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Species plan name Group member name Species group

Andrena ferox Bees/Ants/Wasps

Bombus distinguendus Bees/Ants/Wasps

Bombus humilis Bees/Ants/Wasps

Bombus ruderatus Bees/Ants/Wasps

Bombus subterraneus Bees/Ants/Wasps

Bombus sylvarum Bees/Ants/Wasps

Cerceris quadricincta Bees/Ants/Wasps

Cerceris quinquefasciata Bees/Ants/Wasps

Chrysis fulgida Bees/Ants/Wasps

Colletes floralis Bees/Ants/Wasps

Formica exsecta Bees/Ants/Wasps



Formica rufibarbis Bees/Ants/Wasps

Homonotus sanguinolentus Bees/Ants/Wasps

Nomada armata Bees/Ants/Wasps

Osmia inermis Bees/Ants/Wasps

Osmia parietina Bees/Ants/Wasps

Osmia uncinata Bees/Ants/Wasps

Osmia xanthomelana Bees/Ants/Wasps

Pseudepipona herrichii Bees/Ants/Wasps

Anisodactylus poeciloides Beetles

Anostirus castaneus Beetles



Bembidion argenteolum Beetles

Bidessus minutissimus Beetles

Bidessus minutissimus Beetles

Byctiscus populi Beetles



Carabus intricatus Beetles

Cicindela germanica Beetles

Cicindela hybrida Beetles

Cicindela sylvatica Beetles

Cicindela sylvatica Beetles

Cryptocephalus coryli Beetles



Cryptocephalus nitidulus Beetles

Cryptocephalus nitidulus Beetles

Cryptocephalus primarius Beetles



Cryptocephalus sexpunctatus Beetles



Ernoporus tiliae Beetles

Ernoporus tiliae Beetles

Gastrallus immarginatus Beetles

Gnorimus nobilis Beetles

Gnorimus nobilis Beetles

Grouped plan for river shingle beetles Bembidion testaceum Beetles

Grouped plan for river shingle beetles Bembidion testaceum Beetles

Grouped plan for river shingle beetles Hydrochus nitidicollis Beetles

Grouped plan for river shingle beetles Hydrochus nitidicollis Beetles

Grouped plan for river shingle beetles Lionychus quadrillum Beetles

Grouped plan for river shingle beetles Meotica anglica Beetles

Grouped plan for river shingle beetles Perileptus areolatus Beetles

Grouped plan for river shingle beetles Perileptus areolatus Beetles

Grouped plan for river shingle beetles Thinobius newberyi Beetles

Limoniscus violaceus Beetles

Lucanus cervus Beetles

Malachius aeneus Beetles

Malachius aeneus Beetles

Melanapion minimum Beetles



Melanotus punctolineatus Beetles

Melanotus punctolineatus Beetles

Oberea oculata Beetles

Oberea oculata Beetles

Procas granulicollis Beetles

Rhynchaenus testaceus Beetles



Synaptus filiformis Beetles



Acrocephalus palustris Birds

Alauda arvensis Birds

Alauda arvensis Birds

Botaurus stellaris Birds




Burhinus oedicnemus Birds




Caprimulgus europaeus Birds



Carduelis cannabina Birds

Carduelis cannabina Birds

Crex crex Birds

Crex crex Birds

Crex crex Birds

Emberiza cirlus Birds



Emberiza schoeniclus Birds

Emberiza schoeniclus Birds

Jynx torquilla Birds

Lanius collurio Birds

Loxia scotica Birds

Loxia scotica Birds

Lullula arborea Birds



Melanitta nigra Birds






Miliaria calandra Birds




Muscicapa striata Birds

Muscicapa striata Birds

Passer montanus Birds

Passer montanus Birds

Perdix perdix Birds

Perdix perdix Birds

Phalaropus lobatus Birds



Pyrrhula pyrrhula Birds

Pyrrhula pyrrhula Birds

Sterna dougallii Birds

Sterna dougallii Birds

Streptopelia turtur Birds




Tetrao tetrix Birds

Tetrao tetrix Birds

Tetrao urogallus Birds

Tetrao urogallus Birds

Turdus philomelos Birds

Turdus philomelos Birds

Acaulon triquetrum Bryophyte

Acaulon triquetrum Bryophyte

Acrobolbus wilsonii Bryophyte

Adelanthus lindenbergii Bryophyte

Andreaea frigida Bryophyte

Bartramia stricta Bryophyte



Bryoerythrophyllum caledonicum Bryophyte

Bryum warneum Bryophyte

Bryum warneum Bryophyte

Buxbaumia viridis Bryophyte

Cephaloziella nicholsonii Bryophyte

Cephaloziella nicholsonii Bryophyte

Cryphaea lamyana Bryophyte

Cryphaea lamyana Bryophyte

Didymodon glaucus Bryophyte

Didymodon glaucus Bryophyte

Didymodon tomaculosus Bryophyte

Ditrichum cornubicum Bryophyte

Ditrichum cornubicum Bryophyte

Ditrichum plumbicola Bryophyte

Herbertus borealis Bryophyte

Jamesoniella undulifolia Bryophyte

Leiocolea rutheana Bryophyte

Leiocolea rutheana Bryophyte

Lejeunea mandonii Bryophyte

Leptodontium gemmascens Bryophyte

Leptodontium gemmascens Bryophyte

Marsupella profunda Bryophyte

Marsupella profunda Bryophyte

Orthodontium gracile Bryophyte

Orthodontium gracile Bryophyte

Orthotrichum obtusifolium Bryophyte

Orthotrichum obtusifolium Bryophyte

Orthotrichum pallens Bryophyte

Pallavicinia lyellii Bryophyte

Pallavicinia lyellii Bryophyte

Petalophyllum ralfsii Bryophyte

Petalophyllum ralfsii Bryophyte

Pohlia scotica Bryophyte

Rhynchostegium rotundifolium Bryophyte

Rhynchostegium rotundifolium Bryophyte

Riccia huebeneriana Bryophyte

Seligeria carniolica Bryophyte

Seligeria carniolica Bryophyte

Sematophyllum demissum Bryophyte

Sematophyllum demissum Bryophyte

Sphagnum balticum Bryophyte

Thamnobryum angustifolium Bryophyte

Thamnobryum cataractarum Bryophyte

Tortula cernua Bryophyte

Tortula cernua Bryophyte

Tortula freibergii Bryophyte

Weissia multicapsularis Bryophyte

Weissia multicapsularis Bryophyte

Weissia rostellata Bryophyte

Zygodon forsteri Bryophyte

Zygodon gracilis Bryophyte

Zygodon gracilis Bryophyte

Lophopus crystallinus Bryozoan



Argynnis adippe Butterflies



Boloria euphrosyne Butterflies



Carterocephalus palaemon Butterflies

Carterocephalus palaemon Butterflies

Euphydryas aurinia Butterflies

Euphydryas aurinia Butterflies

Hesperia comma Butterflies

Maculinea arion Butterflies

Maculinea arion Butterflies

Mellicta athalia Butterflies





Plebejus argus Butterflies

Plebejus argus Butterflies

Polyommatus bellargus Butterflies

Decticus verrucivorus Crickets/Grasshoppers

Decticus verrucivorus Crickets/Grasshoppers

Gryllotalpa gryllotalpa Crickets/Grasshoppers

Gryllus campestris Crickets/Grasshoppers

Stethophyma grossum Crickets/Grasshoppers

Stethophyma grossum Crickets/Grasshoppers

Austropotamobius pallipes Crustacean



Coenagrion mercuriale Damselfly/Dragonfly



Alosa alosa Fish

Alosa alosa Fish

Alosa alosa Fish

Alosa alosa Fish

Alosa fallax Fish

Alosa fallax Fish

Alosa fallax Fish

Coregonus albula Fish



Asilus crabroniformis Flies

Asilus crabroniformis Flies

Blera fallax Flies

Blera fallax Flies

Blera fallax Flies

Bombylius discolor Flies

Brachyptera putata Flies

Cliorismia rustica Flies

Doros profuges Flies

Eristalis cryptarum Flies

Hammerschmidtia ferruginea Flies



Lipsothrix ecucullata Flies

Lipsothrix nervosa Flies

Lipsothrix nervosa Flies

Lipsothrix nigristigma Flies

Lipsothrix nigristigma Flies

Odontomyia hydroleon Flies

Odontomyia hydroleon Flies

Spiriverpa lunulata Flies

Alisma gramineum Flowering plant

Alisma gramineum Flowering plant

Apium repens Flowering plant

Apium repens Flowering plant

Arabis glabra Flowering plant



Asparagus officinalis ssp prostratus Flowering plant

Asparagus officinalis ssp prostratus Flowering plant

Bromus interruptus Flowering plant

Carex vulpina Flowering plant

Carex vulpina Flowering plant

Centaurea cyanus Flowering plant

Centaurea cyanus Flowering plant

Cochlearia micacea Flowering plant

Cochlearia micacea Flowering plant

Coincya wrightii Flowering plant




Cotoneaster integerrimus Flowering plant

Cotoneaster integerrimus Flowering plant

Crepis foetida Flowering plant

Damasonium alisma Flowering plant

Damasonium alisma Flowering plant

Dianthus armeria Flowering plant



Epipactis youngiana Flowering plant

Filago lutescens Flowering plant



Filago pyramidata Flowering plant

Filago pyramidata Flowering plant

Fumaria purpurea Flowering plant

Fumaria purpurea Flowering plant

Galeopsis angustifolia Flowering plant

Galeopsis angustifolia Flowering plant

Galium tricornutum Flowering plant

Galium tricornutum Flowering plant

Gentianella anglica Flowering plant



Gentianella uliginosa Flowering plant

Gentianella uliginosa Flowering plant

Hieracium Sect Alpestria Flowering plant

Juniperus communis Flowering plant




Linnaea borealis Flowering plant



Liparis loeselii Flowering plant



Luronium natans Flowering plant

Luronium natans Flowering plant

Lycopodiella inundata Flowering plant



Melampyrum sylvaticum Flowering plant



Mentha pulegium Flowering plant

Mentha pulegium Flowering plant

Najas flexilis Flowering plant

Najas flexilis Flowering plant

Najas marina Flowering plant

Najas marina Flowering plant

Pilularia globulifera Flowering plant



Potamogeton compressus Flowering plant



Potamogeton rutilus Flowering plant

Potamogeton rutilus Flowering plant

Ranunculus tripartitus Flowering plant




Rumex rupestris Flowering plant

Salix lanata Flowering plant



Scandix pecten-veneris Flowering plant

Scandix pecten-veneris Flowering plant

Silene gallica Flowering plant

Silene gallica Flowering plant

Sium latifolium Flowering plant

Sium latifolium Flowering plant

Spiranthes romanzoffiana Flowering plant

Thlaspi perfoliatum Flowering plant

Thlaspi perfoliatum Flowering plant

Torilis arvensis Flowering plant

Torilis arvensis Flowering plant

Valerianella rimosa Flowering plant

Valerianella rimosa Flowering plant

Woodsia ilvensis Flowering plant

Woodsia ilvensis Flowering plant

Armillaria ectypa Fungi

Armillaria ectypa Fungi

Batterraea phalloides Fungi

Boletus regius Fungi

Boletus satanas Fungi

Grouped plan for tooth fungi Bankera fuligineoalba Fungi

Grouped plan for tooth fungi Hydnellum aurantiacum Fungi

Grouped plan for tooth fungi Hydnellum caeruleum Fungi

Grouped plan for tooth fungi Hydnellum concrescens Fungi

Grouped plan for tooth fungi Hydnellum ferrugineum Fungi

Grouped plan for tooth fungi Hydnellum peckii Fungi

Grouped plan for tooth fungi Hydnellum scrobiculatum Fungi

Grouped plan for tooth fungi Hydnellum spongiosipes Fungi

Grouped plan for tooth fungi Phellodon confluens Fungi

Grouped plan for tooth fungi Phellodon melaleucus Fungi

Grouped plan for tooth fungi Phellodon tomentosus Fungi

Grouped plan for tooth fungi Sarcodon glaucopus Fungi

Grouped plan for tooth fungi Sarcodon squamosus Fungi

Grouped plan for tooth fungi Sarcodon scabrosus Fungi

Hericium erinaceum Fungi

Hygrocybe calyptriformis Fungi

Hygrocybe spadicea Fungi

Hypocreopsis rhododendri Fungi

Microglossum olivaceum Fungi

Piptoporus quercinus Fungi

Poronia punctata Fungi

Tulostoma niveum Fungi

Bufo calamita Herpetiles



Lacerta agilis Herpetiles



Rana lessonae Herpetiles



Triturus cristatus Herpetiles




Alectoria ochroleuca Lichen

Bacidia incompta Lichen

Belonia calcicola Lichen

Biatoridium monasteriense Lichen

Bryoria smithii Lichen

Buellia asterella Lichen

Calicium corynellum Lichen

Caloplaca aractina Lichen

Chaenotheca phaeocephala Lichen

Chaenotheca phaeocephala Lichen

Cladonia botrytes Lichen

Cladonia mediterranea Lichen

Cladonia mediterranea Lichen

Cladonia peziziformis Lichen

Enterographa elaborata Lichen

Enterographa sorediata Lichen

Graphina pauciloculata Lichen

Heterodermia leucomelos Lichen

Heterodermia leucomelos Lichen

Lecanographa grumulosa Lichen

Peltigera lepidophora Lichen

Squamarina lentigera Lichen

Squamarina lentigera Lichen

Teloschistes chrysophthalmus Lichen

Thelenella modesta Lichen

Thelenella modesta Lichen

Arvicola terrestris Mammal

Arvicola terrestris Mammal

Barbastella barbastellus Mammal

Lepus europaeus Mammal

Lepus europaeus Mammal

Lutra lutra Mammal

Lutra lutra Mammal

Muscardinus avellanarius Mammal



Myotis bechsteinii Mammal

Pipistrellus pipistrellus Pipistrellus pipistrellus Mammal

Pipistrellus pipistrellus Pipistrellus pygmaeus Mammal

Pipistrellus pipistrellus Pipistrellus pipistrellus Mammal

Pipistrellus pipistrellus Pipistrellus pygmaeus Mammal

Rhinolophus ferrumequinum Mammal



Rhinolophus hipposideros Mammal

Rhinolophus hipposideros Mammal

Sciurus vulgaris Mammal

Amphianthus dohrnii Marine

Ascophyllum nodosum mackii Marine

Atrina fragilis Marine

Atrina fragilis Marine

Eunicella verrucosa Marine

Grouped plan for deep-water fish Marine

Anisus vorticulus Molluscs

Catinella arenaria Molluscs

Margaritifera margaritifera Molluscs




Myxas glutinosa Molluscs

Pisidium tenuilineatum Molluscs

Pseudanodonta complanata Molluscs

Segmentina nitida Molluscs

Segmentina nitida Molluscs

Vertigo angustior Molluscs

Vertigo genesii Molluscs

Vertigo geyeri Molluscs

Vertigo moulinsiana Molluscs

Acosmetia caliginosa Moths

Acosmetia caliginosa Moths

Aspitates gilvaria Moths

Aspitates gilvaria Moths

Athetis pallustris Moths

Athetis pallustris Moths

Catocala promissa Moths

Catocala sponsa Moths

Coleophora tricolor Moths

Coleophora tricolor Moths

Coscinia cribraria bivittata Moths

Coscinia cribraria bivittata Moths

Cosmia diffinis Moths

Cosmia diffinis Moths

Cyclophora pendularia Moths

Cyclophora pendularia Moths

Dicycla oo Moths

Epione vespertaria Moths



Eustroma reticulatum Moths



Heliophobus reticulata marginosa Moths

Hemaris tityus Moths

Hemaris tityus Moths

Idaea dilutaria Moths

Idaea dilutaria Moths

Idaea ochrata cantiata Moths

Idaea ochrata cantiata Moths

Jodia croceago Moths

Lycia zonaria britannica Moths

Lycia zonaria britannica Moths

Macaria carbonaria Moths

Macaria carbonaria Moths

Noctua orbona Moths

Noctua orbona Moths

Oria musculosa Moths

Pareulype berberata Moths



Pechipogo strigilata Moths

Pechipogo strigilata Moths

Polia bombycina Moths

Polia bombycina Moths

Pyropteron chrysidifromis Moths

Pyropteron chrysidifromis Moths

Rheumaptera hastata Moths

Rheumaptera hastata Moths

Shargacucullia lychnitis Moths

Shargacucullia lychnitis Moths

Siona lineata Moths

Siona lineata Moths

Trichopteryx polycommata Moths

Trichopteryx polycommata Moths

Tyta luctuosa Moths

Tyta luctuosa Moths

Xylena exsoleta Moths

Xylena exsoleta Moths

Zygaena loti scotica Moths



Zygaena viciae argyllensis Moths



Clubiona rosserae Spider

Dolomedes plantarius Spider



Eresus sandaliatus Spider

Eresus sandaliatus Spider

Chara connivens Stonewort

Chara connivens Stonewort

Chara curta Stonewort



Nitella gracilis Stonewort

Nitella tenuissima Stonewort

Nitella tenuissima Stonewort

Nitellopsis obtusa Stonewort




Tolypella intricata Stonewort



Tolypella prolifera Stonewort



Hirudo medicinalis Worm

Target type Target text 2005 baselineUK

Range T1 3.00

Range T1 4.00

Range T1 8.00

Range T1 5.00

Range T1 0.00

Range T1 5.00

Range T1 3.00

Range T1 5.00

Range T1 2.00

Range T1 6.00

T1 300.00

T2 53.00

Range T3 0.00

Range T1 1.00

Range T1 1.00

Range T1 1.00

Range T1 1.00

Range T1 5.00

Range T1 9.00

Range T1 1.00

Target number

Target units

Maintain the range of populations of Andrena ferox in England.

Site(s) / Population(s)

Maintain the range of populations of Bombus distinguendus in Scotland.


Maintain the range of populations of Bombus humilis in the UK.


Maintain the range of populations of Bombus ruderatus in England.


Establish and maintain a viable population within known historic range by 2015.


Maintain the range of populations of Bombus sylvarum in the UK.


Maintain the range of populations of Cerceris quadricincta in England.


Maintain the range of populations of Cerceris quinquefasciata in England.


Maintain the range of populations of Chrysis fulgida in England.


Maintain the range of populations of Colletes floralis in the UK.


Population Size

Maintain the size of populations in Scotland and England.


Population Size

Enhance the Scottish populations at Mar Lodge and Rannoch and the population at Chudleigh Knighton Heath (Devon) by 2015.


Establish self-sustaining populations in appropriate locations in the south of England such as Devon, Dorset or the New Forest by 2030.


Maintain the range of populations of Formica rufibarbis in the Thames Basin Heaths.


Maintain the range of populations of Homonotus sanguinolentus in Dorset Basin Heaths.


Maintain the range of populations of Nomada armata in the Salisbury Plain.


Maintain the range of populations of Osmia inermis in the Cairngorms/ Grampians.


Maintain the range of populations of Osmia parietina in the UK.


Maintain the range of populations of Osmia uncinata in Scotland.

Occupied 10 km squares

Maintain the range of populations of Osmia xanthomelana in the Lleyn Peninsula.


Range T1 1.00

Range T1 22.00

Range T1 2.00

T2 Hectares 0.04

Range T3 2.00

Range T1 0.00

Range T1 13.00

Range T2 13.00

Range T1 Maintain populations at all known sites. 4.00

T2 0.00

Range T3 4.00

Range T1 7.00

Range T1 5.00

Range T1 3.00

Range T1 0.00

Range T2 0.00

Range T1 Maintain populations at all known sites 5.00

T2 0.00

Range T3 5.00


Range T2 3.00

Maintain the range of populations of Pseudepipona herrichii in the Dorset Basin Heaths.


Maintain populations of this species at all known sites.




New target type

Increase the extent of suitable habitat by 50% at Birk Crag by 2010.Ensure there are a minimum of 4 viable populations by 2010.


if it is re-found at Lough Neagh, maintain its presence at this site.


Maintain populations within each of the catchments currently occupied by this species.


Encourage spread to two additional 1km squares by 2015.

Occupied 1 km squaresSite(s) / Population(s)

Population Size

Enhance populations at current sites by 2010.


Establish viable populations at a minimum of 5 sites in total by 2010.


Maintain viable populations of blue ground beetle at all known sites on Dartmoor.


Maintain populations of this species at all current sites within its known range.






Ensure the establishment and maintenance of five new viable populations at suitable sites within the historic range by 2015.



Population Size

Enhance populations at all known sites by 2010.


Establish new populations so that the southern and northern areas contain five each by 2010.



Ensure that viable populations are established and maintained at a minimum of five sites (including current sites) by 2010.



Range T2 3.00

T3 0.00

Range T1 2.00

Range T2 2.00

T3 0.00

Range T1 Hectares 834.00

T2 Hectares 834.00

Range T1 6.00

Range T1 20.00

Range T2 20.00

Range T1 10.00

Range T2 10.00

Range T3 6.00

Range T4 6.00

Range T5 7.00

Range T6 7.00

Range T7 23.00

Range T8 23.00


Ensure that viable populations are established and maintained at a minimum of five sites (including current sites) by 2010.


Population Size



Maintain populations at all known sites in both England and Scotland.


Ensure the establishment and maintenance of two new viable populations in England and two in Scotland by 2015.


Population Size

Enhance populations at all known sites by 2010


Maintain the area of habitat in key areas occupied by the species.

New target type

Increase the area of available habitat by a further 8 ha per 5 year period.Maintain current range of the maple woodboring beetle.


Maintain the current known range of the noble chafer.


Increase the number of populations of noble chafer within its range through re-establishing it into areas within its historical distribution by 2015.


Maintain populations of Bembidion testaceum within each of the catchments currently occupied.


Encourage the spread of Bembidion testaceum populations to two additional 1km2 by 2015.


Maintain populations of Hydrochus nitidicollis within each of the catchments currently occupied.


Encourage the spread of Hydrochus nitidicollis populations to one additional 1km2 by 2015.


Maintain populations of Lionychus quadrillum within each of the catchments currently occupied.


Maintain populations of Meotica anglica within each of the catchments currently occupied.


Maintain populations of Perileptus areolatus within each of the catchments currently occupied.


Encourage the spread of Perileptus areolatus populations to five additional 10km2 by 2010.


Range T9 2.00

Range T1 3.00

Range T1 150.00

Range T1 6.00

Range T2 0.00

Range T1 Maintain populations at all known sites 3.00

T2 0.00

Range T3 3.00

Range T1 3.00

T2 Hectares 0.10

Range T1 1.00

Range T2 Expand current range of this species. 1.00

Range T1 17.00

Range T3 3.00

Range T1 3.00

T2 0.00

Range T1 3.00

T2 Hectares 0.35

Range T3 3.00

Maintain populations of Thinobius newberyi within each of the catchments currently occupied.


Maintain all known and newly discovered populations and the trees they inhabit.


Maintain populations of stag beetle within its natural geographical range in the UK.


Maintain populations of this species on all known sites across its current range.


Ensure the establishment and maintenance of five new viable populations across the historic range by 2015.



Population Size



Ensure that viable populations are established and maintained at a minimum of five, well-separated sites (including current sites) in England, together with at least one in lowland Scotland by 2015.




New target type

Increase the extent of suitable habitat by 50% at 1 sites by 2010.Maintain current single population by habitat protection and appropriate management.



Maintain the known range of the climbing corydalis weevil in the UK.


Ensure that viable populations are established and maintained at a minimum of six, well-separated sites, (including current sites) within its historical range by 2015, including at least two in Northern Ireland


Maintain populations of this species at all known sites


Population Size





New target type

Increase the extent of suitable habitat by 10% on the River Parrett by 2010.Ensure there are populations of this species in a minimum of 4 river catchments by 2010.


T1 7.00

T1 Population index 100.00

Range T2 100.00

T1 Displaying males 46.00

Range T2 28.00


Range T4 0.00

T1 290.00

Range T2 45.00

T3 103.00

T4 0.60

T1 Displaying males 4,089.00

Range T2 272.00

Range T3 272.00


Range T2 100.00

Population Size

Increase the marsh warbler population to 15 breeding pairs by 2010.

Breeding pairs / units

Population Size

Ensure the BBS index is at 100% of the 2003 level by 2010 for the UK, England, Northern Ireland and Scotland (increasing to 115% by 2015), and is maintained at this level in Wales.

Maintain the percentage of occupied BBS squares at the 2003 levels.

% Occupied BBS Squares

Population Size

Increase the number of booming male bitterns to 60 in the UK by 2010. Increase the number of sites supporting booming male bitterns in the UK to 32 by 2010.


New target type

Increase the number of booming male bitterns in the UK on inland sites (ie sites not at risk from saline intrusion) to 24 by 2010.

Restore bittern range to > 4 occupied 10km squares in Wales by 2020.


Population Size

Increase the population of stone-curlews to 300 pairs by 2010.


Increase the range of the stone-curlew to 49 10 km squares by 2010.


Population Size

Increase the population of stone-curlews breeding on semi-natural habitats to 120 pairs by 2010.


Population Size

Achieve annual breeding productivity of 0.7 young fledged per breeding pair by 2010.

Fledged young per breeding pair

Population Size

Achieve an increase in the number of churring males in the UK, from 4,079 to 4800 by 2016. (an 18% population increase in 12 years)

Maintain the current range (272 occupied 10km squares) of nightjar in UK.


Increase the range to 311 occupied ten km squares by 2016 (a 13% range increase in 12 years).


Population Size

Increase the BBS index to 115% of the 2003 level by 2010 for UK, England and Scotland, and maintain the index at the 2003 level in Wales. In Northern Ireland, ensure the population is at 115% of 2010 baseline level by 2015, the immediate priority for Northern Ireland is to establish population baseline by 2010.

Maintain the percentage of occupied BBS squares at the 2004 level.



Range T2 2.00

Range T3 79.00

T1 800.00

Range T2 124.00

Range T3 0.00


Range T2 100.00

T1 0.00

T1 0.00

Range T1 83.00

T2 0.00

T1 1,500.00

Population Size

To increase the number of calling male corncrakes in England and Northern Ireland to 22 by 2010. To increase the number of 10 km squares supporting calling male corncrakes in England and Northern Ireland to 3 by 2010.


Maintain the range of corncrakes in the Scotland at or above the currrent level.


Population Size

Increase UK population from 800 pairs to 1050 pairs by 2010.


Increase range through natural recolonisation in South Devon/Cornwall from 124 tetrads to 140 tetrads by 2010.


Increase the range in southern England by establishing 1 self sustaining population by 2010, 2 self sustaining populations by 2015, and 3 self sustaining populations by 2020.


Population Size

For UK, England and Scotland, increase the BBS index to 115% of the 2003 level by 2010. For Northern Ireland, increase the population to 115% of the 2010 baseline by 2015. For Wales, maintain the population at the 2010 baseline level. The immediate priority for Northern Ireland annd Wales is to establish the population baseline by 2010.

For UK, England, Northern Ireland and Scotland, increase the percentage of occupied BBS squares to 110% of the 2003 level by 2010. In Wales, maintain the percentage of occupied BBS squares at the 2010 level (immediate priority is to establish the population baseline by 2010).


Population Size

Re-establish the wryneck as a regular breeding species in the UK by 2015.


Population Size

Re-establish the red-backed shrike as a regular breeding species in the UK by 2015.


Achieve an increase in the breeding range of Scottish crossbill from current 83 occupied 10 km squares, to 90 occupied 10 km squares by 2010.


Population Size

Increase the current breeding population of Scottish crossbill.


Population Size

Achieve an increase in the number of breeding pairs in the UK, from 1,500 to 2,150 by 2018.


Range T2 90.00

Range T3 90.00

T1 95.00

Range T2 23.00

Range T3 0.00

Range T4 14.00

Range T5 14.00

T6 Individuals 50,000.00



Range T3 0.00

Range T4 0.00


Maintain the current range (90 occupied 10 km squares) of woodlark in UK.


Increase the range to 125 occupied ten km squares by 2018 (a 39% range increase in 12 years).


Population Size

Increase the population of common scoter to at least 100 breeding pairs by 2010.


Maintain at least the existing breeding range of common scoter in Scotland (23 Occupied 10 km squares).


Regain common scoter as a breeding species in Northern Ireland by 2015.


Maintain the current range of moulting common scoters in the UK.


Maintain the current range of wintering common scoters in the UK.


Population Size

Maintain the current population of wintering common scoters in the UK.

Population Size

In England, ensure the BBS index is no longer showing a negative trend 2010 and is at least at 100% of the 2003 level by 2015. In Scotland, ensure the population is at 100% of the 2010 baseline by 2015. Immediate priority for Scotland will be to establish the baseline population by 2010.

Population Size

In Wales, establish viable breeding population of >10 singing males by 2020.In England, ensure the percentage of occupied BBS squares is at 100% of the 2003 level by 2010. In Scotland, increase the percentage of occupied BBS squares to 110% of the 2010 level by 2015. Immediate priority for Scotland will be to establish the population baseline by 2010.


In Wales, increase number of occupied 1km squares to 4 by 2020.


Population Size

In England, ensure the BBS index is no longer showing a negative trend by 2010 and is at least at 100% of the 2003 level by 2015. In Northern Ireland, Scotland and Wales ensure the population is at 100% of the 2010 baseline by 2015. Immediate priority for these countries will be to establish the baseline population by 2010.

Range T2 0.00


Range T2 0.00

T1 65,000.00

Range T2 1,450.00


Range T2 10.00

Range T3 26.00


In England and Wales, maintain the percentage of occupied BBS squares at the 2003 level. In Northern Ireland and Scotland, maintain the percentage of occupied BBS (i.e. 1 km) squares at 2010 levels by 2015. The immediate priority in NI and Scotland will be to establish the baseline.


Population Size

In England, increase the BBS index to 150% of the 2003 level by 2010. In Northern Ireland, Scotland and Wales ensure the population is at 150% of the 2010 baseline by 2015. Immediate priority for these countries will be to establish the baseline population by 2010.

In England, increase the percentage of occupied BBS squares to 110% of the 2003 level by 2010. In Northern Ireland, Scotland and Wales, increase the percentage of occupied BBS squares to 110% of 2010 levels by 2015. Immediate priority in these countries will be to establish the population baseline by 2010.


Population Size

Ensure the UK population of grey partridge is above 90,000 breeding pairs by 2010.


Achieve an increase in the range of grey partridge from current 1,450 occupied 10 km squares, to 1,530 occupied 10 km squares by 2015.


Population Size

Maintain red-necked phalarope as a UK breeding species with 35 males by 2010. Ensure that breeding red-necked phalarope occur at 10 sites, in any single year.


Ensure that 26 available sites are in suitable condition for breeding phalarope.


Population Size

In England, ensure the BBS index is no longer showing a negative trend by 2010 and is at least at 100% of the 2003 level by 2015. In Wales, increase the population to 140% of the 2003 level by 2015. In Northern Ireland and Scotland ensure the population is at 100% of the 2010 baseline by 2015. Immediate priority for Northern Ireland and Scotland will be to establish the baseline population by 2010.

Range T2 100.00

Range T1 95.00

T2 0.94

T1 Population index Trend -ve


Range T3 Trend -ve

Range T4 0.00

T1 Displaying males 4,388.00

Range T2 295.00


Range T2 40.00


Range T2 100.00

Range T1 6.00

T2 0.00

Range T1 28.00

Maintain the percentage of occupied BBS squares at the 2003 level in the UK, England, Northern Ireland and Scotland, aiming for an increase to 120% of current level by 2015 in Wales.


Increase the UK roseate tern population to 130 pairs by 2010, 155 pairs by 2015 and 180 pairs by 2020.


Population Size

Enable roseate tern productivity at all colonies to average above 1.2 fledged young per pair for each of three successive years within each five year period.

Fledged young per breeding pair

Population Size

For UK and England, ensure the BBS index is no longer showing a negative trend by 2010 and is at least at 100% of the 2003 level by 2015.

Population Size

In Wales, establish viable breeding population of >10 singing males by 2020.In the UK and England, ensure a stable or positive trend in the percentage of occupied BBS squares by 2010.


In Wales, increase range from 2005 level to 2 occupied 10 km squares by 2015.


Population Size

Increase the population of black grouse to 4500 lekking males by 2010.

Restore the range of black grouse to 300 occupied 10km squares by 2010.


Population Size

Increase the population of capercaillie in Scotland to 5000 birds by 2010.Achieve an increase in the range of capercaillie from current 40 occupied 10 km squares, to 45 occupied 10 km squares by 2010


Population Size

In England, Northern Ireland and Scotland, increase the BBS index to 115% of the 2003 level by 2010. In Wales, maintain populations at the current (2003) level.

Maintain the percentage of occupied BBS squares at the 2003 levels in the UK and all four countries.


Maintain the current range of triangular pygmy moss.


Population Size

Increase population size at 2 sites by 2015.




Range T1 1.00

Range T1 22.00

Range T1 1.00

T2 0.00

Range T3 1.00

T1 7.00

Range T1 12.00

T2 0.00

Range T1 7.00

Range T1 31.00

T2 0.00

Range T1 11.00

T2 7.00

Range T1 1.00

Range T2 1.00

Range T1 17.00

Range T1 2.00

T2 0.00

Range T1 15.00

Range T1 1.00

Range T1 7.00

Range T1 3.00

Range T2 3.00

Maintain populations of this species at its one known site.


Maintain existing populations within known range.


Maintain the population of Bartramia stricta at its single known extant site.


Population Size

Achieve favourable condition for Bartramia stricta at its one extant site by 2015.


Double the number of sites by re-establishing this species at one suitable former site by 2015.


Population Size

Maintain the size of the existing 7 main populations at 2000/2005 levels.


Maintain the range of this species in the UK at 12 extant sites.


Population Size

Achieve an increase in population size and/or number of populations at 3 sites by 2015.


Maintain the range of this species at seven 10km squares.


Maintain the current range of greater copperwort.


Population Size



Maintain the UK range of this species at ten 10km squares.


Population Size

Maintain the extent of populations within the range in the UK.


Maintain the population of glaucous beard-moss at its sole British site.


Expand the range of glaucous beard-moss from its current single site to one additional site by 2015.


Maintain the range of this species in the UK at seventeen 10km squares.


Maintain current range of Cornish path-moss.


Population Size

Increase the population size at the 2 known sites by 2015.


Maintain the current range of lead moss in Britain.


Maintain populations of this species at its known extant site.


Maintain populations of this species at all 7 sites in the UK.


Maintain viable populations at all extant sites in England and Scotland.


Extend the range of this species to a further site in Norfolk by 2015, bringing the total number of sites to four.


Range T1 8.00

Range T1 8.00

Range T2 8.00

Range T1 11.00

T2 11.00

Range T1 9.00

Range T2 9.00

Range T1 8.00

T2 0.00

Range T1 8.00

Range T1 21.00

T2 0.00

Range T1 27.00

T2 0.00

Range T1 2.00

Range T1 2.00

T2 0.00

Range T1 23.00

Range T1 1.00

T2 0.00

Range T1 4.00

T2 4.00

Maintain viable populations of this species at all 8 extant sites in the UK.


Maintain current range (post-2000) of the Thatch-moss.


Increase number of sites (thatched roofs) from the current 8 sites to 10 sites by 2015.


Maintain the current range of western rustwort.


Population Size

Increase the number of populations within current range from 11 sites to 12 sites by 2010.


Maintain the current range of slender thread moss.


Increase the number of populations of slender moss from 9 sites to 12 sites by 2015.


Maintain all known populations of this species.


Population Size

Increase the extent of populations of Orthotrichum obtusifolium through expansion of existing stands and encouraging regeneration by 2010.


Maintain viable populations of this species at all 8 known sites.


Maintain viable populations of veilwort at all extant sites in the UK.


Population Size

Increase the population size of veilwort at 5 sites by 2015.


Maintain the geographical range in the UK at 27 occupied 10km squares.


Population Size

Increase the population size of petalwort at 7 sites by 2015.


Maintain populations of this species at its two extant sites


Maintain populations of round-leaved feather-moss at both known sites.


Population Size

Increase the population size at the 2 known sites by 2015.


Maintain populations of this species at 23 sites in the UK.


Maintain viable populations of this species at its one extant site and any other sites where extant colonies are found.


Population Size

Increase the population size of this species at its one extant site by 2010.


Maintain populations of this species at all extant sites.


Population Size

Increase the extent of populations of this species at all extant sites by 2015.


Range T1 2.00

Range T1 1.00

Range T1 1.00

Range T1 4.00

T2 0.00

Range T1 12.00

Range T1 2.00

T2 0.00

Range T1 16.00

Range T1 3.00

Range T1 10.00

T2 0.00

Range T1 3.00

Range T2 3.00

Range T3 20.00

Range T1 47.00

Range T2 19.00

T3 47.00

Range T1 194.00

Range T2 29.00

Range T3 94.00

Range T1 27.00

Range T2 0.00

Range T1 Maintain the core range of the species. 280.00

Maintain viable populations of this species at both extant sites.


Maintain the population of Derbyshire feather-moss at its one extant site.


Maintain the population of Yorkshire feather-moss at its one extant site..


Maintain the UK range of this species at four 10km squares.


Population Size

Increase the population size at two sites by 2015.


Maintain the range of this species in Britain.


Maintain populations of the many-fruited beardless- moss at its known extant sites.


Population Size

Increase the population size of this species at its two extant sites by 2010.


Maintain the range of species at sixteen 10km squares.


Maintain populations of the knothole moss at its known extant sites.


Maintain current range of Nowell’s limestone moss.


Population Size





Ensure adult colonies are present at 6 sites by 2010.


Ensure Lophopus statoblasts are present in 25 sections of river systems by 2010.


Maintain the core range of the species in the UK.


Maintain viable populations within the existing 19 networks.


Population Size

Increase the number of occupied sites within each network.


Maintain the core range of the species in the UK.


Maintain viable networks (metapopulations) within 29 core regions.


Increase the number of occupied sites within each network.


Maintain current range of the chequered skipper in Scotland.


Restore a viable population in England by 2020 and a further four populations by 2030.



Range T2 315.00

Range T1 37.00

T1 10.00

Range T2 0.00

Range T1 25.00

T2 Hectares 20.00

Range T3 10.00

Range T4 0.00

Range T5 4.00

Range T1 75.00

Range T2 377.00

Range T1 95.00

Range T1 5.00

T2 Individuals 700.00

Range T1 2.00

Range T1 6.00

Range T1 2.00

Increase the amount of occupied habitat from current 315 1km squares to 373 1km squares within core areas by 2010.


Achieve an increase in the range from 37 to 43 occupied 10km squares by 2010. To achieve this target will mean maintaining existing range.


Population Size

Consolidate the 10 re-established populations in four landscape areas in England, aiming to achieve colonies containing 400 to 5000 adults in each year.


Re-establish populations at a further 10 former sites in five landscape areas in England by 2020.


Maintain a minimum of 25 interconnected colonies in Kent.


New target type

Increase area of suitable interconnected habitat (active coppice & open areas) in Kent to 1980 levels by 2010 and then maintain.

Maintain the current range in east Cornwall, Devon and Somerset.


Restore populations in east Cornwall, Devon & Somerset to 1989 status by 2030.


Maintain the re-introduced populations in Essex.


Maintain the current range of the silver-studded blue.


Expand distribution of the silver-studded blue within current range.


Achieve an increase in the range from 95 to 114 occupied 10km squares by 2010.


Achieve an increase in range of the wart-biter grasshopper from 5 to 10 sites/populations by 2010.


Population Size

Achieve an increase in population size from approximately 700 to approximately 1000 individuals by 2010.

Achieve an increase in range of the mole cricket from 2 to 3 occupied 10km squares by 2010.


Achieve an increase in the range of the field cricket from 6 to 9 occupied 10km squares by 2010.


Achieve an increase in range of the large marsh grasshopper from 2 to 3 occupied vice counties by 2010.

Occupied vice counties

T2 12.00

Range T1 241.00

Range T2 241.00

T3 19.00

Range T1 23.00

Range T2 84.00

T3 21.00

Range T1 0.00

Range T2 0.00

Range T3 0.00

Range T4 0.00

Range T1 0.00

Range T2 0.00

Range T3 0.00

Range T1 3.00

Population Size

Maintain the extant populations of this species in 12 occupied 10 km squares.


Maintain current range of white-clawed crayfish in the UK.


Achieve an increase in range of white-clawed crayfish in the UK by 59 10 km squares to 300 by 2030.


Population Size

Maintain key populations of white-clawed crayfish in the UK.


Maintain populations of southern damselfly across the current geographical range in the UK.


Expand the UK range by restoring habitat in additional 36 one-km squares in England and Wales to achieve larger and better linked population clusters by 2015.


New target type

Increase the number of population clusters in Favourable Condition (as defined by the statutory agencies). 100% to be in favourable condition by 2030.


Expand the range of allis shad to 2 historic river site(s) by 2015 by natural re-colonisation or re-introduction (target applicable in England and Wales).


Maintain spawning allis shad populations in at least the lower part of the R Tamar (target applicable in England).


Expand the range of allis shad up the River Severn beyond Worcester by 2010, and Shrewsbury by 2015.


Maintain breeding populations of shad spp. in the Scottish and English Solway rivers. (This will involve establishing the extent of breeding shad use by 2010).


There should be no decline in the breeding distribution of twaite shad at all extant river sites in the UK.


Expand the range of twaite shad up the River Severn beyond Worcester by 2010, and Shrewsbury by 2015.


Maintain breeding populations of twaite shad in the Scottish and English Solway rivers. (This will involve establishing the extent of breeding shad use by 2010).


Ensure the continued survival of the species in Bassenthwaite Lake, Derwentwater and Loch Skene.


Range T2 1.00

Range T3 2.00

Range T1 141.00

T2 60.00

Range T1 2.00

Range T2 2.00

T3 2.00

Range T1 36.00

Range T1 30.00

Range T1 15.00

Range T1 13.00

Range T1 16.00

Range T1 12.00

Range T2 0.00

T3 0.00

Range T1 6.00

Range T1 53.00

T2 90.00

Range T1 7.00

T2 21.00

Range T1 2.00

Establish a self-sustaining population in a second water in Scotland by 2010 and further populations at an additional two sites by 2020.


Establish a self-sustaining population in at least one additional Lake District water by 2010.


Maintain the current range of the hornet robberfly.


Population Size

Maintain key (meta)populations of the hornet robberfly in England and Wales.


Maintain a population at all currently occupied sites.


Achieve an increase in the range from 2 to 3 sites by 2010.


New target type

Maintain and enhance areas of suitable breeding habitat at currently occupied sites.


Maintain populations within current geographic range by 2010.


Maintain populations of this species in all known river systems.






Maintain viable populations of the bog hoverfly at all known areas on Dartmoor.


Maintain a population at all currently occupied sites.


Increase the amount of suitable breeding habitat at 5 potentially occupied sites by 2010 and maintained afterwards.


New target type

Enhance areas of suitable breeding habitat at currently occupied sites.


Maintain the current range of this species.


Maintain the current range of this species.


Population Size

Maintain key populations in England and Wales.


Maintain populations of this species in all currently occupied river systems.


Population Size

Ensure there are at least 4 populations of this species in each of the seven occupied river systems by 2010.


Maintain populations of this species at all extant sites.


Range T2 2.00

Range T1 27.00

Range T1 1.00

Range T2 1.00

Range T1 5.00

Range T2 5.00

Range T1 26.00

Range T2 0.00

Range T3 Metapopulation(s) 2.00

Range T1 28.00

T2 18.00

Range T1 3.00

Range T1 11.00

T2 Increase populations at 2 sites by 2015. 0.00

Range T1 81.00

T2 Hectares 770.00

Range T1 55.00

T2 55.00


Increase number of occupied 1km squares.


Maintain populations on all currently occupied rivers.


Maintain viable populations of this species at its extant site.


Establish and maintain a further five viable populations by 2015.


Maintain populations of this species at all extant sites within its current range.


Expand the current range of creeping marshwort to a further 2 sites by 2015.


Maintain the current (natural) range within twenty-six 10km squares.


Establish populations at 3 sites within the historic range by 2010.


Establish four meta-populations within the species current range by 2010.Maintain the geographical range, as defined by presence, at all 28 known sites.


Population size

Ensure that all 28 populations have at least 10 plants, including both sexes, by 2010.


Maintain populations of interrupted brome at all extant sites within its current range.


Maintain the current range of true fox-sedge.


Population Size


Maintain current range of natural populations (sites where the species is deemed to be long establised) within 81 10km squares in the UK.


New target type

Achieve a two-fold increase in the area of habitat suitable for the natural colonisation of the species by 2010 in priority areas.

Maintain populations of this species at all extant sites within its natural range.


New target type

Achieve management that provides suitable habitat for population expansion by 2015.


Ensure that the total number of 0.1km squares containing plants that are able to flower does not fall below 29 in 3 out of every 4 consecutive years.

Range T2 Kilometres 2.40



Range T1 1.00

T2 Individuals 6.00

Range T1 0.00

Range T1 9.00

Range T2 9.00

Range T1 35.00

Range T2 35.00

Range T3 Establish two metapopulations by 2010. Metapopulation(s) 1.00

Range T1 13.00

Range T1 21.00

T2 0.00


Range T1 10.00

Range T2 Establish two metapopulations by 2010. Metapopulation(s) 0.00

Ensure that the south to north range of the plant on the east coast of Lundy does not contract from that of the 1998 range - Marisco Castle to Knight's Templar Rock (2.4 km)

Population Size

Ensure that the total number of plants that flower in 3 out of every 4 years does not fall below 1200 individuals.

Population Size

The total number of plants that flower in the southern quarter of the island (Millcombe to Lametry) is at least 400 in 3 out of every 4 years.

Maintain the current population at the one extant site.


Population size

Reinforce the existing population with seed and / or vegetative material derived from the remaining six naturally-established plants to achieve a population of 100 annually fruiting plants and evidence of natural seedling establishment within 20 years.

Establish 3 self-sustaining populations of this species by 2010 (and maintain them by 2015).


Maintain viable populations at nine extant native and introduced sites.


Establish and maintain viable populations at 2 historic sites by 2010, bringing the total number of sites to eleven.


Maintain viable populations of this species at all extant native sites.


Establish populations at 3 sites within historic range by 2010, bringing the total to 38 sites.


Maintain all extant populations where Epipactis youngiana plus either E. helleborine or E. dunensis occur.


Maintain viable populations of this species at all extant sites.


Population Size

Achieve an increase in population size at ten extant populations by 2010.


Establish three metapopulations by 2010.Maintain viable populations of this species at all extant sites.


Range T1 73.00

T2 10.00

Range T1 77.00


Range T1 2.00

Range T2 0.00

T1 21.00

T2 0.00

Range T3 102.00

T1 4.00

Range T2 4.00

T1 No. of species 11.00

Range T1 400.00

T2 0.00


T4 0.00

Range T1 77.00

T2 0.00

Maintain the geographical range of this species in the UK.


Population Size

Maintain viable populations within the existing core areas.


Maintain current range of natural populations within 77 10km squares in the UK.


Achieve a 2-fold increase in the area of habitat suitable for the natural colonisation of the species by 2010 in priority areas.

Maintain viable populations at all extant 'natural' sites where the species is deemed to be long-established.


Facilitate natural colonisation of three suitable sites within priority areas by 2010 (by ensuring the appropriate habitat condition are in place).


Population Size

Maintain all extant populations in vulnerable vice countries in the UK.


Population Size

Within vulnerable areas increase population size at five sites by 2010.


Maintain 102 populations (=1km sq) in stronghold vice countries.


Population size

Develop and maintain viable populations at all 4 extant sites in south Wales


Restore two new viable populations to former sites in South Wales by 2015.


Population Size

For each species, ensure the survival of at least 200 plants in at least two wild populations within appropriate habitats by 2015.

Maintain the current range of juniper in the UK.


Population Size

Restore representative tree-line juniper populations where relict juniper persists at 5 sites in Scotland by 2015.


Population Size

Increase overall population size Juniperus ssp. Hemisphearica from 11 individuals to 22 by 2010.

Population Size

Restore H15 Juniperus ssp. Nana communities in 3 areas of Scotland by 2015.


Achieve self-sustaining populations at extant sites within native stronghold areas.


Population Size

Establish populations of Linnaea borealis at 3 suitable sites by 2015, (so as to increase linkages between isolated populations to facilitate gene flow)


Range T3 9.00

Range T1 7.00

T2 7.00

Range T3 7.00

Range T1 40.00

T2 0.00

Range T1 62.00

Range T2 25.00


T1 22.00

Range T2 22.00

T3 0.00

Range T1 18.00

T2 0.00

Range T1 40.00

Range T2 40.00

Range T1 7.00

Ensure the survival of isolated populations outside the Speyside stronghold range through appropriate site management.


Maintain 3 fen sites in England and 4 dune populations in Wales for the fen orchid.


Population Size

Maintain viable populations at all extant sites in Wales and in the Norfolk Broads.


Extend the range of fen orchid to a further 3 sites in the broads and 1 in Carmarthenshire by 2010.


Maintain the current range of this species in the UK.


New target type

By 2010 increase connectivity of sites within two vulnerable lowland populations (Pembrokeshire and Severn Valley) through landscape scale enhancements and local improvements to habitat.


Maintain current range of the species in the UK in 62 10-km squares.


Maintain 25 extant populations in vulnerable areas.


Establish one new metapopulation within the species' historic range (excluding the New Forest) by 2010.

Population Size

Maintain existing populations of this species as components of viable and functioning ecosystems.


Establish, by 2010, small cow-wheat at five additional suitable sites in order to commence process of extending distribution in Britain.


New target type

Ensure there are 5 new populations of this species of greater genetic diversity by 2010 (so they might be able to adapt to the effects of climate change).


Maintain the current range of pennyroyal in the UK.


Population Size

Increase the population size at 4 sites by 2015.


Maintain populations of this species at all extant sites (with post-1980 records) within its current range.


Restore species to three water bodies where it is understood to be extinct, including Esthwaite Water, by 2020.


Maintain viable populations at all extant sites in the Norfolk Broads.


Range T2 7.00

Range T1 91.00

Range T2 7.00

Range T3 0.00

Range T1 28.00

T2 13.00

T3 0.00

Range T1 11.00

Range T2 0.00

Range T1 27.00

Range T2 18.00

Range T3 0.00

Range T4 0.00

Range T1 32.00


T2 2.00

Range T3 2.00

Range T1 166.00


Range T1 87.00

Extend the range to a further 3 waterways adjacent to existing sites by 2010.




Maintain extant viable populations in the 7 vulnerable areas.


Establish two new metapopulation within the species' historic range (excluding the New Forest) by 2010.


Maintain the current range of this species in the UK.


Population Size

Ensure that all extant populations achieve long-term viability and favourable condition by 2015.


New target type

Establish connectivity between two existing, healthy populations by 2015.


Maintain populations of this species at all extant sites (with post-1980 records) within its current range.


Restore species to two water bodies where it is understood to be extinct by 2020.




Maintain extant populations in vulnerable Natural Areas.


Establish two new metapopulations within the species' historic range by 2010.


Restore populations to an additional five 1-km squares by 2010 outside developing metapopulation areas.


Maintain the number of extant populations of this species in the UK.


Population Size

Increase population size of Salix lanata to over 2000 plants by 2010.

Population Size

Ensure that populations are stable or increasing at all known sites by 2015.


Increase the range of the species by ensuring that populations at four sites can expand by 2015.


Maintain current range of natural populations within 166 10km squares in the UK.



Maintain current range of natural populations within 87 10-km squares in the UK.



Range T1 64.00

Range T2 0.00

Range T1 76.00

Range T1 16.00

Range T2 0.00

Range T1 77.00


Range T1 20.00


Range T1 6.00

T2 1.00

Range T1 4.00

T2 Hectares 0.00

Range T1 16.00

Range T1 1.00

Range T1 33.00

Range T1 21.00

Range T2 7.00

Achieve a 2-fold increase in the area of habitat suitable for the natural colonisation of the species by 2010 in priority areas

Maintain the current range of greater water-parsnip in the UK.


Increase the range from baseline by return of species at five historic sites by 2010.


Maintain viable populations of this species throughout its UK range.


Ensure viable populations are maintained at 16 extant sites within the species natural range


Establish one metapopulation within the species natural range by 2010


Maintain current range of natural populations with 77 10-km squares in the UK.



Maintain viable populations at all extant ‘natural’ sites where the species is deemed to be long-established.



Maintain populations of this species at all extant and re-introduced sites in the UK.


Population Size

Reinforce the populations of Woodsia ilvensis at two extant sites by 2010. Consider further reinforcement if plant numbers fall below 4 plants at the remaining Scottish site.


Achieve an increase in the known post-1960 range from four to six occupied 10 km squares by 2015.


Population Size

Maintain areas of fruiting populations at extant sites by 2015.Maintain the known range of sandy stiltball at 16 10km squares.


Maintain the range of the Royal bolete at 1 10km squares.


Maintain the range of the Devil's bolete at 33 10km squares.


Maintain the range of Bankera fuligineoalba at 21 10km squares.


Maintain the range of Hydnellum aurantiacum at 7 10km squares.


Range T3 11.00

Range T4 47.00

Range T5 15.00

Range T6 23.00

Range T7 28.00

Range T8 28.00

Range T9 22.00

Range T10 30.00

Range T11 21.00

Range T12 5.00

Range T13 43.00

Range T14 13.00

Range T1 42.00

Range T1 320.00

Range T1 23.00

Range T1 14.00

Range T1 69.00

Range T1 30.00

Range T1 4.00

Range T1 3.00

T1 2,500.00

Range T2 27.00

Range T3 17.00

Range T1 14.00

Maintain the range of Hydnellum caeruleum at 11 10km squares.


Maintain the range of Hydnellum concrescens at 47 10km squares.


Maintain the range of Hydnellum ferrugineum at 15 10km squares.


Maintain the range of Hydnellum peckii at 23 10km squares.


Maintain the range of Hydnellum scrobiculatum at 28 10km squares.


Maintain the range of Hydnellum spongiosipes at 28 10km squares.


Maintain the range of Phellodon confluens at 22 10km squares.


Maintain the range of Phellodon melaleucus at 30 10km squares.


Maintain the range of Phellodon tomentosus at 21 10km squares.


Maintain the range of Sarcodon glaucopus at 5 10km squares.


Maintain the range of Sarcodon imbricatus/ squamosus at 43 10km squares.


Maintain the range of Sarcodon scabrosus at 13 10km squares.


Maintain the known post-1960 range of 42 occupied 10 km squares in UK.


Maintain the overall geographic range of the Pink meadow-cap.


Maintain the range of the Date-colored waxcap at 23 10km squares.


Maintain the range of this species at 14 10km squares.


Maintain the range of the Olive earthtongue at 69 10km squares


Maintain the known post-1960 range of 30 occupied 10 km squares in UK.


Maintain populations of Nail Fungus at viable levels in the New Forest.




Population Size

Achieve an increase in the number of breeding females in the UK, from 2500 to 3500 by 2010.


Achieve an increase in the range from 27 to 28 occupied 10km squares in the UK by 2010.


Achieve an increase in the range from 17 to 21 occupied vice counties in the UK by 2010.


Achieve an increase in the range from current 14 occupied vice counties to 18 occupied vice counties by 2010.


Range T2 384.00

Range T3 Hectares 1,019.00

Range T1 0.00

T2 0.00

Range T3 0.00

Range T1 904.00

Range T2 88.00

Range T3 100,000.00

T4 60,000.00

Range T1 21.00

Range T1 30.00

Range T1 1.00

Range T1 2.00

Range T1 1.00

Range T1 0.00

Range T1 3.00

Range T1 2.00

Range T1 1.00

Range T1 1.00

Range T1 7.00

Achieve an increase in the range from current 384 occupied kilometre squares to 388 occupied kilometre squares by 2010.


Increase the potential area of occupancy from current 1019 ha of occupied habitat to 1,252 ha of occupied habitat by 2010.

Establish two viable populations within the species historical range by 2010.


Population Size

Increase overall population size of pool frog to 50 breeding pairs by 2010.


Achieve an increase in the range to 2 occupied vice counties by 2010 (within the species historical range).


Achieve an increase in the range of occupied 10 km squares from 904 to 926 by 2010.


Achieve an increase in the range from 88 to 89 occupied vice counties by 2010.


Achieve an increase in the number of occupied ponds from 100,000 to 120,000 by 2010.


New target type

Achieve an increase in the number of ponds with a Habitat Suitability Index of >0.7 from 60,000 to 72,000 by 2010.


Maintain existing populations of this species within known range.


Maintain the range of this species at thirty 10km squares in the UK.


Maintain the extant population of this species at its known site.


Maintain viable populations of this species at both extant sites.


Maintain the range of this species at its one extant site


Re-establish a population of starry breck lichen at 1 site in Breckland by 2010.


Maintain viable populations of this species at all 3 extant sites.




Maintain a population at the one extant site.


Maintain a population at the one extant site.


Maintain existing populations of this species within known range.


Range T1 7.00

T2 0.00

Range T1 3.00

Range T1 2.00

Range T1 12.00

Range T1 15.00

Range T1 22.00

T2 0.00

Range T1 28.00

Range T1 1.00

Range T1 2.00

Range T2 0.00

Range T1 0.00

Range T1 1.00

T2 0.00

Range T1 730.00

Range T2 730.00

Range T1 86.00

Range T1 1,604.00


Range T1 2,219.00

Range T2 2,219.00

Maintain extant populations of this species at 7 sites.


Population Size

Increase population size of this species at 2 sites by 2015.




Maintain populations of this species at both known extant sites.


Maintain the range of this species at least at twelve occupied 10km squares (11 sites).


Maintain the range of this species at 15 extant sites.


Maintain the range of this species at 22 extant sites.


Population Size

Increase the extent of existing populations at 3 sites by 2015.


Maintain the geographical range of this taxa at 28 10km squares.


Maintain populations of this species at the extant site.


Maintain the range of the species at 2 discreet sites in Breckland.


Restore populations of scaly breck lichen at 1 former site by 2010.


Maintain population levels at any sites that are found to be extant.


Maintain the known population and any newly discovered sites.


Population Size

Increase the extent of the population of Thelenella modesta at its known extant site through appropriate management to provide additional habitat for potential spread by 2010.


Maintain the current range (730 occupied 10km squares) of water vole in UK.


Achieve an increase in range by 50 new occupied 10km squares in the UK by 2010.


Maintain the current range of B. barbastellus in the UK


Maintain current range of brown hare in the UK.


Population Size

Increase the population size of brown hare to double the 1995 level (population index = 100) by 2010.Maintain the current distribution of the otter throughout the UK.


Expand the distribution of otters to achieve 85% occupancy of 10 km squares by 2015.

% Occupied 10 km squares

Range T1 376.00

Range T2 11.00

T3 Population index Trend -ve

Range T1 44.00





Range T1 79.00

Range T2 79.00


Range T1 308.00


Range T1 603.00

Range T1 6.00

Range T1 132.00

Maintain the current range (376 occupied 10km squares) of dormouse in UK.


Re-establish self-sustaining dormouse populations at 16 sites, in counties where they have been lost, by 2010.


Population Size

Ensure the dormouse population index is at 100% of the 1991level by 2015 and increase to 115% of the 1991 level by 2020. (Target involves converting the current (2005) negative population trend into a stable or positive population trend by 2010).

Maintain the current range of M. bechsteinii in the UK.


Population Size

Maintain P. pipistrellus population above 2005 baseline level (baseline available only at UK level at this time).

Population Size

Maintain P. pygmaeus population above 2005 baseline level (baseline available only at UK level at this time).

Population Size

Increase P. pipistrellus population index by 35% of the 2005 baseline level by 2020.

Population Size

Increase P. pygmaeus population index by 35% of the 2005 baseline level by 2020.Maintain the current range (79 occupied 10km squares) of greater horseshoe bats in UK.


Achieve an increase the range of greater horseshoe bats in the UK by four 10 km squares by 2010, increasing the total number of occupied squares to 83.


Population Size

Ensure greater horseshoe bat population is at 25% of 2005 baseline level by 2010. Achieve an increase in the range of lesser horseshoe bats in the UK by 86 occupied 10km squares to 394 occupied squares by 2030.


Population Size

Increase R. hipposideros population index by 25% of the 2005 baseline level by 2020.Maintain populations of red squirrels across their current range in the UK.


Maintain current known UK distribution range (Isles of Scilly to Bolt Head)


Maintain the geographical range of this species on UK shores.


Range T1 3.00

T2 Individuals 7.00

Range T1 18.00

T1 0.00

Range T1 7.00

Range T1 2.00

Range T1 66.00

Range T2 66.00

T3 0.00

Range T4 2.00

Range T1 1.00

Range T1 29.00

Range T1 5.00

Range T1 14.00

T2 27.00

Range T1 52.00

Range T1 22.00

Range T1 59.00

Range T1 54.00

Maintain current known range at individual geographical locations around the UK.


Population Size

Maintain the population size of A. fragilis on all known sites (with greater survey effort, numbers will hopefully increase).

Maintain the current known distribution range for this species in the UK.


Population Size

Stabilise all stocks of commercially exploited deep-water species at or above safe biological limits by 2020.

Spawning Stock biomass

Maintain the 7 distinct populations of little ramshorn whirlpool snail currently recorded.


Ensure that viable populations are maintained at all known sites.


Maintain the number of all viable populations of freshwater pearl-mussel in the UK.


Increase the number of viable freshwater pearl mussel populations from 66 to 74 by 2015.


Population Size

Increase the size of 5 viable populations of freshwater pearl mussel by 2015.


Re-establish populations of freshwater pearl mussel at 12 sites within its natural range by 2015.


Ensure the known remaining population and any new populations found are maintained.


To maintain, at least, the existing populations of the fine-lined pea mussel in 29 defined river reaches.


Maintain key populations of P. complanata across their current range in the UK.


Maintain the current range for this species of 27 distinct sites within 14 10km squares.


Population Size

Increase the population size within the current known sites.


Maintain known populations of the narrow-mouthed whorl snail in the UK.


Maintain known range of round-mouthed whorl snail in the UK.


Maintain the known range of Geyer's whorl snail in the UK.


Maintain viable populations of Desmoulin's whorl snail across its current range.


Range T1 1.00

Range T2 1.00

Range T1 11.00

Range T2 11.00

Range T1 1.00

Range T2 1.00

Range T1 8.00

Range T1 7.00

Range T1 10.00

Range T2 10.00

Range T1 2.00

Range T2 2.00

Range T1 9.00

Range T2 9.00

Range T1 31.00

Range T2 13.00

Maintain the single population of the reddish buff moth.


Ensure that there are at least 3 viable populations within the former range in Britain by 2010.


Ensure the populations are maintained on all extant sites.


Ensure that there are at least 14 viable populations within the former range on the North Downs by 2010.


Maintain the single population of the marsh moth.




Maintain populations of the light crimson underwing on all extant sites, by ensuring the requirements of this species are included within the long-term management plans by 2010.


Maintain populations of the dark crimson underwing on all extant sites, by ensuring the requirements of this species are included within the long-term management plans by 2010.


Ensure the populations of the basil thyme case-bearer are maintained on all extant sites.


Ensure that there are at least 12 viable populations within the historic range by 2010.


Ensure the populations of the speckled footman are maintained on all extant sites.




Ensure the populations of the white-spotted pinion are maintained on all extant sites within its known range.


Ensure that there are viable populations in at least 11 10km squares by 2010, concentrating effort on existing strongholds in East Midlands and Essex.


Ensure the populations of the dingy mocha are maintained on all extant sites.


Ensure that there are viable populations in at least 15 10km squares by 2010.


Range T1 6.00

Range T1 4.00

Range T2 4.00

T3 Hectares 0.00

Range T1 20.00

Range T2 6.00

T3 0.00

Range T1 0.00

Range T1 53.00

Range T2 53.00

Range T1 3.00

T2 Hectares 0.00

Range T1 3.00

Range T2 3.00

T1 0.00

Maintain populations of the heart moth on all extant sites, by ensuring the requirements of this species are included within the long-term management plans by 2010.


Ensure the populations of the dark bordered beauty are maintained on all extant sites.




New target type

Increase the amount of potentially suitable habitat on at least one England site by 10ha and in Scotland by 0.5ha by 2010 (to include any newly discovered sites).

Ensure the populations of the netted carpet are maintained on all extant sites.


Ensure that there are viable populations in at least seven 10km squares by 2010.


New target type

Increase the amount of potentially suitable habitat on, or adjacent to, 5 sites by at least 50 square metres by 2010.


If refound, maintain extant populations of the bordered gothic. (Priority will be to maintain populations at any sites that are found to be extant).


Ensure the populations of the narrow-bordered bee hawk moth are maintained on all extant sites.


Ensure that an additional 4 viable populations (on 2005 figure) occur within the historic range by 2010.


Ensure the populations of the silky wave are maintained on all extant sites.


New target type

Increase the amount of potentially suitable breeding habitat on each of the three extant sites (as of 2005) by at least 0.25ha by 2010.

Ensure the populations of the bright wave are maintained on all extant sites.


Ensure that at least 4 viable populations occur within the historic range by 2010.


Population Size

If refound in Britain, enhance the population size at known sites by 2010.


Range T1 3.00

T2 Hectares 0.00

Range T1 20.00

Range T2 20.00

Range T1 33.00

Range T2 33.00

Range T1 1.00

Range T1 9.00

T2 0.00

Range T3 9.00

Range T1 12.00

Range T2 12.00

Range T1 4.00

Range T2 4.00

Range T1 3.00

T2 Hectares 0.00

Range T1 28.00

Ensure the populations of the belted beauty are maintained on all extant sites.


New target type

Increase the amount of potentially suitable habitat by at least 0.1ha by 2010. Ensure the populations of the netted moutain moth are maintained on all extant sites.




Ensure the populations of the lunar yellow underwing are maintained on all extant sites within its known range.




Ensure the populations of the brighton wainscot are maintained on all extant sites.


Ensure the populations of the barberry carpet are maintained on all extant sites, including re-introduction/introduction sites where the moth has survived for more than 3 generations.


Population Size

Enhance population size at 4 known sites (as of 2005) by 2010.




Ensure the populations of the common fan-foot are maintained on all extant sites.




Ensure the populations of the pale shining brown are maintained on all extant sites.




Ensure the populations of the fiery clearwing are maintained on all extant sites.


New target type

Increase the amount of potentially suitable habitat by at least 0.5ha by 2010.Ensure the populations of the argent and sable moth are maintained on all extant sites.


Range T2 28.00

Range T1 32.00

Range T2 0.00

Range T1 4.00

Range T2 4.00

Range T1 30.00

Range T2 30.00

Range T1 17.00

Range T2 17.00

Range T1 26.00

Range T2 26.00

Range T1 8.00

T2 Hectares 0.00

Range T3 8.00


Range T2 1.00



Ensure the populations of the striped lychnis are maintained on all extant sites.




Ensure the populations of the black veined moth are maintained on all extant sites.




Ensure the populations of the barred tooth-stripe are maintained on all extant sites within its known range. Emphasis should be on maintaining populations within current stronghold areas.




Ensure the populations of the four-spotted moth are maintained on all extant sites within its known range. Emphasis should be on maintaining populations within current stronghold areas.




Ensure the populations of the sword grass are maintained on all extant sites within its known range. Emphasis should be on maintaining populations within current stronghold areas.




Ensure the populations of the slender Scotch burnet are maintained on all extant sites.


New target type

Increase the amount of potentially suitable habitat by 0.25ha by 2010.Maintain and seek to enhance current metapopulation links between colonies by 2010.


Population Size

Achieve an increase in population size to 1,500 individuals by 2010Maintain the current range of this species in Scotland.


Range T3 1.00

Range T1 3.00


Range T2 9.00

Range T3 4.00


Range T2 1.00

Range T1 8.00

T2 3.00

Range T1 53.00

Range T2 0.00

T3 9.00

Range T1 10.00

T1 4.00

Range T2 4.00

Range T1 10.00

T2 4.00



Maintain populations at all known sites and any new sites found to support populations.


Increase the overall range of the fen raft spider at Redgrave & Lopham Fen to 13 Ha of habitat occupied 3 years in 5 by 2010 and to 65 Ha by 2020.

There should be no overall decrease in occupied range of fen raft spider at Pevensey Levels from that recorded in 1990 at any time.


The number of sites with sustainable populations of fen raft spider should be increased by six by 2010. By 2020 the total number of sites with sustainable populations should be increased to 12.


Population Size

Enhance the population size at the known site (Wareham Forest) by 2010.

Restore populations to two suitable sites within the historic range by 2010.


Maintain populations of this species at 8 extant sites.


Population Size

Establish viable populations at 4 extant sites by 2010.


Maintain viable populations in 53 10km squares.


Re-establish populations of Chara curta in two priority areas in East Anglia and Wales through habitat restoration by 2010.


Population Size

Maintain nine strategic extant stronghold populations.


Maintain viable populations of this species in 10 extant sites.


Population Size



Re-establish populations of Nitella tenuissima at three historic sites through habitat restoration by 2010, taking the total number of sites to seven.


Maintain populations of this species in 10 extant sites.


Population Size



T3 0.00

Range T4 0.00

T1 2.00

T2 2.00

Range T3 5.00

Range T1 4.00

T2 2.00

T3 2.00

Range T1 89.00

Population Size

Establish and maintain 1 new metapopulation (outside the Norfolk Broads) by 2010.


Re-establish populations of Nitellopsis obtusa at one historic site through habitat restoration by 2010.


Population Size

Maintain 2 extant metapopulations of this species.


Population Size

Increase population from 2 to 3 metapopulations by 2010.


Maintain viable populations at 5 extant sites outside existing metapopulations.


Maintain viable populations of this species at 4 extant sites.


Population Size

Maintain 2 extant metapopulations of this species.


Population Size

Increase population from 2 to 3 metapopulations by 2010.


Maintain populations of medicinal leech at no less than 89 sites across the current geographical range in the UK.


2005 baseline 2010 targetE NI S W UK E NI S

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

0.00 0.00 4.00 0.00 4.00 0.00 0.00 4.00

6.00 0.00 0.00 2.00 8.00 6.00 0.00 0.00

5.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

3.00 0.00 0.00 2.00 5.00 3.00 0.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

5.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

2.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

1.00 2.00 3.00 0.00 6.00 1.00 2.00 3.00

41.00 0.00 259.00 0.00 300.00 41.00 0.00 259.00

41.00 0.00 12.00 0.00 53.00 41.00 0.00 12.00

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

0.00 0.00 1.00 0.00 1.00 0.00 0.00 1.00

1.00 0.00 0.00 4.00 5.00 1.00 0.00 0.00

0.00 0.00 9.00 0.00 9.00 0.00 0.00 9.00

0.00 0.00 0.00 1.00 1.00 0.00 0.00 0.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

22.00 0.00 0.00 0.00 22.00 22.00 0.00 0.00

2.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

0.04 0.00 0.00 0.00 0.06 0.06 0.00 0.00

2.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 0.00 tbc 0.00

0.00 0.00 2.00 11.00 13.00 0.00 0.00 2.00

0.00 0.00 2.00 11.00 14.00 0.00 0.00 2.00

4.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

0.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

4.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

7.00 0.00 0.00 0.00 7.00 7.00 0.00 0.00

5.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

0.00

0.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

5.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

0.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

5.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

3.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

3.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

0.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

1.00 0.00 1.00 0.00 2.00 1.00 0.00 1.00

1.00 0.00 1.00 0.00 4.00 2.00 0.00 2.00

0.00 0.00 0.00 0.00 2.00 1.00 0.00 1.00

834.00 0.00 0.00 0.00 834.00 834.0 0.00 0.00

834.00 0.00 0.00 0.00 842.00 842.0 0.00 0.00

6.00 0.00 0.00 0.00 6.00 6.00 0.00 0.00

20.00 0.00 0.00 0.00 20.00 20.00 0.00 0.00

20.00 0.00 0.00 0.00 25.00 25.00 0.00 0.00

6.00 0.00 0.00 4.00 10.00 6.00 0.00 0.00

6.00 0.00 0.00 4.00 11.00 7.00 0.00 0.00

6.00 0.00 0.00 0.00 6.00 6.00 0.00 0.00

6.00 0.00 0.00 0.00 6.00 6.00 0.00 0.00

2.00 0.00 0.00 5.00 7.00 2.00 0.00 0.00

2.00 0.00 1.00 4.00 7.00 2.00 0.00 1.00

6.00 0.00 1.00 16.00 23.00 6.00 0.00 1.00

6.00 0.00 1.00 16.00 28.00 11.00 0.00 1.00

0.00 0.00 0.00 2.00 2.00 0.00 0.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

149.00 0.00 0.00 1.00 150.00 149.00 0.00 0.00

6.00 0.00 0.00 0.00 6.00 6.00 0.00 0.00

0.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

0.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

3.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

0.10 0.00 0.00 0.00 0.15 0.15 0.00 0.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

1.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

5.00 0.00 4.00 8.00 17.00 5.00 0.00 4.00

3.00 0.00 0.00 0.00 5.00 4.00 1.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

0.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

2.00 0.00 0.00 1.00 3.00 2.00 0.00 0.00

0.35 0.00 0.00 0.00 0.39 0.39 0.00 0.00

2.00 0.00 0.00 1.00 4.00 3.00 0.00 0.00

7.00 0.00 0.00 0.00 15.00 15.00 0.00 0.00

100.00 100.00 100.00 100.00 100.00 100.00 100.00 100.00

100.00 100.00 100.00 100.00 100.00 100.00 100.00 100.00

46.00 0.00 0.00 0.00 60.00 58.00 0.00 0.00

28.00 0.00 0.00 0.00 32.00 31.00 0.00 0.00

12.00 0.00 0.00 0.00 24.00 22.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 0.00 0.00 0.00

290.00 0.00 0.00 0.00 300.00 300.00 0.00 0.00

45.00 0.00 0.00 0.00 49.00 49.00 0.00 0.00

103.00 0.00 0.00 0.00 120.00 120.00 0.00 0.00

0.60 0.00 0.00 0.00 0.70 0.70 0.00 0.00

3,821.00 0.00 24.00 244.00 4,089.00 3,821.00 0.00 24.00

225.00 0.00 6.00 41.00 272.00 225.00 0.00 6.00

225.00 0.00 6.00 41.00 290.00 235.00 1.00 8.00

100.00 0.00 100.00 100.00 115.00 115.00 Establish 115.00

100.00 100.00 100.00 100.00 100.00 100.00 100.00 100.00

1.00 5.00 0.00 0.00 22.00 15.00 7.00 0.00

1.00 1.00 0.00 0.00 3.00 2.00 1.00 0.00

0.00 0.00 79.00 0.00 79.00 0.00 0.00 79.00

800.00 0.00 0.00 0.00 1,050.00 1,050.00 0.00 0.00

124.00 0.00 0.00 0.00 140.00 140.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

100.00 0.00 100.00 0.00 115.00 115.00 Establish 115.00

100.00 100.00 100.00 0.00 110.00 110.00 110.00 110.00

0.00 0.00 0.00 0.00 1.00 0.00 0.00 1.00

0.00 0.00 0.00 0.00 1.00 0.00 0.00 1.00

0.00 0.00 83.00 0.00 90.00 0.00 0.00 90.00

0.00 0.00 n/av/ 0.00 0.00 0.00 0.00 tbc

1,500.00 0.00 0.00 0.00 1,500.00 1,500.00 0.00 0.00

90.00 0.00 0.00 0.00 90.00 90.00 0.00 0.00

90.00 0.00 0.00 0.00 108.00 105.00 0.00 0.00

0.00 0.00 95.00 0.00 100.00 0.00 0.00 100.00

0.00 0.00 23.00 0.00 23.00 0.00 0.00 23.00

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

4.00 1.00 6.00 3.00 14.00 4.00 1.00 6.00

4.00 1.00 6.00 3.00 14.00 4.00 1.00 6.00

9,000.00 3,000.00 13,000.00 25,000.00 50,000.00 9,000.00 3,000.00 13,000.00

100.00 0.00 0.00 0.00 Trend stable or Trend stable or 0.00 Establish bas

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

100.00 0.00 0.00 0.00 0.00 100.00 0.00 Establish bas

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

100.00 0.00 0.00 0.00 Trend 0/ +ve Trend 0/ +ve Establish Establish bas

100.00 0.00 0.00 100.00 100.00 100.00 Establish Establish bas



55,000.00 0.00 9,000.00 1,000.00 90,000.00 76,000.00 0.00 12,500.00

1,100.00 0.00 300.00 50.00 1,450.00 1,100.00 0.00 300.00

0.00 0.00 33.00 0.00 35.00 0.00 0.00 35.00

0.00 0.00 10.00 0.00 10.00 0.00 0.00 10.00

0.00 0.00 26.00 0.00 26.00 0.00 0.00 26.00

Trend -ve 0.00 0.00 100.00 0.00 Trend 0/ +ve Establish Establish bas

100.00 100.00 100.00 100.00 100.00 100.00 100.00 100.00

70.00 15.00 8.00 2.00 130.00 100.00 20.00 8.00

0.98 0.57 1.00 0.00 1.20 1.20 1.20 1.20

Trend -ve 0.00 0.00 0.00 Trend stable or Trend stable or 0.00 0.00

0.00 0.00 0.00 6.00 0.00 0.00 0.00 0.00

Trend -ve 0.00 0.00 0.00 Trend 0/ +ve Trend 0/ +ve 0.00 0.00

0.00 0.00 0.00 1.00 0.00 0.00 0.00 0.00

895.00 0.00 3,250.00 243.00 4,520.00 1,000.00 0.00 3,250.00

43.00 0.00 230.00 22.00 300.00 48.00 0.00 230.00

0.00 0.00 1,980.00 0.00 5,000.00 0.00 0.00 5,000.00

0.00 0.00 40.00 0.00 45.00 0.00 0.00 45.00

100.00 100.00 100.00 100.00 115.00 115.00 115.00 115.00

100.00 100.00 100.00 100.00 100.00 100.00 100.00 100.00

6.00 0.00 0.00 0.00 6.00 6.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

0.00 0.00 28.00 0.00 28.00 0.00 0.00 28.00

0.00 0.00 1.00 0.00 1.00 0.00 0.00 1.00

4.00 0.00 18.00 0.00 22.00 4.00 0.00 18.00

0.00 0.00 0.00 1.00 1.00 0.00 0.00 0.00

0.00 0.00 0.00 1.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00 1.00 1.00 0.00 0.00 0.00

0.00 0.00 7.00 0.00 7.00 0.00 0.00 7.00

4.00 0.00 5.00 3.00 12.00 4.00 0.00 5.00

0.00 0.00 0.00 0.00 2.00 1.00 0.00 1.00

0.00 0.00 7.00 0.00 7.00 0.00 0.00 7.00

31.00 0.00 0.00 0.00 28.00 28.00 0.00 0.00

0.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

6.00 0.00 0.00 5.00 11.00 6.00 0.00 0.00

5.00 0.00 0.00 2.00 7.00 5.00 0.00 0.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

16.00 0.00 0.00 1.00 17.00 16.00 0.00 0.00

2.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

3.00 0.00 2.00 10.00 15.00 3.00 0.00 2.00

0.00 0.00 1.00 0.00 1.00 0.00 0.00 1.00

5.00 0.00 2.00 0.00 7.00 5.00 0.00 2.00

1.00 0.00 2.00 0.00 3.00 1.00 0.00 2.00

1.00 0.00 2.00 0.00 3.00 1.00 0.00 2.00

5.00 0.00 3.00 0.00 8.00 5.00 0.00 3.00

8.00 0.00 0.00 0.00 8.00 8.00 0.00 0.00

8.00 0.00 0.00 0.00 9.00 9.00 0.00 0.00

11.00 0.00 0.00 0.00 11.00 11.00 0.00 0.00

11.00 0.00 0.00 0.00 12.00 12.00 0.00 0.00

7.00 1.00 1.00 0.00 9.00 7.00 1.00 1.00

7.00 1.00 1.00 0.00 10.00 8.00 1.00 1.00

0.00 0.00 8.00 0.00 8.00 0.00 0.00 8.00

0.00 0.00 0.00 0.00 8.00 0.00 0.00 8.00

8.00 0.00 0.00 0.00 8.00 8.00 0.00 0.00

14.00 0.00 1.00 6.00 21.00 14.00 0.00 1.00

0.00 0.00 0.00 0.00 2.00 1.00 0.00 0.00

11.00 1.00 1.00 14.00 27.00 11.00 1.00 1.00

0.00 0.00 0.00 0.00 4.00 2.00 0.00 0.00

0.00 0.00 2.00 0.00 2.00 0.00 0.00 2.00

2.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

0.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

9.00 0.00 1.00 13.00 23.00 9.00 0.00 1.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

0.00 0.00 0.00 4.00 4.00 0.00 0.00 0.00

0.00 0.00 0.00 4.00 4.00 0.00 0.00 0.00

1.00 0.00 1.00 0.00 2.00 1.00 0.00 1.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

4.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

12.00 0.00 0.00 0.00 12.00 12.00 0.00 0.00

2.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

0.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

8.00 4.00 0.00 4.00 16.00 8.00 4.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

10.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

3.00 0.00 0.00 0.00 6.00 6.00 0.00 0.00

19.00 0.00 0.00 1.00 25.00 24.00 0.00 0.00

45.00 0.00 0.00 2.00 47.00 45.00 0.00 0.00

17.00 0.00 0.00 2.00 19.00 17.00 0.00 0.00

45.00 0.00 0.00 2.00 59.00 55.00 0.00 0.00

101.00 0.00 79.00 14.00 194.00 101.00 0.00 79.00

19.00 0.00 7.00 3.00 29.00 19.00 0.00 7.00

47.00 0.00 42.00 5.00 104.00 52.00 0.00 45.00

0.00 0.00 27.00 0.00 27.00 0.00 0.00 27.00

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

139.00 22.00 45.00 74.00 280.00 139.00 22.00 45.00

171.00 0.00 97.00 47.00 373.00 205.00 0.00 107.00

37.00 0.00 0.00 0.00 43.00 43.00 0.00 0.00

10.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

0.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

25.00 0.00 0.00 0.00 25.00 25.00 0.00 0.00

20.00 0.00 0.00 0.00 30.00 30.00 0.00 0.00

10.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

0.00 0.00 0.00 0.00 7.00 7.00 0.00 0.00

4.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

67.00 0.00 0.00 8.00 75.00 67.00 0.00 0.00

339.00 0.00 0.00 38.00 389.00 349.00 0.00 0.00

95.00 0.00 0.00 0.00 114.00 114.00 0.00 0.00

5.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

700.00 0.00 0.00 0.00 1,000.00 1,000.00 0.00 0.00

2.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

6.00 0.00 0.00 0.00 9.00 9.00 0.00 0.00

2.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

12.00 0.00 0.00 0.00 12.00 12.00 0.00 0.00

194.00 23.00 2.00 22.00 241.00 194.00 23.00 2.00

194.00 23.00 2.00 22.00 253.00 204.00 24.00 2.00

14.00 4.00 0.00 1.00 19.00 14.00 4.00 0.00

16.00 0.00 0.00 7.00 23.00 16.00 0.00 0.00

62.00 0.00 0.00 22.00 99.00 74.00 0.00 0.00

16.00 0.00 0.00 5.00 24.00 18.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

1.00 0.00 0.00 0.00 0.00 1.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 tbc 0.00 tbc

tbc 0.00 tbc tbc 0.00 tbc 0.00 tbc

0.00 0.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 tbc 0.00 tbc

2.00 0.00 1.00 0.00 3.00 2.00 0.00 1.00

0.00 0.00 1.00 0.00 2.00 0.00 0.00 2.00

2.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

112.00 0.00 0.00 29.00 141.00 112.00 0.00 0.00

40.00 0.00 0.00 20.00 60.00 40.00 0.00 0.00

0.00 0.00 2.00 0.00 2.00 0.00 0.00 2.00

0.00 0.00 2.00 0.00 3.00 0.00 0.00 3.00

0.00 0.00 2.00 0.00 2.00 0.00 0.00 2.00

36.00 0.00 0.00 0.00 36.00 36.00 0.00 0.00

1.00 0.00 28.00 1.00 30.00 1.00 0.00 28.00

8.00 0.00 0.00 7.00 15.00 8.00 0.00 0.00

12.00 0.00 1.00 0.00 13.00 12.00 0.00 1.00

16.00 0.00 0.00 0.00 16.00 16.00 0.00 0.00

0.00 0.00 12.00 0.00 12.00 0.00 0.00 12.00

0.00 0.00 0.00 0.00 5.00 0.00 0.00 5.00

0.00 0.00 0.00 0.00 12.00 0.00 0.00 12.00

0.00 0.00 6.00 0.00 6.00 0.00 0.00 6.00

29.00 0.00 0.00 24.00 53.00 29.00 0.00 0.00

60.00 0.00 0.00 30.00 90.00 60.00 0.00 0.00

7.00 0.00 0.00 0.00 7.00 7.00 0.00 0.00

21.00 0.00 0.00 0.00 28.00 28.00 0.00 0.00

1.00 0.00 0.00 1.00 2.00 1.00 0.00 0.00

1.00 0.00 0.00 1.00 5.00 2.00 0.00 0.00

9.00 0.00 13.00 5.00 27.00 9.00 0.00 13.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

1.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

5.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

5.00 0.00 0.00 0.00 6.00 6.00 0.00 0.00

26.00 0.00 0.00 0.00 26.00 26.00 0.00 0.00

0.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

2.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

23.00 0.00 0.00 5.00 28.00 23.00 0.00 0.00

15.00 0.00 0.00 3.00 28.00 23.00 0.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

11.00 0.00 0.00 0.00 11.00 11.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

71.00 0.00 7.00 3.00 81.00 71.00 0.00 7.00

630.00 0.00 0.00 140.00 1,540.00 1,260.00 0.00 0.00

0.00 0.00 55.00 0.00 55.00 0.00 0.00 55.00

0.00 0.00 55.00 0.00 55.00 0.00 0.00 55.00

29.00 0.00 0.00 0.00 29.00 29.00 0.00 0.00

2.40 0.00 0.00 0.00 2.40 2.40 0.00 0.00

1,200.00 0.00 0.00 0.00 1,200.00 1,200.00 0.00 0.00

400.00 0.00 0.00 0.00 400.00 400.00 0.00 0.00

0.00 0.00 0.00 1.00 1.00 0.00 0.00 0.00

0.00 0.00 0.00 6.00 20.00 0.00 0.00 0.00

0.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

9.00 0.00 0.00 0.00 9.00 9.00 0.00 0.00

9.00 0.00 0.00 0.00 11.00 11.00 0.00 0.00

31.00 0.00 0.00 4.00 35.00 31.00 0.00 0.00

31.00 0.00 0.00 4.00 38.00 32.00 0.00 0.00

1.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

6.00 0.00 7.00 0.00 13.00 6.00 0.00 7.00

21.00 0.00 0.00 0.00 21.00 21.00 0.00 0.00

0.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

1.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

10.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

0.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

28.00 5.00 38.00 2.00 73.00 28.00 5.00 38.00

4.00 1.00 4.00 1.00 10.00 4.00 1.00 4.00

75.00 0.00 0.00 2.00 77.00 75.00 0.00 0.00

880.00 0.00 0.00 0.00 1,770.00 1,770.00 0.00 0.00

2.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

0.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

19.00 0.00 0.00 2.00 21.00 19.00 0.00 0.00

0.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

102.00 0.00 0.00 0.00 102.00 102.00 0.00 0.00

0.00 0.00 0.00 4.00 4.00 0.00 0.00 0.00

0.00 0.00 0.00 4.00 5.00 0.00 0.00 0.00

0.00 0.00 11.00 0.00 14.00 0.00 0.00 14.00

161.00 15.00 123.00 101.00 400.00 161.00 15.00 123.00

0.00 0.00 0.00 0.00 2.00 0.00 0.00 2.00

7.00 0.00 0.00 4.00 22.00 14.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 0.00 0.00 1.00

0.00 0.00 77.00 0.00 77.00 0.00 0.00 7.00

0.00 0.00 0.00 0.00 1.00 0.00 0.00 1.00

0.00 0.00 9.00 0.00 9.00 0.00 0.00 9.00

3.00 0.00 0.00 4.00 7.00 3.00 0.00 0.00

3.00 0.00 0.00 4.00 7.00 3.00 0.00 0.00

3.00 0.00 0.00 4.00 11.00 6.00 0.00 0.00

17.00 0.00 0.00 33.00 40.00 17.00 0.00 0.00

0.00 0.00 0.00 0.00 2.00 1.00 0.00 0.00

34.00 1.00 22.00 5.00 62.00 34.00 1.00 22.00

18.00 1.00 0.00 6.00 25.00 18.00 1.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

0.00 3.00 19.00 0.00 22.00 0.00 3.00 19.00

0.00 3.00 19.00 0.00 27.00 0.00 3.00 24.00

0.00 0.00 0.00 0.00 5.00 0.00 0.00 5.00

16.00 1.00 0.00 1.00 18.00 16.00 1.00 0.00

0.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

0.00 0.00 40.00 0.00 40.00 0.00 0.00 40.00

0.00 0.00 40.00 0.00 40.00 0.00 0.00 40.00

7.00 0.00 0.00 0.00 7.00 7.00 0.00 0.00

7.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

39.00 0.00 29.00 23.00 91.00 39.00 0.00 29.00

4.00 0.00 2.00 1.00 7.00 4.00 0.00 2.00

0.00 0.00 0.00 0.00 2.00 1.00 0.00 1.00

21.00 0.00 1.00 6.00 28.00 21.00 0.00 1.00

11.00 0.00 1.00 1.00 13.00 11.00 0.00 1.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

0.00 0.00 11.00 0.00 11.00 0.00 0.00 11.00

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

15.00 0.00 0.00 12.00 27.00 15.00 0.00 0.00

18.00 0.00 0.00 0.00 18.00 18.00 0.00 0.00

0.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

0.00 0.00 0.00 0.00 5.00 4.00 0.00 0.00

29.00 0.00 0.00 3.00 32.00 29.00 0.00 0.00

0.00 0.00 1,800.00 0.00 2,000.00 0.00 0.00 2,000.00

0.00 0.00 2.00 0.00 2.00 0.00 0.00 2.00

0.00 0.00 2.00 0.00 2.00 0.00 0.00 2.00

164.00 0.00 0.00 2.00 166.00 164.00 0.00 0.00

790.00 0.00 0.00 140.00 1,850.00 1,570.00 0.00 0.00

65.00 0.00 3.00 19.00 87.00 65.00 0.00 3.00

215.00 0.00 0.00 140.00 710.00 430.00 0.00 0.00

62.00 2.00 0.00 0.00 64.00 62.00 2.00 0.00

0.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

1.00 9.00 66.00 0.00 76.00 1.00 9.00 66.00

16.00 0.00 0.00 0.00 16.00 16.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

77.00 0.00 0.00 0.00 77.00 0.00 0.00 0.00

360.00 0.00 0.00 0.00 720.00 720.00 0.00 0.00

19.00 0.00 0.00 1.00 20.00 19.00 0.00 0.00

590.00 0.00 0.00 140.00 1,450.00 1,170.00 0.00 0.00

1.00 0.00 3.00 2.00 6.00 1.00 0.00 3.00

0.00 0.00 1.00 0.00 2.00 0.00 0.00 2.00

1.00 1.00 1.00 1.00 4.00 1.00 1.00 1.00

0.00 0.00 0.00 0.00 0.00 tbc tbc tbc

16.00 0.00 0.00 0.00 16.00 0.00 0.00 0.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

33.00 0.00 0.00 0.00 33.00 33.00 0.00 0.00

1.00 0.00 20.00 0.00 21.00 1.00 0.00 20.00

0.00 1.00 6.00 0.00 7.00 0.00 1.00 6.00

0.00 0.00 11.00 0.00 11.00 0.00 0.00 11.00

38.00 1.00 7.00 1.00 47.00 38.00 1.00 7.00

3.00 0.00 12.00 0.00 15.00 3.00 0.00 12.00

0.00 0.00 23.00 0.00 23.00 0.00 0.00 23.00

21.00 0.00 6.00 1.00 28.00 21.00 0.00 6.00

24.00 1.00 2.00 1.00 28.00 24.00 1.00 2.00

16.00 0.00 4.00 2.00 22.00 16.00 0.00 4.00

22.00 0.00 7.00 1.00 30.00 22.00 0.00 7.00

5.00 0.00 15.00 1.00 21.00 5.00 0.00 15.00

0.00 0.00 5.00 0.00 5.00 0.00 0.00 5.00

14.00 0.00 29.00 0.00 43.00 14.00 0.00 29.00

8.00 0.00 5.00 0.00 13.00 8.00 0.00 5.00

41.00 0.00 0.00 1.00 42.00 41.00 0.00 0.00

126.00 21.00 89.00 84.00 320.00 126.00 21.00 89.00

7.00 0.00 6.00 10.00 23.00 7.00 0.00 6.00

3.00 0.00 11.00 0.00 14.00 3.00 0.00 11.00

23.00 6.00 13.00 27.00 69.00 23.00 6.00 13.00

29.00 0.00 1.00 0.00 30.00 29.00 0.00 1.00

4.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

0.00 0.00 3.00 0.00 3.00 0.00 0.00 3.00

2,150.00 0.00 200.00 150.00 3,500.00 2,800.00 0.00 350.00

22.00 0.00 3.00 2.00 28.00 23.00 0.00 3.00

14.00 0.00 2.00 1.00 21.00 17.00 0.00 2.00

11.00 0.00 1.00 2.00 18.00 13.00 0.00 1.00

379.00 0.00 1.00 4.00 388.00 381.00 0.00 1.00

1,000.00 0.00 2.00 17.00 1,252.00 1,200.00 0.00 2.00

0.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

0.00 0.00 0.00 0.00 50.00 50.00 0.00 0.00

0.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

796.00 0.00 51.00 57.00 926.00 813.00 0.00 54.00

58.00 0.00 21.00 9.00 89.00 58.00 0.00 22.00

88,000.00 0.00 6,000.00 6,000.00 120,000.00 105,600.00 0.00 7,200.00

52,800.00 0.00 3,600.00 3,600.00 72,000.00 63,360.00 0.00 4,320.00

0.00 0.00 21.00 0.00 21.00 0.00 0.00 21.00

25.00 0.00 4.00 1.00 30.00 25.00 0.00 4.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

0.00 0.00 1.00 1.00 2.00 0.00 0.00 1.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

2.00 0.00 1.00 0.00 3.00 2.00 0.00 1.00

2.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

0.00 0.00 0.00 1.00 1.00 0.00 0.00 0.00

0.00 0.00 0.00 1.00 1.00 0.00 0.00 0.00

0.00 0.00 7.00 0.00 7.00 0.00 0.00 7.00

7.00 0.00 0.00 0.00 7.00 7.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

0.00 0.00 0.00 3.00 3.00 0.00 0.00 0.00

1.00 1.00 0.00 0.00 2.00 1.00 1.00 0.00

12.00 0.00 0.00 0.00 12.00 12.00 0.00 0.00

11.00 0.00 0.00 4.00 15.00 11.00 0.00 0.00

15.00 0.00 0.00 7.00 22.00 15.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

28.00 0.00 0.00 0.00 28.00 28.00 0.00 0.00

0.00 0.00 1.00 0.00 1.00 0.00 0.00 1.00

2.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

0.00 0.00 1.00 0.00 1.00 0.00 0.00 1.00

0.00 0.00 1.00 0.00 1.00 0.00 0.00 1.00

582.00 0.00 79.00 69.00 730.00 582.00 0.00 79.00

582.00 0.00 79.00 69.00 780.00 605.00 0.00 95.00

82.00 0.00 0.00 4.00 86.00 82.00 0.00 0.00

1,022.00 0.00 412.00 170.00 1,604.00 1,022.00 0.00 412.00

150.00 0.00 150.00 150.00 200.00 200.00 0.00 200.00

878.00 148.00 988.00 205.00 2,219.00 878.00 148.00 988.00

878.00 148.00 988.00 205.00 2,377.00 997.00 156.00 1,003.00

327.00 0.00 0.00 62.00 376.00 327.00 0.00 0.00

11.00 0.00 0.00 0.00 16.00 16.00 0.00 0.00

Trend -ve 0.00 0.00 Trend -ve Trend 0/ +ve Trend 0/ +ve 0.00 0.00

44.00 0.00 0.00 0.00 44.00 44.00 0.00 0.00

100.0

100.0

110.0

110.0

68.00 0.00 0.00 11.00 79.00 68.00 0.00 0.00

68.00 0.00 0.00 11.00 83.00 72.00 0.00 0.00

100.00 0.00 0.00 100.00 110.00 110.00 0.00 0.00

225.00 0.00 0.00 83.00 308.00 225.00 0.00 0.00

108.00

172.00 111.00 300.00 20.00 603.00 172.00 111.00 300.00

6.00 0.00 0.00 0.00 6.00 6.00 0.00 0.00

0.00 2.00 130.00 0.00 132.00 0.00 2.00 130.00

1.00 0.00 2.00 0.00 3.00 1.00 0.00 2.00

5.00 0.00 2.00 0.00 7.00 5.00 0.00 2.00

16.00 0.00 0.00 2.00 18.00 16.00 0.00 0.00

0.00

7.00 0.00 0.00 0.00 7.00 7.00 0.00 0.00

2.00 0.00 0.00 0.00 2.00 0.00 0.00 0.00

3.00 0.00 62.00 1.00 66.00 3.00 0.00 62.00

3.00 0.00 62.00 1.00 68.00 5.00 0.00 62.00

0.00 0.00 0.00 0.00 2.00 0.00 0.00 2.00

0.00 0.00 2.00 0.00 6.00 0.00 2.00 4.00

0.00 0.00 0.00 1.00 1.00 0.00 0.00 0.00

29.00 0.00 0.00 0.00 29.00 29.00 0.00 0.00

4.00 0.00 0.00 1.00 5.00 4.00 0.00 0.00

14.00 0.00 0.00 0.00 14.00 14.00 0.00 0.00

27.00 0.00 0.00 0.00 27.00 27.00 0.00 0.00

43.00 3.00 3.00 3.00 52.00 43.00 3.00 3.00

11.00 0.00 11.00 0.00 22.00 11.00 0.00 11.00

11.00 10.00 33.00 5.00 59.00 11.00 10.00 33.00

52.00 0.00 0.00 2.00 54.00 52.00 0.00 0.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

1.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

11.00 0.00 0.00 0.00 11.00 11.00 0.00 0.00

11.00 0.00 0.00 0.00 14.00 14.00 0.00 0.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

1.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

8.00 0.00 0.00 0.00 8.00 8.00 0.00 0.00

7.00 0.00 0.00 0.00 7.00 7.00 0.00 0.00

10.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

10.00 0.00 0.00 0.00 12.00 12.00 0.00 0.00

2.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

2.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

9.00 0.00 0.00 0.00 9.00 9.00 0.00 0.00

9.00 0.00 0.00 0.00 11.00 11.00 0.00 0.00

31.00 0.00 0.00 0.00 31.00 31.00 0.00 0.00

13.00 0.00 0.00 0.00 15.00 15.00 0.00 0.00

6.00 0.00 0.00 0.00 6.00 6.00 0.00 0.00

1.00 0.00 3.00 0.00 4.00 1.00 0.00 3.00

1.00 0.00 3.00 0.00 6.00 2.00 0.00 4.00

0.00 0.00 0.00 0.00 10.50 10.00 0.00 0.50

20.00 0.00 0.00 0.00 20.00 20.00 0.00 0.00

6.00 0.00 0.00 0.00 7.00 7.00 0.00 0.00

0.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

30.00 4.00 13.00 6.00 53.00 30.00 4.00 13.00

30.00 4.00 13.00 6.00 57.00 31.00 5.00 14.00

1.00 0.00 0.00 2.00 3.00 1.00 0.00 0.00

0.00 0.00 0.00 0.00 0.75 0.25 0.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

3.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

2.00 0.00 0.00 1.00 3.00 2.00 0.00 0.00

0.00 0.00 0.00 0.00 0.20 0.10 0.00 0.00

0.00 0.00 20.00 0.00 20.00 0.00 0.00 20.00

0.00 0.00 20.00 0.00 24.00 0.00 0.00 24.00

32.00 0.00 1.00 0.00 33.00 32.00 0.00 1.00

32.00 0.00 1.00 0.00 36.00 32.00 0.00 3.00

1.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

9.00 0.00 0.00 0.00 9.00 9.00 0.00 0.00

0.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

9.00 0.00 0.00 0.00 11.00 11.00 0.00 0.00

12.00 0.00 0.00 0.00 12.00 12.00 0.00 0.00

12.00 0.00 0.00 0.00 15.00 15.00 0.00 0.00

4.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

4.00 0.00 0.00 0.00 6.00 6.00 0.00 0.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

0.00 0.00 0.00 0.00 0.50 0.50 0.00 0.00

14.00 0.00 13.00 1.00 28.00 14.00 0.00 13.00

14.00 0.00 13.00 0.00 35.00 16.00 2.00 15.00

32.00 0.00 0.00 0.00 32.00 32.00 0.00 0.00

0.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

4.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

4.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

25.00 0.00 5.00 0.00 30.00 25.00 0.00 5.00

25.00 0.00 5.00 0.00 35.00 28.00 0.00 7.00

17.00 0.00 0.00 0.00 17.00 17.00 0.00 0.00

17.00 0.00 0.00 0.00 20.00 20.00 0.00 0.00

1.00 0.00 25.00 0.00 26.00 1.00 0.00 25.00

1.00 0.00 25.00 0.00 31.00 2.00 0.00 29.00

0.00 0.00 8.00 0.00 8.00 0.00 0.00 8.00

0.00 0.00 0.00 0.00 0.25 0.00 0.00 0.25

0.00 0.00 8.00 0.00 8.00 0.00 0.00 8.00

0.00 0.00 500.00 0.00 1,000.00 0.00 0.00 1,000.00

0.00 0.00 1.00 0.00 1.00 0.00 0.00 1.00

0.00 0.00 1.00 0.00 3.00 0.00 0.00 3.00

3.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

tbc 0.00 0.00 0.00 13.00 13.00 0.00 0.00

9.00 0.00 0.00 0.00 9.00 9.00 0.00 0.00

2.00 0.00 0.00 2.00 6.00 4.00 0.00 0.00

950.00 0.00 0.00 0.00 >1000 >1000 0.00 0.00

0.00 0.00 0.00 0.00 3.00 0.00 0.00 0.00

8.00 0.00 0.00 0.00 8.00 8.00 0.00 0.00

3.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

19.00 8.00 21.00 5.00 53.00 19.00 8.00 21.00

0.00 0.00 0.00 0.00 2.00 1.00 0.00 0.00

2.00 1.00 5.00 1.00 9.00 2.00 1.00 5.00

0.00 0.00 5.00 5.00 10.00 0.00 0.00 5.00

1.00 0.00 0.00 3.00 4.00 1.00 0.00 0.00

1.00 0.00 0.00 3.00 7.00 3.00 0.00 0.00

10.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

4.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

0.00 0.00 0.00 0.00 1.00 1.00 0.00 0.00

2.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

2.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

5.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

4.00 0.00 0.00 0.00 4.00 4.00 0.00 0.00

2.00 0.00 0.00 0.00 2.00 2.00 0.00 0.00

2.00 0.00 0.00 0.00 3.00 3.00 0.00 0.00

78.00 0.00 2.00 9.00 89.00 78.00 0.00 2.00

2010 target 2015 target 2020 targetW UK E NI S W UK

0.00 0.00 0.00

0.00 0.00 0.00

2.00 0.00 0.00

0.00 0.00 0.00

0.00 1.00 1.00 0.00 0.00 0.00 0.00

2.00 5.00 3.00 0.00 0.00 2.00 0.00

0.00 3.00 3.00 0.00 0.00 0.00 0.00

0.00 5.00 5.00 0.00 0.00 0.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

0.00 6.00 1.00 2.00 3.00 0.00 0.00

0.00 0.00 0.00

0.00 60.00 46.00 0.00 14.00 0.00 64.00

0.00 0.00 tbc 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

4.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 5.00 5.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

11.00 0.00 0.00

12.00 15.00 0.00 0.00 3.00 12.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00

0.00 5.00 5.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 6.00 3.00 0.00 3.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 850.00 850.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 30.00 30.00 0.00 0.00 0.00 0.00

4.00 0.00 0.00

4.00 12.00 7.00 0.00 0.00 5.00 0.00

0.00 0.00 0.00

0.00 7.00 7.00 0.00 0.00 0.00 0.00

5.00 0.00 0.00

4.00 0.00 0.00

16.00 0.00 0.00

16.00 0.00 0.00

2.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

0.00 0.00 0.00

0.00 5.00 5.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 6.00 5.00 0.00 1.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 3.00 3.00 0.00 0.00 0.00 5.00

8.00 0.00 0.00

0.00 6.00 4.00 2.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

0.00 0.42 0.42 0.00 0.00 0.00 0.00

1.00 5.00 4.00 0.00 0.00 1.00 6.00

0.00 20.00 20.00 0.00 0.00 0.00 25.00

100.00 115.00 115.00 115.00 115.00 100.00 130.00

100.00 100.00 100.00 100.00 100.00 100.00 100.00

2.00 80.00 74.00 0.00 1.00 5.00 110.00

1.00 37.00 34.00 0.00 1.00 2.00 44.00

2.00 40.00 34.00 0.00 1.00 5.00 66.00

1.00 2.00 0.00 0.00 0.00 2.00 4.00

0.00 350.00 350.00 0.00 0.00 0.00 400.00

0.00 54.00 54.00 0.00 0.00 0.00 64.00

0.00 150.00 150.00 0.00 0.00 0.00 0.00

0.00 0.70 0.70 0.00 0.00 0.00 0.00

244.00 4,800.00 4,465.00 10.00 50.00 275.00 0.00

41.00 0.00 0.00

46.00 311.00 246.00 2.00 12.00 51.00 0.00

100.00 130.00 130.00 115.00 130.00 100.00 150.00

100.00 100.00 100.00 100.00 100.00 100.00 100.00

0.00 40.00 30.00 10.00 0.00 0.00 65.00

0.00 4.00 2.00 2.00 0.00 0.00 5.00

0.00 0.00 0.00

0.00 1,300.00 1,300.00 0.00 0.00 0.00 1,550.00

0.00 156.00 156.00 0.00 0.00 0.00 172.00

0.00 2.00 2.00 0.00 0.00 0.00 3.00

Establish ba 130.00 130.00 115.00 130.00 100.00 150.00

Establish ba 120.00 120.00 120.00 120.00 100.00 130.00

0.00 2.00 1.00 0.00 1.00 0.00 0.00

0.00 2.00 1.00 0.00 1.00 0.00 0.00

0.00 100.00 0.00 0.00 100.00 0.00 110.00

0.00 0.00 0.00 0.00 tbc 0.00 0.00

0.00 2,150.00 2,120.00 0.00 0.00 30.00 0.00

0.00 0.00 0.00

3.00 125.00 120.00 0.00 0.00 5.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00 1.00 0.00 0.00 0.00

3.00 0.00 0.00

3.00 0.00 0.00

25,000.00 0.00 0.00

0.00 100.00 100.00 0.00 100.00 0.00 150.00

5.00 0.00 0.00 0.00 0.00 >5 0.00

0.00 110.00 110.00 0.00 110.00 0.00 120.00

2.00 0.00 0.00 0.00 0.00 >2 0.00

Establish ba 100.00 100.00 100.00 100.00 100.00 115.00

100.00 100.00 100.00 100.00 100.00 100.00 100.00

Establish ba 0.00 220.00 150.00 150.00 150.00 0.00

Establish ba 0.00 120.00 110.00 110.00 110.00 0.00

1,500.00 120,000.00 101,000.00 0.00 17,000.00 2,000.00 160,000.00

50.00 1,530.00 1,150.00 0.00 325.00 55.00 1,610.00

0.00 40.00 0.00 0.00 40.00 0.00 0.00

0.00 10.00 0.00 0.00 10.00 0.00 0.00

0.00 26.00 0.00 0.00 26.00 0.00 0.00

140.00 100.00 100.00 100.00 100.00 140.00 115.00

100.00 100.00 100.00 100.00 100.00 120.00 100.00

2.00 155.00 125.00 30.00 tbc tbc 180.00

1.20 1.20 1.20 1.20 1.20 1.20 1.20

0.00 100.00 100.00 0.00 0.00 0.00 115.00

>6.00 0.00 0.00 0.00 0.00 10.00 0.00

0.00 110.00 110.00 0.00 0.00 0.00 120.00

1.00 0.00 0.00 0.00 0.00 2.00 0.00

270.00 4,720.00 1,200.00 0.00 3,250.00 270.00 5,020.00

22.00 304.00 52.00 0.00 230.00 22.00 308.00

0.00 5,000.00 0.00 0.00 5,000.00 0.00 0.00

0.00 0.00 0.00 0.00 tbc 0.00 0.00

100.00 130.00 130.00 130.00 130.00 100.00 150.00

100.00 100.00 100.00 100.00 100.00 100.00 100.00

0.00 0.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

1.00 1.00 0.00 0.00 0.00 1.00 0.00

1.00 2.00 0.00 0.00 0.00 2.00 0.00

0.00 0.00 0.00

3.00 0.00 0.00

0.00 3.00 2.00 0.00 1.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 5.00 5.00 0.00 0.00 0.00 0.00

5.00 0.00 0.00

2.00 0.00 0.00

0.00 0.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

1.00 0.00 0.00

0.00 0.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

10.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 4.00 2.00 0.00 2.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 10.00 10.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 12.00 9.00 1.00 2.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

6.00 0.00 0.00

1.00 5.00 3.00 0.00 0.00 2.00 0.00

14.00 0.00 0.00

2.00 7.00 4.00 0.00 0.00 3.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

13.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

4.00 0.00 0.00

4.00 4.00 0.00 0.00 0.00 4.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

4.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 9.00 8.00 0.00 0.00 1.00 0.00

1.00 0.00 0.00

2.00 0.00 0.00

2.00 0.00 0.00

4.00 70.00 63.00 0.00 0.00 7.00 78.00

14.00 0.00 0.00

3.00 0.00 0.00

7.00 114.00 57.00 0.00 48.00 9.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 0.00 1.00

74.00 0.00 0.00

61.00 433.00 239.00 0.00 117.00 77.00 493.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 7.00 7.00 0.00 0.00 0.00 10.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 12.00 12.00 0.00 0.00 0.00 17.00

0.00 0.00 0.00

8.00 0.00 0.00

40.00 0.00 0.00

0.00 0.00 0.00

0.00 12.00 12.00 0.00 0.00 0.00 15.00

0.00 1,350.00 1,350.00 0.00 0.00 0.00 1,650.00

0.00 4.00 4.00 0.00 0.00 0.00 5.00

0.00 12.00 12.00 0.00 0.00 0.00 15.00

0.00 4.00 4.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

22.00 0.00 0.00

23.00 265.00 214.00 25.00 2.00 24.00 277.00

1.00 0.00 0.00

7.00 0.00 0.00

25.00 114.00 84.00 0.00 0.00 30.00 129.00

6.00 27.00 20.00 0.00 0.00 7.00 30.00

0.00 2.00 1.00 0.00 0.00 1.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 tbc 0.00 tb 0.00 0.00

tbc 0.00 0.00

0.00 0.00 0.00

0.00 0.00 tbc 0.00 tbc 0.00 0.00

0.00 0.00 0.00

0.00 3.00 0.00 0.00 3.00 0.00 4.00

0.00 3.00 3.00 0.00 0.00 0.00 4.00

29.00 0.00 0.00

20.00 0.00 0.00

0.00 2.00 0.00 0.00 2.00 0.00 0.00

0.00 5.00 0.00 0.00 5.00 0.00 8.00

0.00 2.00 0.00 0.00 2.00 0.00 2.00

0.00 0.00 0.00

1.00 0.00 0.00

7.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 12.00 0.00 0.00 12.00 0.00 0.00

0.00 5.00 0.00 0.00 5.00 0.00 5.00

0.00 12.00 0.00 0.00 12.00 0.00 12.00

0.00 0.00 0.00

24.00 0.00 0.00

30.00 0.00 0.00

0.00 0.00 0.00

0.00 35.00 35.00 0.00 0.00 0.00 0.00

1.00 0.00 0.00

3.00 0.00 0.00

5.00 0.00 0.00

0.00 1.00 1.00 0.00 0.00 0.00 0.00

0.00 6.00 6.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 7.00 7.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 5.00 0.00 0.00 0.00 0.00 0.00

0.00 6.00 0.00 0.00 0.00 0.00 0.00

5.00 28.00 23.00 0.00 0.00 5.00 0.00

5.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

3.00 0.00 0.00

280.00 1,920.00 1,570.00 0.00 0.00 350.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00 0.00 0.00 0.00 0.00

0.00 400.00 400.00 0.00 0.00 0.00 0.00

1.00 0.00 0.00

20.00 50.00 0.00 0.00 0.00 50.00 75.00

0.00 3.00 3.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 14.00 14.00 0.00 0.00 0.00 0.00

4.00 0.00 0.00

6.00 0.00 0.00

0.00 4.00 4.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

2.00 0.00 0.00

1.00 0.00 0.00

2.00 0.00 0.00

0.00 2,210.00 2,210.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

2.00 0.00 0.00

0.00 10.00 10.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

4.00 0.00 0.00

5.00 6.00 0.00 0.00 0.00 6.00 0.00

0.00 16.00 0.00 0.00 16.00 0.00 0.00

101.00 0.00 0.00

0.00 5.00 0.00 0.00 5.00 0.00 0.00

8.00 0.00 0.00

0.00 3.00 0.00 0.00 3.00 0.00 0.00

0.00 0.00 0.00

0.00 3.00 0.00 0.00 3.00 0.00 0.00

0.00 0.00 0.00

4.00 0.00 0.00

4.00 0.00 0.00

5.00 12.00 7.00 0.00 0.00 5.00 0.00

33.00 0.00 0.00

1.00 2.00 1.00 0.00 0.00 1.00 2.00

5.00 0.00 0.00

6.00 0.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

0.00 4.00 4.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 42.00 0.00 0.00 42.00 0.00 43.00

0.00 0.00 0.00

0.00 15.00 15.00 0.00 0.00 0.00 0.00

23.00 0.00 0.00

1.00 0.00 0.00

0.00 4.00 2.00 0.00 2.00 0.00 0.00

6.00 0.00 0.00

1.00 13.00 11.00 0.00 1.00 1.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 1.00 0.00 0.00 1.00 0.00 2.00

12.00 0.00 0.00

0.00 0.00 0.00

0.00 4.00 4.00 0.00 0.00 0.00 0.00

1.00 0.00 0.00

3.00 0.00 0.00

0.00 0.00 0.00

0.00 13.00 0.00 0.00 13.00 0.00 0.00

0.00 4.00 0.00 0.00 4.00 0.00 0.00

2.00 0.00 0.00

280.00 2,320.00 1,970.00 0.00 0.00 350.00 0.00

19.00 0.00 0.00

280.00 887.00 537.00 0.00 0.00 350.00 0.00

0.00 0.00 0.00

0.00 5.00 5.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 900.00 900.00 0.00 0.00 0.00 0.00

1.00 0.00 0.00

280.00 1,810.00 1,460.00 0.00 0.00 350.00 0.00

2.00 0.00 0.00

0.00 0.00 0.00

1.00 6.00 2.00 1.00 1.00 2.00 0.00

tbc 0.00 tbc tbc tbc tbc 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

1.00 0.00 0.00

2.00 0.00 0.00

1.00 0.00 0.00

1.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

84.00 0.00 0.00

10.00 0.00 0.00

0.00 0.00 0.00

27.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

350.00 8,000.00 6,600.00 0.00 700.00 700.00 12,500.00

2.00 30.00 24.00 0.00 3.00 3.00 35.00

2.00 23.00 18.00 0.00 2.00 3.00 24.00

4.00 22.00 15.00 0.00 1.00 6.00 24.00

6.00 392.00 383.00 0.00 1.00 8.00 394.00

50.00 1,500.00 1,398.00 0.00 2.00 100.00 2,000.00

0.00 5.00 5.00 0.00 0.00 0.00 10.00

0.00 125.00 125.00 0.00 0.00 0.00 250.00

0.00 3.00 3.00 0.00 0.00 0.00 4.00

59.00 952.00 833.00 0.00 58.00 61.00 976.00

9.00 90.00 58.00 0.00 23.00 9.00 91.00

7,200.00 140,000.00 123,200.00 0.00 8,400.00 8,400.00 160,000.00

4,320.00 84,000.00 73,920.00 0.00 5,040.00 5,040.00 96,000.00

0.00 0.00 0.00

1.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

1.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 2.00 2.00 0.00 0.00 0.00 0.00

3.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

4.00 0.00 0.00

7.00 0.00 0.00

0.00 3.00 2.00 0.00 0.00 1.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

69.00 0.00 0.00

80.00 835.00 635.00 0.00 110.00 90.00 895.00

4.00 0.00 0.00

170.00 0.00 0.00

200.00 200.00 200.00 0.00 200.00 200.00 0.00

205.00 0.00 0.00

221.00 2,500.00 1,084.00 161.00 1,024.00 231.00 0.00

62.00 0.00 0.00

0.00 21.00 21.00 0.00 0.00 0.00 0.00

Trend 0/ +v 100.00 0.00 0.00 0.00 100.00 115.00

0.00 0.00 0.00

100.0 100.0

100.0 100.0

122.0 135.0

122.0 135.0

11.00 0.00 0.00

11.00 86.00 75.00 0.00 0.00 11.00 91.00

110.00 115.00 115.00 0.00 0.00 115.00 125.00

83.00 327.00 233.00 0.00 0.00 94.00 347.00

116.00 125.00

20.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

2.00 0.00 0.00

0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00 0.00

1.00 74.00 7.00 1.00 64.00 2.00 0.00

0.00 5.00 0.00 0.00 4.00 1.00 0.00

0.00 12.00 2.00 3.00 6.00 1.00 0.00

1.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

3.00 0.00 0.00

0.00 0.00 0.00

5.00 0.00 0.00

2.00 0.00 0.00

0.00 0.00 0.00

0.00 4.00 4.00 0.00 0.00 0.00 5.00

0.00 0.00 0.00

0.00 17.00 17.00 0.00 0.00 0.00 20.00

0.00 0.00 0.00

0.00 4.00 4.00 0.00 0.00 0.00 5.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 5.00 5.00 0.00 0.00 0.00 6.00

0.00 0.00 0.00

0.00 13.00 13.00 0.00 0.00 0.00 15.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 8.00 3.00 0.00 5.00 0.00 10.00

0.00 0.00 15.00 0.00 1.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 7.00 7.00 0.00 0.00 0.00 10.00

0.00 0.00 0.00

6.00 0.00 0.00

7.00 59.00 32.00 5.00 14.00 8.00 63.00

2.00 0.00 0.00

0.50 1.50 0.50 0.00 0.00 1.00 0.00

0.00 0.00 0.00

0.00 5.00 5.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

1.00 0.00 0.00

0.10 0.40 0.20 0.00 0.00 0.20 0.80

0.00 0.00 0.00

0.00 26.00 0.00 0.00 26.00 0.00 28.00

0.00 0.00 0.00

1.00 41.00 32.00 0.00 6.00 3.00 43.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 6.00 6.00 0.00 0.00 0.00 9.00

0.00 12.00 12.00 0.00 0.00 0.00 14.00

0.00 0.00 0.00

0.00 17.00 17.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 8.00 8.00 0.00 0.00 0.00 10.00

0.00 0.00 0.00

0.00 1.00 1.00 0.00 0.00 0.00 0.00

1.00 0.00 0.00

2.00 38.00 17.00 2.00 16.00 3.00 40.00

0.00 0.00 0.00

0.00 8.00 8.00 0.00 0.00 0.00 10.00

0.00 0.00 0.00

0.00 6.00 6.00 0.00 0.00 0.00 8.00

0.00 0.00 0.00

0.00 38.00 30.00 0.00 8.00 0.00 40.00

0.00 0.00 0.00

0.00 21.00 21.00 0.00 0.00 0.00 22.00

0.00 0.00 0.00

0.00 33.00 3.00 0.00 30.00 0.00 36.00

0.00 0.00 0.00

0.00 0.50 0.00 0.00 0.50 0.00 0.00

0.00 0.00 0.00

0.00 1,500.00 0.00 0.00 1,500.00 0.00 0.00

0.00 0.00 0.00

0.00 5.00 0.00 0.00 5.00 0.00 0.00

0.00 0.00 0.00

0.00 30.00 40.00 0.00 0.00 0.00 65.00

0.00 0.00 0.00

2.00 8.00 5.00 0.00 0.00 3.00 12.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 6.00 6.00 0.00 0.00 0.00 0.00

5.00 0.00 0.00

1.00 4.00 2.00 0.00 0.00 2.00 0.00

1.00 9.00 2.00 1.00 5.00 1.00 0.00

5.00 0.00 0.00

3.00 0.00 0.00

4.00 8.00 4.00 0.00 0.00 4.00 9.00

0.00 0.00 0.00

0.00 8.00 8.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 4.00 4.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 0.00 0.00

0.00 4.00 4.00 0.00 0.00 0.00 0.00

9.00 0.00 0.00

2020 target 2030 target E NI S W UK E NI S

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

48.00 0.00 16.00 0.00 69.00 51.00 0.00 18.00

tbc 0.00 0.00 0.00 0.00 tbc 0.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

5.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

5.00 0.00 0.00 1.00 8.00 7.00 0.00 0.00

25.00 0.00 0.00 0.00 0.00

130.00 130.00 130.00 100.00 0.00

100.00 100.00 100.00 100.00 0.00

190.00

64.00

133.00

0.00 0.00 0.00 4.00 0.00

400.00 0.00 0.00 0.00 500.00 500.00 0.00 0.00

64.00 0.00 0.00 0.00 0.00

0.00

0.00

0.00

0.00

0.00

150.00 130.00 150.00 100.00 0.00

100.00 100.00 100.00 100.00 0.00

50.00 15.00 0.00 0.00 tbc tbc 20.00 0.00

3.00 2.00 0.00 0.00 tbc tbc 5.00 0.00

0.00

1,550.00 0.00 0.00 0.00 0.00

172.00 0.00 0.00 0.00 0.00

3.00 0.00 0.00 0.00 0.00

150.00 130.00 150.00 100.00 0.00

130.00 130.00 130.00 100.00 0.00

0.00

0.00

0.00 0.00 110.00 0.00 120.00 0.00 0.00 120.00

0.00 0.00 tbc 0.00 0.00 0.00 0.00 tbc

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

150.00 0.00 150.00 0.00 0.00

0.00 0.00 0.00 10.00 0.00

120.00 0.00 120.00 0.00 0.00

0.00 0.00 0.00 4.00 0.00

115.00 115.00 115.00 115.00 0.00

100.00 100.00 100.00 100.00 0.00

330.00 220.00 220.00 220.00 0.00

130.00 120.00 120.00 120.00 0.00

135,000.00 0.00 22,500.00 2,500.00 0.00

1,200.00 0.00 350.00 60.00 0.00

0.00

0.00

0.00

115.00 115.00 115.00 140.00 0.00

100.00 100.00 100.00 100.00 0.00

150.00 30.00 tbc tbc 0.00

1.20 1.20 1.20 1.20 0.00

115.00 0.00 0.00 0.00 0.00

0.00 0.00 0.00 >10.00 0.00

120.00 0.00 0.00 0.00 0.00

0.00

1,500.00 0.00 3,250.00 270.00 5,520.00 2,000.00 0.00 3,250.00

56.00 0.00 230.00 22.00 313.00 61.00 0.00 230.00

0.00

0.00

150.00 150.00 150.00 100.00 0.00

100.00 100.00 100.00 100.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

71.00 0.00 0.00 7.00 84.00 77.00 0.00 0.00

0.00

0.00

0.00

0.00

1.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

0.00

273.00 0.00 127.00 93.00 519.00 273.00 0.00 137.00

0.00

0.00

10.00 0.00 0.00 0.00 0.00

0.00

0.00

0.00

17.00 0.00 0.00 0.00 22.00 22.00 0.00 0.00

0.00

0.00

0.00

0.00

15.00 0.00 0.00 0.00 20.00 20.00 0.00 0.00

1,650.00 0.00 0.00 0.00 3,000.00 3,000.00 0.00 0.00

5.00 0.00 0.00 0.00 0.00

15.00 0.00 0.00 0.00 0.00

0.00

0.00

0.00

224.00 26.00 2.00 25.00 300.00 244.00 27.00 2.00

0.00

0.00

95.00 0.00 0.00 34.00 160.00 120.00 0.00 0.00

22.00 0.00 0.00 8.00 35.00 27.00 0.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00 0.00 4.00 0.00 0.00

4.00 0.00 0.00 0.00 0.00

0.00

0.00

0.00

0.00 0.00 8.00 0.00 0.00

0.00 0.00 2.00 0.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00 0.00 5.00 0.00 0.00

0.00 0.00 12.00 0.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00 0.00 0.00 75.00 100.00 0.00 0.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

1.00 0.00 0.00 1.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

1.00 0.00 42.00 0.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00 0.00 2.00 0.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

11,250.00 0.00 625.00 625.00 25,000.00 22,500.00 0.00 1,250.00

27.00 0.00 3.00 5.00 40.00 30.00 0.00 3.00

19.00 0.00 2.00 3.00 26.00 20.00 0.00 2.00

16.00 0.00 1.00 7.00 26.00 17.00 0.00 1.00

384.00 0.00 1.00 9.00 396.00 385.00 0.00 1.00

1,848.00 0.00 2.00 150.00 2,702.00 2,500.00 0.00 2.00

10.00 0.00 0.00 0.00 15.00 15.00 0.00 0.00

250.00 0.00 0.00 0.00 560.00 560.00 0.00 0.00

4.00 0.00 0.00 0.00 5.00 5.00 0.00 0.00

851.00 0.00 62.00 63.00 1,026.00 888.00 0.00 70.00

58.00 0.00 24.00 9.00 93.00 58.00 0.00 26.00

140,800.00 0.00 9,600.00 9,600.00 200,000.00 176,000.00 0.00 12,000.00

84,480.00 0.00 5,760.00 5,760.00 120,000.00 105,600.00 0.00 7,200.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

675.00 0.00 120.00 100.00 950.00 700.00 0.00 140.00

0.00

0.00

0.00 0.00 0.00 0.00 0.00

0.00

0.00

0.00

0.00

115.00 0.00 0.00 115.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

80.00 0.00 0.00 11.00 96.00 85.00 0.00 0.00

125.00 0.00 0.00 125.00 0.00

241.00 0.00 0.00 106.00 394.00 258.00 0.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

5.00 0.00 0.00 0.00 6.00 6.00 0.00 0.00

0.00

20.00 0.00 0.00 0.00 0.00

0.00

5.00 0.00 0.00 0.00 0.00

0.00

0.00

0.00

0.00

0.00

6.00 0.00 0.00 0.00 0.00

0.00

15.00 0.00 0.00 0.00 0.00

0.00

0.00

0.00

0.00

4.00 0.00 6.00 0.00 0.00

0.00

0.00

0.00

10.00 0.00 0.00 0.00 0.00

0.00

0.00

33.00 5.00 16.00 9.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.40 0.00 0.00 0.40 0.00

0.00

0.00 0.00 28.00 0.00 0.00

0.00

32.00 0.00 8.00 4.00 0.00

0.00

0.00

9.00 0.00 0.00 0.00 0.00

14.00 0.00 0.00 0.00 0.00

0.00

0.00

0.00

10.00 0.00 0.00 0.00 10.00 10.00 0.00 0.00

0.00

0.00

0.00

17.00 2.00 17.00 4.00 0.00

0.00

10.00 0.00 0.00 0.00 0.00

0.00

8.00 0.00 0.00 0.00 0.00

0.00

31.00 0.00 9.00 0.00 0.00

0.00

22.00 0.00 0.00 0.00 0.00

0.00

4.00 0.00 32.00 0.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

65.00 0.00 0.00 0.00 0.00

0.00

8.00 0.00 0.00 4.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

5.00 0.00 0.00 4.00 0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

0.00

2030 target 2050 target Additional InformationW UK E NI S W

0.00 Maintain range including main




0.00 Investigate release of Stock

0.00 Maintain range including mai



0.00 Maintain range including mai

0.00 Maintaining range including m

0.00 Maintain existing populations

0.00 0.00 Research has allowed the propa

0.00 0.00 Research has allowed the propa






0.00 Maintaining range measured as



0.00 This species has been a survey

0.00 Populations are currently kn

0.00 This target relates to Birk Cr

0.00 Further survey work is needed

0.00 Survey of Lough Neagh failed

0.00 Single grouped plan for river s


0.00 Comprises notification of sit


0.00 Biology and requirements are

0.00 Continuity of woodland habitat

0.00 Links to Maritime cliff and sl

0.00 Links to Sand dune HAP. This

0.00 Links to Lowland heathland H

0.00 Links to Lowland heathland H



0.00 Because of differences in hos







0.00


0.00 Key areas for delivery are th

0.00 The ideal for increasing avail

0.00 The number of known localities

0.00 Protection and maintenance of

0.00 Species re-establishment prog

0.00 Single grouped plan for river









0.00 Maintain habitat (trees) in su

0.00 The majority of stag beetle r

0.00 Good work has been done on th

0.00



0.00 Target aims to reintroduce spec

0.00 Populations are currently k

0.00 Target applies to one site -

0.00 Maintain current single popul

0.00 0.00 1. Extend existing site by lan

0.00 Procas granulicollis is probabl

0.00



0.00 Populations are currently kno

0.00 The baseline figure for suitab

1.00 0.00 Efforts should initially concen

0.00 Although this species formerly

0.00 Extent of decline since 1970:

0.00 Relatively widespread species

0.00 UK target is 110 by 2020 and

0.00 UK target is 44 sites by 2020

0.00 UK target is 66 by 2020 and 13

0.00 Target applicable to Wales. Ta

0.00 0.00 Targetting of specific measur

0.00 This target seeks to restore t

0.00 Semi-natural habitats suitable

0.00 This target should be achieve

0.00 Target applicable across Engl

0.00 Target applicable across Eng

0.00 With emphasis on restoring nig

0.00


In England and Scotland, increase the BBS index to 130% of the 2003 level by 2015 and to 150% of the 2003 level by 2020. Maintian the index at its current level in Wales. Extent of decline since 1970: > 50% (1970-2003 CBC/BBS combined index). ELS is considered the main delivery mechanism in England. Tir Gofal is the main delivery mechanism in Wales.

0.00 0.00 England: The 2020 target was

0.00 0.00 England: The target is based

0.00 Core areas (Hebrides and Orkn

0.00 This target is based upon inc

0.00 Target is based upon net incr

0.00 Self sustaining populations de


0.00 Extent of range change: -12%

0.00 This species has ceased to bre

0.00 This species has ceased to bre

0.00 0.00 There needs to be expansion o

0.00 0.00 No baseline is available since

0.00 Across England and Wales. T

0.00 Across England.

0.00 With emphasis on restoring wo

0.00 This target is based on the m

0.00 This range is based on the nu

0.00 The species formerly bred in N

0.00 This target has been set as th

0.00 This target has been set as t

0.00 This target has been set as t

0.00 Ensure that the average rate

0.00 Probably no longer regular bre


0.00

0.00 In England, this target requi


0.00 Increase the BBS index to 220


0.00 The 2020 UK target is equivale

0.00 The 2020 UK target is equivale

0.00 Population to be maintained i

0.00 10 sites used in any one year,

0.00 At least 26 sites are maintain

0.00 Ensure that the average rate of change between 2006 and 2010 is not negative. The slope of the regression of the log-transformed BBS index for 2006-2010 against year should be > or = zero. Extent of decline since 1970: > 50% (1970-2003 CBC/BBS combined index). ELS is considered the main delivery mechanism in England.


0.00

0.00

0.00 Ensure that the average rate o

0.00


0.00

270.00 0.00 Existing recovery areas in Wal

22.00 0.00 Existing recovery areas in Nor

0.00 Links to Native Pinewood HAP

0.00 Range expansion should be foc



0.00 Target refers to 4 sites in Dor

0.00 Target refers to Sussex site

0.00 Maintain all 28known sites for

N.B. This is the overall UK long-term target - individual country targets have not been set in all cases because of uncertainty about achievability. Maintain favourable conditions at current and historical breeding sites in each of the four countries in order to promote expansion and recolonisation. Country targets:1. Restore roseate tern numbers in Wales and Scotland to or above their 2003 levels (2 breeding pairs in Wales, 8 in Scotland) and maintain these numbers until 2010 - target to be reviewed in 2010.2. In England, increase the breeding population from 70 pairs in 2003 to 100 pairs in 2010, 125 pairs in 2015 and 150 pairs in 2020.Carry out appropriate management at all colonies to ensure that roseate terns can breed successfully.

0.00 This species needs appropriat

0.00 Baseline is the number of 1km

0.00

0.00 Achieving favourable condition

0.00 Potential for re-introducing th

0.00 The 7 main populations are a

0.00 This target will be implement

0.00 This target will be aimed at t

0.00 Ephemeral species, therefore

0.00 Target based on 2003-2005 data

0.00 Target refers to enhancing populati


0.00 This species is now known from

0.00 Target 1 refers to maintaining

0.00 Consideration should be given

0.00 Delivery will focus on follow u

0.00 Target 1 refers to maintaining

0.00 Target 2 requires creation of

0.00 Target refers to number of kno

0.00 The single known UK site for

0.00 Monitor and maintain/improve

0.00 Maintain the English & Scotti

0.00 Consider one former site in No

0.00 Target will focus on site mana

0.00 Each thatched roof equates to

0.00 Target refers to reintroductio

0.00 Target refers to 4 sites in W

0.00 Target refers to potential tra

0.00 Target refers to 1990 onwards

0.00 Target refers to reintroductio

0.00 Target maintains all known pop

0.00 Management would aim to increa

0.00 Research is a priority (ecolo

0.00 Delivery will be focused on on

0.00 This will target direct manage


0.00 Despite occurring in all 4 UK

0.00 Pohlia scotica is a ruderal sp

0.00 Target refers to maintaining s

0.00 Target 2 requires creation of

0.00 This target will be achieved

0.00 Maintain and ehance the popula

0.00 Maintain and ehance the popula


0.00 Target refers to increasing po


0.00 Target refers to maintaining

0.00 Target refers to single known


0.00 Will involve targeted manageme

0.00 This minute species probably r

0.00 Target refers to maintaining s

0.00 Target refers to increasing p

0.00 This target will be achieved

0.00 Target refers to 3 ‘sites’ (B

0.00 This species is known only fro

0.00 Target refers to reinforcement

0.00 Adult colonies are currently

0.00 Initial effort should be aimed

0.00 Each separate 'section' of a r

0.00 See species action plan. Key

0.00 See species action plan. Key

7.00 0.00 Habitat management of sites ad

0.00 See species action plan

The Pearl Bordered Fritillar

Increase the number of occupi

0.00 See species action plan. Cor

0.00 0.00 See species action plan. Targe

0.00 The core range is defined as

109.00 0.00 MF persists within a network

0.00 See species action plan. Core

0.00

0.00


0.00 The target of 25 colonies in t


0.00 0.00 There are currently 10 popula



0.00 See species action plan. Targ

0.00 Achieving this target will al

0.00 0.00 Pursuit of target should be bas

0.00 0.00 Pursuit of target should be b

0.00 Confirm presence in the two c

0.00 Achieve multiple populations

0.00 In the last 25 years, the spec

See species action plan, Four landscape areas include: North Atlantic Coast (Cornwall), Polden Hills, Cotswolds, and Dartmoor.

See species action plan. Pop/ns to be re-established on a further 2 sites in Cornwall, 5 in Somerset, 2 in the Cotswolds and 1 in the south Hams area of Devon.

0.00 Pursuit (and quantification) of

0.00 The figures for UK, E, NI, S &

27.00 0.00

0.00 Key sites are those where pop

0.00 Achieving this target will in

40.00 0.00 Aim of target is to improve th

8.00 0.00 Based on work in the New Fore

0.00 Allis shad are still reguarly

0.00 Consolidation through managem

0.00 Historic range establishment f

0.00 Ascertain if shad breed in the

0.00 In Britain, spawning populatio

0.00 Historic range establishment f

0.00 Ascertain if shad breed in the

0.00 This target is aimed at provid

Safe havens (Ark sites) will be created in or near SACs and in other areas where important populations exist. These will include; In EnglandIn England/Wales: River Wye/ Afon Gwy Fynwy/ Monmouthshire; Gloucestershire; Herefordshire; Powys SO109369, In Northern Ireland: Largalinny Fermanagh H074537, Magheraveely Marl Loughs Fermanagh H494284, Upper Ballinderry River Tyrone H734792, West Fermanagh Scarplands Fermanagh H085491.In Wales: River Usk/ Afon Wysg Casnewydd/ Newport; Fynwy/ Monmouthshire; Powys SO301113.

0.00 In the UK the vendace has only

0.00 This target is aimed at provid

0.00 There are post-1980 records f

0.00 There are recent records from

0.00 Currently occupied sites are 2

0.00 Supplement the amount of breed

0.00 Where the amount of breeding h

0.00 This is a widespread species a

0.00 For this species, a site/popul

0.00

0.00

0.00 6 main populations centres on

0.00 Currently occupied sites are 1

0.00 Habitat management to provide

0.00 Where the amount of dead aspen

0.00

0.00 This cranefly is widespread in

0.00 It is currently known from c.

0.00 Currently known from the Seve

0.00 The target number of 28 repre

0.00 It is likely that this species

0.00 Potentially suitable habitat f

0.00 Recorded from few sites in Sco

0.00 Sites = lake/ditch/pond; extan

0.00 Establishment will ideally be

0.00 Oxfordshire (Port Meadows,

0.00 New populations would be in

0.00 Extant populations in Gloucs,

0.00 To achieve this, sites will be

0.00 This target could use a 'floa

0.00 The key areas for this species

0.00 There are currently 10 populat

0.00 Target refers to the 3 current

0.00 Target refers to occurrence a

0.00 T2 involves translocation (rei

0.00 Natural sites are defined here

0.00 A proxy target that promotes

0.00 It occurs in 18 10km squares i

0.00 This target attempts to provid

0.00 29 occupied 0.1 km squares rep

0.00 This target is to maintain a nor

0.00

0.00

0.00

100.00 0.00

0.00 New populations would be in S

0.00

0.00

0.00 Native sites, not planted popu

0.00

0.00 This target could use a ‘floa

0.00 As a taxon associated with bin

0.00 SU94, TL88, TM46 all have 2 e

0.00 SU94, TL88, TM46 all have 2 e

0.00 This target could use a 'floa

0.00 Retention of disused chalk pi

0.00 This target could use a ‘floa

Sites = individual ponds; extant = post-1995 records. Native sites = 5 - Heath House, Halfpenny, Chequers, New, Quaves. Introduced sites = 4 - Brimmer, Black Park, Penny, Jeremy. Mechanical clearance & restoration of grazing are both thought necessary for establishment of viable populations.

Establishment will ideally be achieved by restoration of historic sites through habitat management, with the aim of restoring plant populations from buried seed banks. Particular attention should be paid to sites (4 no. - Latchmoor, Daisy, Manning, Coleshill) where D. alisma has been seen since 1990. Mechanical clearance & restoration of grazing are both thought necessary for establishment of viable populations.

0.00 Establish positive management

0.00 An apparently widespread spec

0.00 Arable plants such as this sp


0.00

0.00 With a view to facilitating na

0.00 Vulnerable areas - West Corn

0.00

0.00 Stronghold vice countries with

0.00

0.00 Restore the habitat at Penall

0.00 T1 – Established viable additi

0.00 Current range as defined in th

0.00 This target includes tree lin

0.00

0.00 This target aims to ensure tha

0.00 Self sustaining is defined as

0.00 Ongoing research into pollinat

Natural sites are defined here as populations thought to have arisen naturally (i.e. not from intentional sowing) as part of an arable community. Long-established is here defined as (i) either 'natural sites that have long history of continuity (albeit perhaps sporadically over time), or (ii) newly recorded, viable populations where the consensus opinion among botanists and other conservationists is that the populations have arisen from a long-established seed bank, as opposed to international sowing.

0.00 This target describes manageme

0.00

0.00 The populations on all three si

0.00 Three sites in England have be

0.00

0.00

0.00

0.00

0.00 A metapopulation is deemed to

0.00 Ownership of sites supporting

0.00 Target relates directly to targ

0.00 Preliminary genetic research h

0.00 T1 is based on native populati

0.00 T2 relates to instigating app

0.00 There are 40 Scottish lochs wi

0.00 There are 52 identifiable wate

0.00 Currently known from seven br

The area occupied by the plant on the three sites in England totals less than 3ha and this represents only a small part of the fen on these sites. In order to maintian populations it will be necessary to ensure that the fen sites in their entirety are maintained. The survival of Welsh populations also depends on the management of landscape-scale processes and targetted work on small, currently threatened sites.

There is still concern that some populations are threatened because they are isolated and there is a need to improve ‘connectivity’ between fragmented populations. Reducing isolation or improving connectivity can be achieved through: habitat management; habitat creation; water level/hydrological management; water quality improvements.Identify sites by 2010; address priority sites by 2015 and complete by 2020.

Vulnerable Joint Character Areas (England) are Thames Basin Heaths, Wealdon Greensand, Hensbarrow, Dartmoor, Eden Valley (Wan Fell), Cumbrian High Fells. Scotland - Moray/Nairn area for targeting population delivery.

0.00 Establishment would ideally b

0.00

0.00 Vulnerable Areas = Norfolk, St

0.00 The target to create new 'meta

0.00 There are still isolated larg

0.00 Population viability is diffic

0.00 To demonstrate that the popul

0.00 There are 11 Scottish lochs wi

0.00 There are 8 sites in which P.

0.00

0.00

0.00 A metapopulation is deemed to

0.00 Restoration should be achieved

0.00 R. rupestris is thought to for

0.00 Most of the sites are believed

0.00 Although population size is re

0.00 All population increase has so

0.00 Little accurate data is availa



Stronghold Areas= Powys, New Forest, Surrey/Berkshire, Cumbria, Cornwall, Pembrokeshire, Gwynedd, Scotland (Western Isles, Strathclyde, Highlands). Vulnerable Areas = Norfolk, Staffordshire, Lothian, Tayside, North Yorkshire, Humberside, Clwyd. To achieve a 'viable' population may require management/protection at specific sites to enhance population size/resilience. This may equate to the site being deemed to be in favourable status for this species.

Vulnerable areas with extant populations of R. tripartitus are West Penwith, Cornish Killas & Granites, Bodmin Moor, The Culm, Low Weald, High Weald, London Basin. Stronghold vice countries: Pembrokeshire, Anglesey, Cornwall, West Glamorgan, Kent, East Sussex?


0.00 Establish positive management

0.00 Regenerate degraded habitats

0.00 Viable populations means stabl

0.00 Extant sites in the Cotswolds

0.00 A metapopulation is here defin



0.00


0.00 There have now been 4 re-intro

0.00 Target small vulnerable popula

0.00 Fruiting to be confirmed in al

0.00 Survey all known sites (and an

0.00 Usually found in sandy or othe

0.00 The key actions for regius sho

0.00

0.00 Single grouped action plan for


Natural sites are defined here as populations thought to have arisen naturally (i.e. not from intentional sowing) as part of an arable community. Long-established is here defined as (i) either 'natural sites that have long history of continuity (albeit perhaps sporadically over time), or (ii) newly recorded, viable populations where the consensus opinion among botanists and other conservationists is that the populations have arisen from a long-established seed bank, as opposed to international sowing.













0.00 Action aimed at 5y investigati

0.00

0.00

0.00

0.00

0.00 Action aimed at 5y investigati

0.00 The New Forest remains the co

0.00

1,250.00 50,000.00 45,000.00 0.00 2,500.00 2,500.00 Increase the number of breedi

7.00 48.00 33.00 0.00 6.00 9.00 In 2005 the potential area of

4.00 27.00 21.00 0.00 2.00 4.00 This is one of two range targe

8.00 26.00 17.00 0.00 1.00 8.00 Maintain populations in existi

10.00 396.00 385.00 0.00 1.00 10.00 Maintain populations in existi

200.00 2,702.00 2,500.00 0.00 2.00 200.00 Mainain existing extent of occ

0.00 20.00 20.00 0.00 0.00 0.00 Populations to be established

0.00 750.00 750.00 0.00 0.00 0.00 To ensure that the population

0.00 0.00 6.00 0.00 0.00 0.00 The six vice counties are Wes

68.00 1,026.00 888.00 0.00 70.00 68.00 Increase the area of occupancy

9.00 0.00 Maintain populations in the vi

12,000.00 0.00 Increase the number of popula

7,200.00 0.00

0.00 Site/population: ranges from a

0.00 This will largely be achieved

0.00 Belonia calcicola has finally


0.00 This will be achieved through

0.00 This will involve attempting t


0.00 There are approximately 20 pop

0.00 Urgent action required as only

0.00 Urgent action required as only

0.00 Requires liaison with FE & ma

Viability target. Increase the number of ponds that are considered of suitable quality to sustain viable great crested newt populations, and to encourage creation/retention of metapopulations. This is to be done through habitat management and creation. We aim to maintain a consistent proportion of 'occupied ponds' in this condition as more ponds become occupied by the species through conservation work. This target defines suitability through the Habitat Suitability Index developed by Oldham, R.S et al (2000) Evaluating the suitability of habitat for the great crested newt (Triturus cristatus), Herpetological Journal, Vol.10, pp 143-155. Oldham et al (2000) indicates that c.60% of occupied ponds currently have an HSI score of 0.7 or above. The aim is to maintain this proportion. (60% of our 200,000 occupied ponds (Population -2030 target) equals 120,000). However this is based on a small sample from only two counties (Leicestershire & Gloucestershire), so it is possible that this proportion is not representative for the UK as a whole. Further research and survey is likely to change this observed proportion and so a change in the target is likely at next revision opportunity. Detailed guidance for LBAP practitioners on the delivery of these targets will be provided in the GCN SAP Work Programme (SAP implementation document), including disaggregation of the targets at the country level, and how LSAPs can achieve their local targets.

0.00 Target will be achieved throug



0.00 A very threatened species on c

0.00 T1. This will largely be achie




0.00 Target will be implemented ma



0.00 This will be achieved by the cr

0.00 This species was last recorded

0.00 This target will entail some m

0.00 Little is known of the ecology

0.00 Maintenance of current distri

110.00 0.00 Further increase in range by

0.00 The target is to maintain the

0.00 General aim is to retain the

0.00 In light of the documented dec

0.00 The current 2005 baseline for

0.00 The majority of range expansio

0.00 Meeting this target will invol

0.00

0.00 Count data from key sites are




0.00 The target is to increase the


0.00 Meeting this target will invol

11.00 0.00 A range extension target shoul

0.00 Count data from maternity site

136.00 0.00 The target is an increase in


0.00

0.00 Target aimed at maintaining t

0.00 This target aims to maintain t

Reintroductions to the following 11 counties: Cambridgeshire, Nottinghamshire, Cheshire, Buckinghamshire, Warwickshire, North Yorkshire, Suffolk, Bedfordshire, Staffordshire, Lincolnshire, Derbyshire

To maintain populations of red squirrels across their current range conservation activity will focus on selected priority woodland areas - see details for each country. Implicit in this aim is that the populations will be viable in the long term and that they will be present in all of the main centres of population where they occur today. The aim also accepts that, at the moment, not enough is known about the populations across the UK, or about the management of red squirrels, to be able to predict what proportion of the present red squirrel population might be safeguarded.

Throughout the UK red squirrels face pressures from non-natives, disease and habitat loss. In England and Northern Ireland they are undergoing an active loss of red squirrels as it is not possible to maintain the range at the current level. In Wales the target set is to maintain the current range and although losses may occur it is possible that this may be countered by range increase on Anglesey as a result of reintroductions and recolonisation of grey free areas. In Scotland there has been a slight range expansion, due to increased afforestation, but the continued northward spread of grey squirrel populations is a major concern for the future

0.00 Target aimed at maintaining th

0.00 Surveys should be carried out

0.00 Target based on the existing

0.00 ICES Working Group on the Bio

0.00 Up to date population status c

0.00 Communication with land-owners

0.00 Viable freshwater pearl mussel

0.00 There are pearl mussel popula

0.00 Most viable populations are not

0.00 Freshwater pearl mussels have

0.00 Species known only to occur at

0.00

0.00

0.00 Communication with land-owner

0.00 Population expansion may resu

0.00 Ensuring populations are maint

0.00 Vertigo genesii occupies a bot

0.00

0.00 Maintaining range is considere

Due to the recent survey work of I Killeen and M Willing, (contained in the report Further Surveys to Elucidate the Distribution of the Fine-Lined Pea Mussel Pisidium tenuilineatum Stelfox, 1918 (2004) Technical report W1-054/TR) detailed knowledge is available for the first time on the distribution of the fine-lined pea mussel.

Further work on the fine-lined pea mussel could be focused on certain river reaches of the Rivers Lyde, Windrush, Evenlode, Glyme, Leach, Monnow, Axe, Frome, Piddle, Avon, Test and Axe, as in these rivers the fine lined pea mussel consists of less than 5% of the total pea mussel population.To maintain key populations of P. complanata across their current range. Implicit in this aim is that the populations will be viable in the long term and that they will be present in all of the main centres of population where they occur today. The aim also accepts that, at the moment, not enough is known about the populations across the UK, or about the management of P. complanata, to be able to predict what proportion of the present population might be safeguarded. There should be a long term target to maintain key populations of as their highly localised distribution puts them under threat. key populations: (found on the Brue, Medway, Old West, Arun and Wye systems).

Populations of Pseudanodonta complanata are generally restricted to a distinct, narrow stretch of river. Within this habitat over 90% of the population may be found within a single ‘hotspot’ of just a few hundred metres. Although key populations have been estimated as containing as many as 1,000,000 individuals their localised nature makes them vulnerable. Principal threats come from river management activities and zebra mussel invasion (a new and significant threat). Action to meet the target should focus on reducing these threats. Other threats include deterioration in water quality, eutrophication, drought, low numbers of host fish populations and pollution incidents.

The distribution of Vertigo geyeri in the UK is much better known now than at the time of publication of the original plan and the number of known populations has increased from 13 to 32. Its association with botanically rich calcareous seepages means that a majority of its populations are actively conserved as part of general habitat conservation activities. Maintaining range is considered sufficient to ensure secure status. For most populations this will entail little more than continuing with existing habitat management, but improvements to habitat quality will be required in some cases. An assessment of habitat condition for all populations is needed before action can be targeted.

0.00 Ensure autecological studies,

0.00 0.00 Identify and encourage survey

0.00 Ensure autecological studies

0.00 Identify and encourage survey



0.00 Ensure annual surveillance on













0.00 Ensure larval counts (or adult

0.00 Ensure surveillance of larvae


0.00 Undertake management to increa

0.00 Currently there is no site whe



0.00 Undertake surveillance of adu

0.00 Undertake management to incre

0.00 Ensure timed counts of adults

0.00 Identify potential sites and e

0.00 Encourage survey. Wales, sou

0.00 Ensure habitat and species at

0.00 Undertake site liaison and app

0.00 Ensure surveillance for larva




0.00 Ensure annual surveillance is

0.00 Ensure surveillance of larvae

0.00 Ensure surveillance for larvae

0.00 Ensure surveillance for larvae



0.00 Ensure surveillance for adults

0.00 0.00 Identify and encourage survey

0.00 Ensure timed counts of ova an

0.00 Ensure liaison with site man





0.00 Ensure annual surveillance of

0.00 Encourage site liaison and app





0.00 Ensure surveillance of adults




0.00 Target is about increasing the

0.00 Survey to identify suitable si

0.00 Core area - Western Argyll

0.00 Survey to identify suitable si

0.00 This is an elusive species wit



0.00 Target areas to be identified

0.00 Known site - Wareham Forest -

0.00

0.00 The extant sites are Slapton

0.00 This target focuses on the healt

0.00 Scotland - On mainland Orkney

0.00 This target aims to restore the

0.00 With no net loss, 9 sites are

0.00 Sites are Llyn Gynon, Pond-Y

0.00 England: Maintain populations

0.00 England: Restore viable popula

0.00 Sites: Blagdon Lake, Chew Va

0.00

0.00 This target could use a 'float

0.00 Significant restoration work is

0.00 Key areas for T. intricata inc


0.00 Key areas for T. intricata inc

0.00 Key areas for T. prolifera i

0.00 Key areas for T. prolifera i


0.00 * three of these ‘sites’ in th

Monitoring

Monitoring over 10-yr pe

Repeat surveys of known s



Extinct. Awaiting re-intro





Repeat surveys of known

To be determined. Probab

Count of active nests

Count of active nests

Yearly direct monitoring



Monitoring over 10-yr per





Sites to be monitored on

Annual monitoring at both

Suitable habitat will be

N/A

Monitor all known 1km2 s

Monitor potential new sit

Sites should be monitored


Annual or better monitorin








Annual or better monitori




Monitoring will be by ref

Data on the current cond

Known populations should

Monitored by surveillance

reporting and monitoring

Monitor all known 1km2 e

Survey suitable habitat at

Monitor all known locatio

Survey suitable habitat a

Monitor all 10km2 every


Monitor all known catchm

Monitor selected sites for

Monitor all known sites e

Two monitoring methods ar





A precise definition of su

Annual survey for Oberea

5 yearly survey of all pot

Monitoring will be undert





Lengths of suitable habit

Progress will be monitore

Population targets to be

Range targets to be meas

Bittern monitoring will c




Monitoring to be achieve




By next planned SCARABBS


By next planned SCARAB


Range targets to be mea

Full surveys of the UK co

Full surveys of the UK co

Full surveys of the UK cor

Cirl bunting is included





The status of this specie

The status of this specie

Scottish Crossbill is inc

Scottish Crossbill is in



By next planned SCARAB

An amended baseline will



Aerial surveys of all key










Range targets to be measu

An unbiased index of Grey

The percentage of BBS sq

Regular sites to have vi

Sites to have visits dur

Sites to have audit (cond



The breeding population a

The breeding population a




Scarrabs surveys in 2005

Scarrabs surveys in 2005

National surveys will tak

National surveys will tak



Sites should be monitore

For reporting purposes, s

Periodic (5 yearly) re-sur

Essential to monitor popu

Occupied sites (burns an

Visit annually to assess


Monitor main sites at 6 ye

Monitored by assessing a

This can be assessed thro

Difficult to monitor as ep

All SSSI should be visite

Target will be monitored




Sites are monitored over

Sites should be visited a

Target will be monitoired

Sites should be visited ev

Monitoring programme set

Monitoring programme requ

Site visit once every 3 ye

Target will have been met

Thatch sites monitored ev

Thatch sites monitored ev

Visit annually (especially

Monitoring by measuremen

Sites should be visited e

Monitoring should be link

Monitoring should be link

Sites monitored every 5

The population will be dee

The population will be de


This target will be deeme

SNH needs to commission s

Sites should be visited at


Monitoring carried out on

The site is currently mon

The site is currently mon

3 yearly monitoring of all

Target will be achieved if

Site should be monitored

Site should be visited at

Sites are currently monit

Sites are currently monit

Pops at high risk and ann

Target will be monitored

Monitoring carried out on

Sites should be visited a

Sites should be visited at


Annual searches for adult c

Searching for adult colonie

Seiving samples of flood

Annual transects and time

Annual transects and time

Targeted surveys on a 5 y

Annual transects on 60 si

Targeted surveys on a 5



Transect monitoring

BNM database

Monitoring of this species at a site and fine scale level (1 km2.) must be initiated, this is overdue and ideally requires resourcing. Better Target values can be set once adequate base line survey data has been collected. Monitoring should aim to be repeated within a 5 year interval for “natural” sites and more regularly (3yrs. max) in artificial, or other sites deemed to be at higher risk.

Larval web surveys repea

Transect monitoring & B

Transect monitoring at al

Transect monitoring at all

Annual timed counts at a

Survey all suitable habita


Annual transect monitori

Annual transect monitori

Targeted subsample surve

Targeted survey of restor


All existing and newly re

All existing and newly re

Confirmation of presence

Annual counts of singing

All newly re-introduced p

All newly re-introduced p

Regular presence/absence

To date, in the UK only

Determining absence/pres

Common Standards Monitor

If implemented, by fish s

Egg searching technique

Measured by the number of

Fish survey techniques

If implemented, by fish s

Measured by the number of

Fish survey techniques

Water quality should be m

Periodic momitoring shou

Periodic momitoring shou

Populations at key sites w

Populations at key sites

Annual monitoring for lar

Annual monitoring of the a

Annual monitoring of the a

If the species is to be m

5-year cycle of river sys


Unknown. The adults are

It should be possible to m

Annual monitoring for lar

Monitoring of the amount

Annual monitoring of the

Monitor habitat within ra

A sample of c.25 sites su

A sample of c.25 sites su

3-year cycle of river syst

3-year cycle of river syst

Common Standards Monitori

Common Standards Monitori

Monitor all known rivers

To be deemed extant, a po

To be deemed extant, a po

Sites to be monitored annu

The population is deemed

Criteria will be defined f

A dedicated survey has be

A dedicated survey has be

Annually until populations

Sites visited at least 6 y

Monitoring of known popula

Monitoring of the Cereal

Baseline data is from Ric

SCM 6-year cycle for mon

Fluctuation in cabbage n




Annual surveys and recor

Annual surveys and recor

Annual monitoring of indiv

Annual monitoring using v

Monitoring all extant popu

Annual monitoring using v

Monitoring its continued


Monitoring of extant pop


To be deemed extant, a population must be recorded in at least one year in the five year period proceeding reporting date.

To be deemed extant, a population must be recorded in at least one year in the five year period proceeding reporting date.

Monitoring of range in 10-


Monitoring a range in 10km


Monitoring of known popula



For reporting purposes, r

Monitoring: should be on

Annual survey and monit

Annual survey and monit

T1 – Transplanted sites a

Species monitoring for UK

Scheme evaluation should

Long term monitoring thro

Monitoring through the su

Monitoring will be throug

Measuring success will be

Report the number of occ


Report the number of sit

Baseline - number of 10-k


Populations can be counte

Populations can be counte

Report the number of new

Sites should be assessed

Report the number of site

26 out of the 40 lochs oc

The proposed SEPA EIP (E

Aquatic macrophytes surv

Monitor status of specie

Population is deemed exta



Sites in which P. rutilus

The two sites which have



Monitoring should be unde

Periodic monitoring at no



Monitoring range in 10-km


Monitoring range in 10-km


Establish and maintain fi

Local recording schemes u

Extant is defined as plant

Extant is defined as plant


Monitoring the Cereal Fie


Biennial monitoring of wi


We are currently working

At least three estimates o






Maintenance is no further loss of distribution.Undertake survey at key sites on a 5 year rolling programme. Need to list key sites - suggest Ouse Washes, Somerset Levels, Romney Marsh, Broadland

Monitoring of known populations: all specified, extant populations should be visited at least once during the reporting period (years). For the purposes of monitoring targets, if the plant is not present, but the overall arable habitat is in good condition (i.e. species rich) then the population is deemed to be extant.





















Natterjacks will continue

Monitorers will record po

Monitorers will record po

Most sites are known and



The breeding populations

The number of breeding a

Annual monitoring of rein

Stratified sample to asse

This target measures overa

Stratified random blanket

Stratified random blanket

Monitoring all know popula

Sites are monitored appr

Annual monitoring of site

Sites are monitored appro

The site should be monit

No active monitoring but

Sites are monitored annua

Sites are monitored appr

Biannual monitoring at le

Biannual monitoring at le

Site visits to 10-15 year



5 yearly monitoring of bot

Monitoring on an annual ba

Monitoring at 5 yearly int

The target will be achieve

Sites are monitored on a 5

Sites are monitored on a 5

Sites are monitored every

Monitoring on an annual b

Monitoring on annual bas

N/A at present.

Periodic monitoring by lic


Baseline data accrued thr

Annual surveys can be car

Volunteer bat workers and

Not clear and will be dif

Hare numbers fluctuate si

Monitoring will continue

Monitoring set up 1999, repeated as part of SCM in 2004. Monitoring will be repeated every 6 years as part of SCM programme. Data suggests P. lepidophora is somewhat of an ephemeral species, present during late summer and over winter, but absent in the summer months.

Volunteer bat workers and

Data will be collected on




Data on occurrence are co

Data on occurrence are co

Monitoring of the populat

Data collection for this

Hibernation surveys are

A new scoping study (fund

Monitoring can be carrie

Targeted survey for monit

Data on occurrence are collected in a variety of ways ranging from periodic public-participation great nut hunt surveys to the ad hoc collection of records from local mammal recorders and, more recently, developers. English Nature now has a national site inventory containing post-1990 records of 1169 sites with dormice in England and Wales. This is the most comprehensive collection of recent dormouse records, but remains far from being a complete inventory. These data are now available through the NBN gateway.

As well as the inventory, progress has been made with population monitoring. A National Dormouse Monitoring Programme has been set up to collect data on the number of dormice found in next-boxes at almost 250 ‘key sites’ across England and Wales and use these to generate an annual index of population change. A recent analysis of the data showed that this is sufficiently sensitive to detect changes at the required level (25% over 25 years nationally). Data on occurrence are collected in a variety of ways ranging from periodic public-participation great nut hunt surveys to the ad hoc collection of records from local mammal recorders and, more recently, developers. English Nature now has a national site inventory containing post-1990 records of 1169 sites with dormice in England and Wales. This is the most comprehensive collection of recent dormouse records, but remains far from being a complete inventory. These data are now available through the NBN gateway.

As well as the inventory, progress has been made with population monitoring. A National Dormouse Monitoring Programme has been set up to collect data on the number of dormice found in next-boxes at almost 250 ‘key sites’ across England and Wales and use these to generate an annual index of population change. A recent analysis of the data showed that this is sufficiently sensitive to detect changes at the required level (25% over 25 years nationally). Data on occurrence are collected in a variety of ways ranging from periodic public-participation great nut hunt surveys to the ad hoc collection of records from local mammal recorders and, more recently, developers. English Nature now has a national site inventory containing post-1990 records of 1169 sites with dormice in England and Wales. This is the most comprehensive collection of recent dormouse records, but remains far from being a complete inventory. These data are now available through the NBN gateway.

As well as the inventory, progress has been made with population monitoring. A National Dormouse Monitoring Programme has been set up to collect data on the number of dormice found in next-boxes at almost 250 ‘key sites’ across England and Wales and use these to generate an annual index of population change. A recent analysis of the data showed that this is sufficiently sensitive to detect changes at the required level (25% over 25 years nationally).

Surveys can be carried o

Surveys can be carried o

Monitoring can be carrie

Landings of commercial s

Baseline monitoring of th


Most of targets will be me

Monitoring of this targe

For reporting purposes re


Carry out monitoring at L

Future action will conce

Monitoring of selected si

Monitoring of selected si


Monitoring known sites e


Periodic monitoring of sel

All future monitoring should incorporate standard methodologies to allow temporal and spatial comparisons between river reaches.

Time intervals for survey work is unknown at the moment but some attempt should be made in the future to compare with the baseline data reported in 2004.

Annual surveillance of la

Habitat assessment and an

Annual surveillance of adu

Habitat assessment and, w

Annual surveillance using


Annual surveillance of ad


Annual surveillance on ke









Surveillance should incor


Surveillance should incorp

Surveillance of larvae on



If a site is located where


Undertake surveillance of



Undertake timed counts of

Undertake timed counts of

Encourage survey.



Undertake surveillance fo

Surveillance for larvae/ad


Undertake surveillance of


Surveillance of larvae at




Surveillance for larvae at

Surveillance of adults on

Ensure surveillance under

Ensure surveillance of ov

Ensure surveillance of ov

Ensure surveillance of adu

Surveillance for larvae/ad

Surveillance of larvae ann

Surveillance for larvae at


Ensure surveillance of ad

Surveillance of adults at

Undertake surveillance for

Ensure surveillance of ad

Surveillance (timed counts

Undertake surveillance fo

Undertake surveillance for







Monitored by assessing al

We have a 13 year run of

Extant = present in at le

High-risk sites are priori


This species can survive


Extant = present in at least one year out of 5 years preceding a reporting period. Viable and stable = always present in a fertile state when surveyed. Populations must be surveyed in at least 3 separate years in a 5 -year period . Fertility indicates the health of the population, and ensures accurate identification (distinguishing it from Chara globularis).

General - appearance one






Repeat sample survey of

Turtle Dove. Long-term trend is for UK

Skylark. Long-term trend is for England

Song Thrush. Long-term trend is for UK

0

100

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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ces

(yea

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CBC/BBS trendBBS trend

2020 target

2015 target

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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2020 target2015 target2010 target

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

Indi

ces

(yea

r 200

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0) CBC/BBS trendBBS trend


Spotted Flycatcher(Note that the BAP target for 2010 is to ‘improve the negative trend’)Long-term trend is for UK

Bullfinch(Note that the BAP target for 2010 is to ‘improve the negative trend’). Long-term trend is for UK

0

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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0

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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2020 target2015 target

0

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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(yea

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0

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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ces

(yea

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0)



Linnet. Long-term trend is for England

Tree Sparrow Long-term trend is for England

Reed Bunting. Long-term trend is for UK

0

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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ces

(yea

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2020 target

2015 target

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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(yea

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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ces

(yea

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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(yea

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2800

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ces

(yea

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0

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

Indi

ces

(yea

r 200

3=10

0)



(Note that the BAP target for 2010 is to ‘improve the negative trend’).Corn Bunting Long-term trend is for UK.

0

50

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250

1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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ces

(yea

r 200

3=10



0

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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(yea

r 200

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0)



0

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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ces

(yea

r 200

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0

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

Indi

ces

(yea

r 200

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0)



0

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400

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800

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1200

1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

Indi

ces

(yea

r 200

3=10

0)

CBC/BBS trend

BBS trend


0

50

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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ces

(yea

r 200

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

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(yea

r 200

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

Indi

ces

(yea

r 200

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0

50

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1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

Indi

ces

(yea

r 200

3=10

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0

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400

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800

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1200

1970 1975 1980 1985 1990 1995 2000 2005 2010 2015 2020

Indi

ces

(yea

r 200

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CBC/BBS trend

BBS trend


Blue = actual NBMP indexRed = projected target increase

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

2017

2018

2019

2020

0

50

100

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300

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P. pipistrellus - Common pipistrelle

Year

Popu

latio

n In

dex

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

2017

2018

2019

2020

0

20

40

60

80

100

120

140

160

180

200

P. pygmaeus - Soprano pipistrelle

Year

Popu

latio

n In

dex

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

2017

2018

2019

2020

0

20

40

60

80

100

120

140

160

180

200

R. hipposideros - Lesser horseshoe

Year

Popu

latio

n In

dex

Blue = actual NBMP indexRed = projected target increase

1995

1996

1997

1998

1999

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

2011

2012

2013

2014

2015

2016

2017

2018

2019

2020

0

20

40

60

80

100

120

140

160

180

200

P. pygmaeus - Soprano pipistrelle

Year

Popu

latio

n In

dex

Southern damselfly - distribution maps

Southern damselfly - population cluster maps

Greater horseshoe roosts are show as circles, maternity sites as diamonds. Red squares show current distribution (88 squares). Blue squares show examples of possible range extension – the darker the colour the sooner the square contributes to the target.

Brownsea Island

Isle of Wight

Northumberland

North Tyne peripheryNorth Tyne

Durham, Tyne & Wear

North Cumbria

South Cumbria

Sefton Coast

ThetfordAberhirnant

Tywi

Crychan

Anglesey

Cynwyd Clocaenog

Nantyr

Cwm MynachCoed y Brenin

Cwrt

Rhandirmwyn

Brechfa

Rheola

Mournes

Antrim

Sperrins

W. Fermanagh

E. Fermanagh

Priority areas forred squirrel conservationin the UK

Brownsea Island

Isle of Wight

Northumberland

North Tyne peripheryNorth Tyne

Durham, Tyne & Wear

North Cumbria

South Cumbria

Sefton Coast

ThetfordAberhirnant

Tywi

Crychan

Anglesey

Cynwyd Clocaenog

Nantyr

Cwm MynachCoed y Brenin

Cwrt

Rhandirmwyn

Brechfa

Rheola

Mournes

Antrim

Sperrins

W. Fermanagh

E. Fermanagh

Priority areas forred squirrel conservationin the UK

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