value. If a habitat is considered to be in an unfavourable condition, consideration must be given to its potential value if restored. Consideration should also be given to secondary or supporting value where a habitat or feature may have no particular interest in itself but may perform an important ecological function such as a buffer against negative impacts or an important link between habitats. The presence of a diverse range of habitats can increase the value of a site. 3.0 Species A number of resources are available to assess the rarity and vulnerability of individual species. Red Data Lists utilise standard criteria defined by the International Union for the Conservation of Nature (IUCN, 2001, now the World Conservation Union, WCU) to classify the scarcity and conservation status of species of flora and fauna. The Red Data List system can operate at an International, National or Regional level (e.g. County Red Data Lists). The IUCN maintains a list of threatened species on a global scale. The IUCN threat categories are defined as follows: Extinct (EX), Extinct in the Wild (EW), Critically Endangered (CR), Endangered (EN), Vulnerable (VU), Near Threatened (NT), Least Concern (LC), Data Deficient (DD) and Not Evaluated (E). Species falling within the categories CR, EN and VU are considered to be threatened. These categories are defined by five criteria as follows: • Criterion A considers the percentage decline of a taxon, regardless of current range or abundance. • Criterion B is designed to identify threats associated with extremely restricted distribution when combined with other risk factors. • Criterion C considers the combination of extremely small population size with similar risk factors to Criterion B. • Criterion D identifies very small or restricted populations. • Criterion E requires quantitative analysis to estimate the extinction probability of a taxon based on known life history, habitat requirements, threats and any specified management options. Earlier Red Data Lists and Books (such as the British Red Data Book for Insects (Shirt 1987) and subsequent reviews: Falk, 1991 and Hyman and Parsons, 1992) classified species on the former IUCN criteria as: Extinct, Endangered (RDB1), Vulnerable (RDB2), Rare (RDB3) and insufficiently known (RDBK). Criteria for the selection of Nationally Notable insects (now termed Nationally Scarce) species generally follow Eversham (1983). These Nationally Notable/Scarce species are further divided into Notable A (present in 16-30 squares) and Notable B (31-100 squares). Rare birds in Britain are defined as any species for which records would have to be verified by the British Birds Rarities Committee. County rarities are taken to include The Landmark Practice Appendix VIII David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report all national rarities and also any species listed in County bird reports requiring a full description, which should be submitted to the relevant County Recorder. The presence of rare birds at any time of year, including locally rare species, adds significantly to the ecological value of a site. In general, however, only rare birds with a regular pattern of occurrence at a site should be included in this category. National and County distribution atlases and species reports such as county bird reports can provide valuable additional information for evaluation. They can also provide information on species status at the level of geographic coverage of the atlas. Species at the edge of their distribution (especially in the context of global change) and notably large populations of species that are uncommon or threatened in the wider context enhances a species value. A species that is rare and declining should be assigned a higher level of importance than one that is stable. Other rarity related evaluation criteria include the need to protect populations for which the UK holds a large / significant proportion of the international / European population. The presence of a diverse assemblage of species can enhance the value of a site. Further guidance on the evaluation of certain protected species has been published by English Nature e.g. Great Crested Newt Mitigation Guidelines (EN, 2001) and Bat Mitigation Guidelines (Mitchell-Jones, 2004) and non-statutory organisations e.g. Froglife (1999, endorsed by English Nature). 4.0 Other resources 4.1 Natural Areas English Nature (now Natural England) has divided England into 120 'Natural Areas' described as areas of the countryside identified by their unique combination of physical attributes, wildlife, land-use and culture (English Nature, 1998). Natural Areas provide a useful framework for assessing species and habitats beyond the traditional administrative boundaries. In the UK Biodiversity Action Plan they are described as: "… biogeographical zones which reflect the geological foundation, the natural systems and processes and the wildlife in different parts of England, and provide a framework for setting objectives for nature conservation" The Natural Area profiles provide contextual information to confirm temporal and spatial scope. They can provide information to aid evaluation of the relative importance of ecological receptors. 4.2 Biodiversity Action Plans The UK Biodiversity Action Plan (BAP) published in 1994 (UK Biodiversity Steering Group, 1995-1999) highlighted 38 key habitat types, now termed priority habitats, which were subsequently revised to include 26 non-maritime and 19 maritime priority habitats. A review was undertaken in 2007 resulting in the publication of a new list (www.ukbap.org.uk/NewPriorityList.aspx) comprising 1,149 priority species and 65 priority habitats (40 terrestrial and 25 maritime). Priority habitats are defined as those for which the UK has international obligations, are suffering high rates of loss or are The Landmark Practice Appendix VIII David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report important for priority species. Priority species within the BAP system are either internationally threatened or have suffered a marked decline in the UK. Species were also considered for inclusion where quantitative data on decline were inadequate but there was convincing evidence of extreme threat. The majority of habitats and species under the National BAP at the time are included on the list prepared under Section 74 of the Countryside and Rights of Way (CRoW) Act (2000). The Biodiversity Strategy for England (DEFRA, 2002) sets out the means by which the government will comply with its duty under S74 of the CRoW Act (now superseded by S41 of the NERC Act) or promote the taking by others, steps to further the conservation of listed habitats and species. Biodiversity Action plans at lower levels such as regional and county have also been produced for many areas. Selection of habitats and species for BAPs is on the grounds that they are in a sub- optimal state and does not imply any specific level of importance of a habitat or species. The value of priority habitats and species should be determined as described above. Only where a specific habitat or species action plan states that all areas of a particular habitat or all populations of a given species should be protected should the habitat or species be valued at the appropriate level of the BAP. BAPs can assist in ecological evaluation but must be reviewed on a case by case basis. 4.3 Bird Species of Conservation Concern Bird Species of Conservation Concern in the UK, Channel Islands and Isle of Man was first published in 1996, updated in 2002 (Gregory et al, 2002) and again in 2009 (Eaton et al 2009). The list is prioritised into species of high (red) and medium (amber) conservation concern; all other species are of lower (green) concern. Red- listed species are globally threatened according to IUCN (World Conservation Union) criteria or in rapid decline (greater than 50% over the past 25 years) in the UK, currently or historically and those that have declined historically and not shown a substantial recent recovery. Amber listed species are in moderate decline (25-49% over the past 25 years), rare breeders, localised or internationally important populations, of an unfavourable conservation status in Europe or those whose population has declined historically but made a substantial recent recovery. It should be noted that despite substantial declines, many red-listed species such as skylark (Alauda arvensis) and song thrush (Turdus merula) remain relatively common in the UK countryside. As for BAPs, inclusion of species on one of the lists is not sufficient in itself for assigning a level of value to the species concerned. Each species should be evaluated according to the guidelines above with reference to the criteria for inclusion of the species. The Landmark Practice Appendix VIII David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report REFERENCES Brown, A.E., Burn, A.J., Hopkins, J.J. and Way, S.F. (1997) The Habitats Directive: selection of Special Areas of Conservation in the UK. Report 270. JNCC, Peterborough. Cheffings, C.M. and Farrell, L. (Eds), Dines, T.D., Jones, R.A., Leach, S.J., McKean, D.R., Pearman, D.A., Preston, C.D., Rumsey, F.J., Taylor, I (2005), The Vascular Plant Red Data List for Great Britain, Species Status 7: 1-116, JNCC, Peterborough. DEFRA (2002), Working with the grain of nature: A Biodiversity Strategy for England. DEFRA, London. DEFRA (2006), Local Sites: Guidance on their Identification, Selection and Management. Eaton, MA, Brown AF, Noble DG, Musgrove AJ, Hearn R, Aebischer NJ, Gibbons DW, Evans A and Gregory RD (2009) Birds of Conservation Concern 3: the population status of birds in the United Kingdom, Channel Islands and the Isle of Man. British Birds 102 pp296-341. Edwards, R. (1997), Provisional Atlas of the aculeate Hymenoptera of Britain and Ireland Part 1: Bees, Wasps & Ants. Recording Society, Huntingdon, BRC EEC (1992), Council Directive 92/43/EEC(c) on the Conservation of Natural Habitats and of Wild Fauna & Flora (The Habitats Directive) EEC (1979), European Community Directive 79/409/EEC on the Conservation of Wild Birds (The Birds Directive) EC (1979), Bern Convention on the Conservation of European Wildlife and Natural Habitats, 1979 English Nature (1998), Natural Areas: nature conservation in context English Nature (2001), Great Crested Newt Mitigation Guidelines, English Nature. Eversham, B (1983), Defining Rare and Notable species – a discussion document. Invertebrate Site Register Report No. 49. Peterborough: NCC. Falk, S.J. (1991), A review of the scarce and threatened bees, wasps and ants of Great Britain. Peterborough, Nature Conservancy Council. Foster, G.N. (2000), A review of the scarce and threatened Coleoptera of Great Britain: Part 3 Aquatic Coleoptera, Peterborough, Joint Nature Conservation Committee Froglife (1999), Reptile Survey: an introduction to planning, conducting and interpreting surveys for snake and lizard conservation. Froglife Advice Sheet 10. Froglife, Halesworth. Gregory, R.D., Wilkinson, N.I., Robinson, J.A., Brown, A.F., Hughes, J., Procter, D.A., Gibbons, D.W. and Galbraith, C.A. (2002), The population status of birds in the United Kingdom, Channel Islands and Isle of Man: an analysis of conservation concern 2002-2007. British Birds 95: pp 410-450 The Landmark Practice Appendix VIII David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report HMSO (1981, 1998), Wildlife & Countryside Act 1981, and amendments, incl. Third Quinquennial Review of Schedules 5 & 8 to the Wildlife & Countryside Act, 1998 HMSO (2010), The Conservation (Natural Habitats, &c.) Regulations 2010 HMSO (2000), Countryside and Rights of Way Act HMSO (2006), Natural Environment and Rural Communities Act 2006 Hyman, P.S. & Parsons M.S. (1992). A review of the scarce and threatened Coleoptera of Great Britain: Part 1 Peterborough, Joint Nature Conservation Committee. IEEM (2006), Guidelines for Ecological Impact Assessment in the UK, IEEM IUCN (2001), IUCN Red List Categories and Criteria: Version 3.1, IUCN Species Survival Commission (www.iucn.org/webfiles/doc/SSC/RedList/redlistcatsenglish.pdf) IUCN (2003), Guidelines for using the IUCN Red List Categories and Criteria, IUCN Species Survival Commission Mitchell-Jones, A.J. (2004), Bat Mitigation Guidelines, English Nature Nature Conservancy Council (1989), Guidelines for the selection of biological SSSIs, Nature Conservancy Council and supplements published by JNCC. Preston, C.D., Pearman, D.A. and Dines, T.D. (2002), New Atlas of the British and Irish Flora OUP Shirt, D B (1987), British Red Data Books 2: Insects, NCC Stroud, D.A., Mudge, G.P., Pienowski, M.W (1990), Protecting internationally important bird sites, NCC Peterborough UK Biodiversity Steering Group (1995), Biodiversity: the UK Steering Group Report: Meeting the Rio Challenge, Volumes 1 and 2, HMSO UK Biodiversity Group (1998-1999), Tranche 2 Action Plans, Volumes I-VI. UKBG/English Nature UNESCO (1987), Convention on Wetlands of International Importance especially as Waterfowl Habitat as amended by the Conference of Parties 28.05.87 The Landmark Practice Appendix VIII David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX IX LEGAL FRAMEWORK The Landmark Practice Appendix IX David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX IX: LEGAL FRAMEWORK 1.0 Protected Sites (European) 1.1 Special Areas of Conservation (SACs) SACs are designated under The Conservation (Natural Habitats &c.) Regulations 2010 (‘The Habitats Regulations’) which implements The European Community Directive on the Conservation of Natural Habitats and of Wild Fauna and Flora 92/43/EEC (the ‘Habitats Directive’, EEC, 1992). Lists of candidate SACs (cSACs) have been submitted to the European Commission for approval. Both possible SACs (pSACs) and cSACs are treated by the planning system as if fully designated. The Habitats Directive also refers to the need for nature conservation outside protected areas (Article 10) and measures to implement this article are incorporated in British legislation through the Habitats Regulations (HMSO, 1994) and ODPM Circular 06/2005 that accompanies PPS9. Article 10 of The EU Habitats Directive 1992 states that: 'Member States shall endeavour, where they consider it necessary, in their land use planning and development policies and, in particular, with a view to improving the ecological coherence of the Natura 2000 network, to encourage the management of features of the landscape which are of major importance for wild flora and fauna.” Article 10 of The EU Habitats Directive 1992 (and Regulation 39(3) of the Conservation (Natural Habitats, & c. Regulations) 2010 goes on to state: “Such features are those which, by virtue of their linear and continuous structure (such as rivers with their banks or the traditional systems of marking field boundaries) or their function as stepping stones (such as ponds or small woods), are essential for the migration, dispersal and genetic exchange of wild species.' 39(3) 1.2 Special Protection Areas (SPAs) SPAs are classified in accordance with the European Community Directive on the Conservation of Wild Birds (79/409/EEC) (the ‘Birds Directive’, EEC, 1979). Under this Directive, the UK Government must also take special measures to conserve the habitat of species listed in Annex I of the Directive and all migratory species. The provisions of the Birds Directive are implemented in England through the Wildlife and Countryside Act 1981 (as amended) and the Habitats Regulations (2010). 1.3 Ramsar sites The Ramsar Convention (UNESCO, 1987) requires signatory states to protect wetlands that are of international importance, particularly as waterfowl habitats. The Landmark Practice Appendix IX David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report 2.0 Protected Sites (National) 2.1 Sites of Special Scientific Interest (SSSIs) The Wildlife and Countryside Act 1981 (as amended 1991 and varied 1998) (HMSO, 1981, 1991, 1998) requires Natural England, the Government body with authority for nature conservation in England, to designate areas which make a significant contribution to a national network of sites of nature conservation value as SSSIs. The Countryside and Rights of Way Act 2000 (HMSO, 2000) came into force in full on 30 January 2001. The Act is in five parts. Part III relates to Nature Conservation and amends existing legislation (i.e. the Wildlife and Countryside Act 1981) through improved protection and management of SSSIs, improved legal protection for threatened species and the provision of a statutory basis for biodiversity conservation. 2.2 Local Nature Reserves Local Nature Reserves are designated under Section 21 of The National Parks and Access to the Countryside Act 1949 (HMSO, 1949) by principal local authorities. The declaring local authority must have a legal interest in the land concerned. Local Nature reserves are designated for people and wildlife. They are places with wildlife or geological features of special interest locally and that give people special opportunities to study and learn about them or simply enjoy them and have contact with nature. 3.0 Non-statutory sites The majority of Local Authorities have a system of 'second tier' sites which do not wholly fulfil SSSI designation criteria, but which are, nonetheless, of local or regional value. The policies, encouraged by Government advice, recognise that protection should be extended beyond the statutory sites to include the best examples of wildlife habitats, populations of rare species and geological features remaining in the area and are particularly valuable in supplementing and supporting the national framework for SSSIs. 4.0 Protected features 4.1 Hedgerow Regulations The Hedgerow Regulations 1997 (HMSO, 1997) were introduced to protect ‘important’ hedgerows in the countryside by controlling their removal through a system of notification. The Regulations apply to lengths of hedgerow greater than 20m in length, not adjoining residential curtilages. ‘Important’ hedgerows are defined within the Regulations on a variety of historical and/or ecological criteria. The Landmark Practice Appendix IX David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report 4.2 Tree Preservation Orders (TPOs) TPOs are made under Part VIII of the Town and Country Planning Act 1990 as amended by s23 of the Planning and Compensation Act 1991 and under the Town and Country Planning (Trees) Regulations 1999. They are made by local planning authorities to protect selected trees and woodlands if their removal would have a significant impact on the local environment and its enjoyment by the public. The criteria do not incorporate any specific considerations of ecological value. TPOs, however, provide legal protection to trees prohibiting the cutting down, uprooting, topping, lopping, wilful damage or wilful destruction. 5.0 Protected species (European) 5.1 Plants Certain plant species are listed under Annex IVb of the Habitats Directive under which it is an offence to deliberately pick, collect, cut, uproot or destroy such a plant. Under the Bern Convention 1979, Contracting Parties are required to take appropriate and necessary legislative and administrative measures to ensure the special protection of the wild flora species specified in Appendix 1. In the UK this is implemented through various national wildlife protection policies. 5.2 Bats All British bats and their roosts are fully protected under international wildlife law against adverse effects including disturbance. Under the terms of the Bonn Convention, which encompasses the Agreement of the Conservation of Bats in Europe, there is a fundamental obligation to protect from damage or disturbance, sites which are important for the conservation status of bats. Such sites include those bats use for shelter or protection and important foraging areas. 5.3 Dormouse (Muscardinus avellanarius) The dormouse is protected under Schedule 2 of the Habitats Regulations 2010 and Schedule 5 of the Wildlife and Countryside Act 1981 (as amended). Taken together, the Regulations and Act make it illegal to intentionally or deliberately kill, injure or capture dormice; deliberately disturb dormice and damage or destroy dormouse breeding sites or resting places. 5.4 Otter (Lutra lutra) The otter is protected under Schedule 2 of the Habitats Regulations 2010 and Schedule 5 of the Wildlife and Countryside Act 1981 (as amended). Taken together, the Regulations and Act make it illegal to intentionally or deliberately kill, injure or capture otters; deliberately disturb otters and damage or destroy otter breeding sites or resting places. The Landmark Practice Appendix IX David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report 5.5 Birds In Britain all wild birds are granted legal protection under the EC Birds Directive and the Wildlife & Countryside Act 1981 (as amended). This legislation protects the birds, their eggs and nests whilst being built or in use. Legal protection makes it an offence to intentionally kill, injure, take or have in possession any wild bird or egg. It is also an offence to intentionally damage or destroy the nest of any wild bird whilst it is being built or in use. Under the Bern Convention 1979, Contracting Parties are required to take appropriate and necessary legislative and administrative measures to ensure the special protection of the wild fauna species specified in Appendix II. In the UK this is implemented through various national wildlife protection policies. 5.6 Great crested newt The great crested newt (Triturus cristatus) is fully protected under Schedule 5 of the Wildlife & Countryside Act 1981 (as amended) and the Conservation (Natural Habitats &c.) Regulations 1994 (and subsequent amendments). The legislation protects the newts and their places of shelter or protection, which may extend 500m from the breeding pond. 5.7 Inverts Under the Habitats Regulations (2010) invertebrate species listed on Schedule 2 it is an offence to deliberately capture or kill, disturb, take or destroy eggs of such a species or to damage or destroy the breeding site or resting place of such an animal. 6.0 Protected species (National) 6.1 Plants Statutory protection in Great Britain is provided by the Wildlife and Countryside Act 1981. The plants and fungi which have special protection are listed on Schedule 8 under which it is an offence to intentionally pick, uproot or destroy any plant on Schedule 8. Five plant species are listed on the Weeds Act 1959 as injurious: common ragwort (Senecio jacobaea), broad-leaved dock (Rumex obtusifolius), curled dock (Rumex crispus), creeping thistle (Cirsium arvense) and spear thistle (Cirsium vulgare). The Act requires landowners to eliminate scheduled weeds to prevent their seeds contaminating neighbouring land. The Ragwort Control Act 2003 amends the Weed Act with respect to common ragwort. Thirty-eight species plus all species of Elodea (of which there are currently three species known to have been introduced) are listed on Schedule 9 of the Wildlife and Countryside Act 1981 under which it is an offence to plant or otherwise cause to grow The Landmark Practice Appendix IX David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report in the wild the scheduled species. Two are marine, thirteen (plus all species of Elodea) aquatic and the remainder terrestrial. 6.2 Wild Mammals Under the Wild Mammals (Protection) Act 1996 it is an offence to mutilate, kick, beat, nail or otherwise impale, stab, burn, stone, crush, drown, drag or asphyxiate any wild mammal with intent to inflict unnecessary suffering. 6.3 Badgers Badgers are protected under the Protection of Badgers Act 1992. This Act makes it illegal to wilfully kill, injure or take any badger, or attempt to do so and it is an offence to intentionally or recklessly damage, destroy or obstruct access to any part of a badger sett. 6.4 Water Voles The water vole (Arvicola terrestris) receives protection under Schedule 5 of the Wildlife and Countryside Act 1981 (as amended). Under the Act it is an offence to intentionally kill, injure or take water voles and intentionally or recklessly damage, destroy or obstruct access to any structure or place used for shelter or protection or obstruct access to any structure or place used by water voles for shelter or protection or to disturb water voles while they are using such a place. 6.5 Birds In Britain all wild birds are granted legal protection under the Wildlife & Countryside Act 1981 (as amended) and the EC Birds Directive. This legislation protects the birds, their eggs and nests whilst being built or in use. Legal protection makes it an offence to intentionally kill, injure, take or have in possession any wild bird or egg. It is also an offence to intentionally damage or destroy the nest of any wild bird whilst it is being built or in use. Birds listed on Schedule 1 of the Wildlife and Countryside Act 1981 (as amended) are subject to special penalties and are also protected from disturbance while nesting including the disturbance of dependent young. 6.6 Reptiles The slow-worm (Anguis fragilis), grass snake (Natrix natrix), adder (Vipera berus) and common lizard (Lacerta vivipara) are protected under Schedule 5 of the Wildlife & Countryside Act 1981 (as amended) in respect of section 9(1) and 9(5) only. Under section 9(1) it is an offence to knowingly kill or injure a reptile. Section 9(5) refers to sale and trade. 6.7 Invertebrates Statutory protection in Great Britain is provided by the Wildlife and Countryside Act 1981. The invertebrates which have special protection are listed on Schedule 5 under which it is an offence to intentionally kill, injure or take these invertebrates and The Landmark Practice Appendix IX David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report intentionally or recklessly damage or destroy, or obstruct access to, any structure or place used for shelter or protection or disturb any such animal while occupying such a structure or place. 7.0 Biodiversity conservation In 2002, the Department of Farming and Rural Affairs (DEFRA) published a list of principally important species and habitats for the purposes of conserving biological diversity in England under Section 74 of the Countryside and Rights of Way Act 2000 in accordance with the 1992 UN Convention on Biological Diversity. This has subsequently been carried forward under Section 41 of the Natural Environment and Rural Communities (NERC) Act 2006. The Biodiversity Strategy for England sets out the means by which the Government will comply with its duty under Section 74 (now Section 41 of the NERC Act) to take or promote the taking by others of steps to further the conservation of listed habitats and species, including through the continued implementation of Action Plans. The Landmark Practice Appendix IX David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report REFERENCES DEFRA (2002), Working with the grain of nature: a biodiversity strategy for England, DEFRA. European Community Directive 79/409/EEC on the Conservation of Wild Birds (The Birds Directive) European Community Directive 92/43/EEC on the Conservation of Natural Habitats and of Wild Fauna and Flora HMSO (1981, 1998), Wildlife & Countryside Act 1981, and amendments, incl. Third Quinquennial Review of Schedules 5 & 8 to the Wildlife & Countryside Act, 1998 HMSO (1949), National Parks and Access to the Countryside Act HMSO (1959), Weeds Act HMSO (1992), The Protection of Badgers Act 1992. HMSO (2010), The Conservation (Natural Habitats, &c) Regulations 2010, HMSO HMSO (1996), Wild Mammals (Protection) Act HMSO (1997), Hedgerow Regulations HMSO (2000), Countryside and Rights of Way Act HMSO (2003), Ragwort Control Act HMSO (2006), Natural Environment and Rural Communities Act 2006 ODPM (2005), Planning Policy Statement 9: Biodiversity and Geological Conservation, The Stationery Office. ODPM (2005), Government Circular: Biodiversity and Geological Conservation – Statutory Obligations and their Impact within the Planning System, The Stationery Office UNESCO (1987), Convention on Wetlands of International Importance especially as Waterfowl Habitat as amended by the Conference of Parties 28.05.87 The Landmark Practice Appendix IX David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX X GREAT CRESTED NEWT HABITAT ASSESSMENT TARGET NOTES The Landmark Practice Appendix X David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report APPENDIX X: GREAT CRESTED NEWT HABITAT ASSESSMENT TARGET NOTES 1) 40 m wide advance landscape planting: Forms the western boundary of the proposed development area, planted with native trees and shrubs at the same time that the landscaping at Marnel Park was carried out (c. 2005). The planted trees have established well for the most part. Ground surface mulched when planted with bark chippings, self sown ruderal vegetation established over much of the ground layer though sparse in places. 2) 5 m wide field margins: Nearly all ryegrass, very little in the way of other plants or flowers. No hedgerows along access track to Kiln Farm. 3) Ditch margins: Wide margins along each side of ditchline. Mixed flora, ruderal vegetation along most of the run mixed with brambles, vetches and other floral resources. Small numbers of cowslips close to the balancing pond. Forms damp corridor through areas of arable fields 4) 40 m wide advance landscape planting: Planted with native trees and shrubs at the same time that the landscaping at Marnel Park was carried out (c. 2005). The planted trees have established well for the most part. Ground surface mulched when planted with bark chippings, self sown ruderal vegetation established over much of the ground layer though sparse in places. Access track between planting and hedgerow forming the northern boundary of the existing Marnel Park properties planted up with a wildflower mix, this is now well established with lots of flowers and seems to support a good range of invertebrate species. 5) 5 m wide field margins. A 5 m wide field margin to the north of the post and rail fence marking the edge of the planting area from Target Note 5. Mostly grass, but with a mix of ruderal plants moving in from the planted area to the south. Great crested newts recorded from this strip during the reptile surveys together with grass snakes and common lizard. 6) 5 m field margins Ryegrass field margins around the arable fields. The Landmark Practice Appendix X David Wilson Homes Land North of Marnel Park, Basingstoke Ecological Surveys report ACKNOWLEDGEMENTS The bat and dormouse surveys were undertaken by ECOSA and the great crested newt and reptile surveys by Matt Smith, independent consultant ecologist on behalf of The Landmark Practice. All other surveys were undertaken by The Landmark Practice. The Landmark Practice Acknowledgements