natural capital, ecosystem services and local ...q1a q1b upland heathland p1b mountain heaths and...
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Copyright © eCountability Ltd 2017www.ecountability.co.uk
1© Alister Hayes
Natural Capital, Ecosystem Services and Local Environmental Records Centres
Jo Treweek/Bill Butcher eCountability Ltd
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Acknowledgements
The whole of this document is copyrighted material © eCountability 2017, included subsets and derivations as described below.
Slides in this presentation were based on data and interpretation supplied by:
Greenspace Information for Greater London CICEcoRecordSussex Biodiversity Records CentreThe Wildlife Centre for Lothian and the Borders LERCMersey ForestForest ResearchALERCBrighton and Hove CouncilEdinburgh City Council
Maps include Data ©OpenStreetMap contributors Data available under the Open Database Licence; Maps include OS Open data, provided under the Open Government Licence, Contains OS data © Crown copyright and database right (2016)SPADES® was developed by eCountability Ltd with a funding contribution from Innovate-UK, the UK’s Innovation Agency.Population Data: © OpenPopGrid, 2015. This product contains information from several Information Providers under Open Government Licence and Ordnance Survey OpenData Licence (http://openpopgrid.geodata.soton.ac.uk/Openpopgrid.xml).Air quality data: © London Atmospheric Emissions Inventory, 2013, Greater London AuthoritySoils data: ‘Soils Data © Cranfield University (NSRI) and for the Controller of HMSO [2017]’London Case Study: based on data supplied by Build UK partners.Modelling approaches developed by Forest Research based on data supplied by Sussex, Wiltshire, London and Greater Manchester LERCs.Photographs in slides 1 and 41 © Alister HayesSlides 7 & 8 are reproduced from the WBCSD website of the Natural Capital Coalition.Slide 11 Green Infrastructure Typology developed by GiGL CIC & eCountability with contributions from SPADES®project partners and Local Authorities.Slide 14 The UK Hab developed by the UK Hab Working Group: Bill Butcher, Jo Treweek, Peter Carey, Lisa Norton, Bob EdmondsSlides 15 & 16 are © Chloe Bellamy, Andrew Rattey (Forest Research), Tom Hunt (ALERC), Alexander van der Jagt (University of Utrecht), Bill Butcher & Jo Treweek (eCountability Ltd).
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Natural Capital, Ecosystem Services and
Local Environmental Records Centres
View of natural capital/ ecosystem services from the consultancy sector
Development of a Spatial Decision Support Tool for assessment of Ecosystem Services impacts of developments
Role of LERCs as Key Data Providers / future needs
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Natural Capital and Ecosystem Services
Natural Capital - the stock of living and non-living environmental resources potentially available to generate value.
Ecosystem Services - the flow of benefits that this stock provides.
Natural capital is about nature’s assets, whilst ecosystem services are the goods and services derived from those assets by particular users or beneficiaries.
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Flow of services to beneficiaries
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Natural Capital Protocol
The Natural Capital Protocol is a framework designed to help generate trusted, credible, and actionable information for business managers to inform decisions.
The Protocol aims to support better decisions by including how we interact with nature, or more specifically natural capital.
The protocol sets out stages and steps for natural capital assessment.
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www.naturalcapitaltoolkit.org
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Road and tracksRoadside (manmade)Roadside (unknown)Parking/loading
Tidal waterForeshore/rocks
RailwayPath
Commercial/InstitutionalResidentialGlasshousesAirportsOther structures
Public park and garden
Private gardensSchool groundsInstitutional grounds
Amenity – residentialAmenity – businessAmenity - transport
Play space
Playing fieldsGolf coursesTennis courtsBowling greensOther sports
Green access routesRiparian routes
WoodlandOpen semi-naturalOpen water
Allotments & community growing areaChurchyardCemetery
Other functional greenspace
Civic space
FarmlandMoorlandOther
ChangeNot GI
Agricultural land
Allotment, community garden or urban farm
Cemetery, churchyard or burial ground
Coastal habitat
Derelict land
General amenity space
Grassland, heathland, moorland or scrubland
Green roof
Institutional ground
Orchard
Outdoor sports facility
Park or public garden
Street treesWater body
Water course
Wetland
ParkFormal garden
CommonCountry parkPrivate woodlandPublic woodlandNature reserve
Railway cuttingDisused railway trackbedRoad island/vergeWalking/cycling route
Recreation groundPlaying fieldGolf courseOther recreational
Amenity green spaceLandscaping around premises
RiverCanal
Play spaceAdventure playgroundYouth area
AllotmentsCommunity gardenCity farm
Cemetery/churchyard
Equestrian centreAgricultureNursery/horticulture
Sewage/water worksDisused quarryVacant landLand reclamationOther Village green
HospitalEducationalReservoir
Parks and gardens
Privately owned parks and gardens
Natural and semi natural urban greenspace
Amenity greenspace
Green corridor
Outdoor sports facilities
Golf course
Race course
School ground and sports pitches
Children and young people
Allotments and urban farms
Community gardens
Cemeteries
Civic spaces
Countryside
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Liverpool
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Brighton
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UK Hab: A Coherent Habitat Classification for the UK The Need
A system that….❖ Includes all semi-natural and anthropogenic habitats to
meet national and local planning needs❖ Allows consistent, accurate data collection and multiple
re-use❖ Allows choice of hierarchical levels, from ecosystems to
detailed categories, according to survey purpose❖ Designed for local, national and international reporting❖ Designed for GIS from the outset❖ Saves time and information loss by avoiding the need
to translate between classifications❖ Can be linked to condition monitoring
Major
eco-
system
category
(level 1)
Ecosystem type for mapping and
assessment (level 2)
Level 2
code
Level 3 habitats - Broad
Habitats
Leve
l 3 co
de
Level 4 Habitats including
Priority Habitats
Leve
l 4 co
de
Level 5 Habitats including
Annex 1 Habitats
Leve
l 5 co
de
Inland dunes with open Corynephorus and
Agrostis grasslands k1a5
Other lowland dry acid grassland k1a6
Siliceous Alpine and Boreal grassland k1b5
Other upland acid grassland k1b6
Bracken k1cSemi-natural dry grasslands and scrubland
facies on calcareous substrates [Festuco-
Brometalia] [lowland] k2a5Semi-natural dry grasslands and scrubland
facies on calcareous substrates [Festuco-
Brometalia] [important orchid sites] k2a6
Alpine and subalpine calcareous grasslands k2b5Species-rich Nardus grassland on siliceous
substrates in mountain areas k2b6Semi-natural dry grasslands and scrubland
facies on calcareous substrates [Festuco-
Brometalia] [upland] k2b7
Lowland meadows k3aLowland hay meadows [Alopecurus pratensis;
Sanguisorba officinalis] k3a5
Upland hay meadows k3b Mountain hay meadows k3b5
Other neutral grassland k3c
Improved grassland k4
Upland oakwood m1aOld sessile oak woods with Ilex and
Blechnum in the British Isles m1a5
Tilio-Acerion forests of slopes; screes and
ravines m1b5
Other upland mixed ashwoods m1b6
Atlantic acidophilous beech forests with Ilex
and sometimes also Taxus in the shrublayer
(Quercion robori-petraeae or Ilici-Fagenion) m1c5
Asperulo-Fagetum beech forests m1c6
Taxus baccata woods of the British Isles m1c7
Stable xerothermophilous formations with
Buxus sempervirens on rock slopes
(Berberidion p.p.) m1c8
Alluvial forests with Alnus glutinosa and
Fraxinus excelsior (Alno-Padion; Alnion
incanae; Salicion albae) m1d5
Bog woodland m1d6
Upland birchwoods m1eOld acidophilous oak woods with Quercus
robur on sandy plains m1f5
Sub-Atlantic and medio-European oak or oak-
hornbeam forests of the Carpinion betuli m1f6
Other Lowland mixed deciduous woodland m1f7
Atlantic hazel m1gDense scrub m1h5
Line of trees m1h6
Other broadleaved woodland types m1h7
Other woodland; mixed; mainly broadleaved m1j5
Other woodland; mixed; mainly conifer m1j6
Native pine woodlands m2a Caledonian forest m2a5
Other Scot's Pine woodland m2b
Other coniferous woodland m2cEuropean dry heaths [lowland] p1a5
Dry Atlantic coastal heaths with Erica vagans p1a6
Northern Atlantic wet heaths with Erica
tetralix [lowland] p1a7
Temperate Atlantic wet heaths with Erica
ciliaris and Erica tetralix p1a8
European dry heaths [upland] p1b5
Northern Atlantic wet heaths with Erica
tetralix [upland] p1b6
Alpine and boreal heaths p1c5
Sub-Arctic Salix spp. scrub p1c6
Hedgerow (priority habitat) p2a
Other hedgerows p2bBlanket bog (H7130) q1a5
Degraded blanket bog q1a6
Active raised bogs q1b5
Degraded raised bogs still capable of natural
regeneration q1b6
Other degraded raised bog q1b7
Reedbeds q2aCalcareous fens with Cladium mariscus and
species of the Carex davallianae q2b5
Petrifying springs with tufa formation
[Cratoneurion] q2b6
Alkaline fens q2b7
Transition mires and quaking bogs [lowland] q2b8
Depressions on peat substrates
(Rhynchosporion) q2b9
Purple moor grass and rush
pastures [Molinia-Juncus] q2cMolinia meadows on calcareous; peaty or
clayey-silt-laden soils [Molinia caeruleae] q2c5
Alpine pioneer formations of Caricion
bicoloris-atrofuscae q2d5
Transition mires and quaking bogs [upland] q2d6
Aquatic marginal vegetation q2e
Arable field margins r1a
Grass and grass-clover leys r1b
Cereal crops r1c
Non-cereal crops including
woody crops r1d
Intensive orchards r1e
Horticulture r1f
Open Mosaic Habitats on
Previously Developed Land s1aBuildings s1b5
Other developed land s1b6
Artificial unvegetated,
unsealed surface s1c
Suburban/ mosaic of
developed/ natural surface s1d
Built linear features s1eSiliceous scree of the montane to snow levels
(Androsacetalia alpinae and Galeopsietalia
ladani) t1a5
Calcareous and calcschist screes of the
montane to alpine levels (Thlaspietea
rotundifolii) t1a6
Calcareous rocky slopes with chasmophytic
vegetation t1a7
Siliceous rocky slopes with chasmophytic
vegetation t1a8
Hydrophilous tall herb fringe communities of
plains and of the montane to alpine levels t1a9
Limestone pavement t1b Limestone pavement (H8240) t1b5
Calaminarian grasslands t1cCalaminarian grasslands of the Violetalia
Calaminariae t1c5
Vegetated sea cliffs of the Atlantic and Baltic
coasts t2a5
Soft rock sea cliffs t2a6
Embryonic shifting dunes t3a5
Shifting dunes along the shoreline with
Ammophila arenaria ["white dunes"] t3a6
Fixed coastal dunes with herbaceous
vegetation ["grey dunes"] t3a7
Decalcified fixed dunes with Empetrum
nigrum t3a8
Atlantic decalcified fixed dunes [Calluno-
Ulicetea] t3a9
Humid dune slacks t3a?
Perennial vegetation of stony banks t3b5
Annual vegetation of drift lines t3b6
Natural eutrophic lakes with Magnopotamion
or Hydrocharition-type vegetation u1a5
Other eutrophic standing waters u1a6
Mesotrophic lakes u1bHard oligo-mesotrophic waters with benthic
vegetation of Chara spp. u1b5
Oligotrophic to mesotrophic standing waters
with vegetation of the Littorelletea uniflorae
and-or the Isoeto-Nanojuncetea u1c5
Oligotrophic waters containing very few
minerals of sandy plains (Littorelletea
uniflorae) u1c6
Aquifer fed naturally
fluctuating water bodies u1d
Ponds (priority habitat) u1e
Other ponds u1f
Lowland rivers with shallow
gradients and rich geology u2a
Water courses of plain to montane levels
with the Ranunculion fluitantis and Callitricho-
Batrachion vegetation u2a5
Meso-eutrophic rivers
flowing predominantly over
sandstone and hard
limestone u2b
Mesotrophic and oligo-
mesotrophic rivers u2c
Acid and nutrient-poor rivers u2d
Other rivers and streams u2e
Intertidal chalk v1a
Sabellaria alveolata reefs v1b
Intertidal underboulder
communities v1c
Estuarine rocky habitats v1d
Splash zone with lichens v1eSalicornia and other annuals colonising mud
and sand v2a5
Spartina swards [Spartinion maritimae] v2a6
Atlantic salt meadows [Glauco-
Puccinellietalia maritimae] v2a7
Mediterranean salt meadows [Juncetalia
maritima] v2a8
Mediterranean and thermo-Atlantic
halophilous scrubs [Sarcocornetea fruticosi] v2a9
Blue mussel beds on
sediment v2b
Seagrass beds [Zostera noltii] v2c
Intertidal mudflats v2dMudflats and sandflats not covered by sea
water at low tide v2d5
Sheltered muddy gravels v2e
Peat and clay exposures with
piddocks v2f
Saline lagoons v2g
Beach v2h
Coastal w
Coastal waters x
Shelf y
Open ocean z
p1a
Broadleaved mixed and
yew woodlandm1
k1a
Upland acid grassland k1b
Calcareous grassland k2
Lowland calcareous
grasslandk2a
Upland calcareous grassland k2b
Acid grassland k1
Lowland dry acid grassland
Upland mixed ashwoods m1b
Lowland beech and yew
woodlandm1c
Wet woodland m1d
Lowland mixed deciduous
woodlandm1f
m1h
Blanket bog
Lowland raised bog
Fen, marsh and swamp q2
Other woodland - mixed m1j
Other woodland -
broadleaved
Coniferous woodland m2
Lowland fens q2b
Upland flushes, fens and
swampsq2d
q1a
q1b
Upland Heathland p1b
Mountain heaths and willow
scrubp1c
Hedgerows p2
Dwarf shrub heath p1
Lowland Heathland
Heathland and shrub p
Woodland and forest m
s1
Sparsely vegetated
landt
Inland rock t1
Supralittoral Sediment t3
sBuilt-up areas and
gardens
Cropland r Arable and horticulture r1
Wetland q
Bog q1
Developed land - sealed
surfaces1b
Coastal sand dunes t3a
Coastal vegetated shingle t3b
Fre
sh w
ate
r
Rivers and lakes u
Standing open water
and canalsu1
Eutrophic standing waters
Terr
est
rial
Grassland k
Neutral grassland k3
Inland rock outcrop and
scree habitatst1a
Supralittoral Rock t2 Maritime cliff and slopes t2a
Urban
u1a
Oligotrophic and dystrophic
lakesu1c
Rivers and streams u2
Littoral Sediment v2
Littoral Rock v1
Ma
rin
e
Marine inlets and
transitional waters
(Classification at levels
3, 4 and 5 yet to be
developed for these
marine ecosystems)
v
Coastal saltmarsh v2a
Hierarchy and Coding❖ Habitat polygons are created and given a primary
code following the hierarchy❖ Secondary codes can be added to each polygon❖ Secondary codes include habitat complexes,
origin, management, land use, environmental qualifiers, species features, and green infrastructure features.
❖ Currently there are over 250 secondary codes that can be applied
Advantages over current systems
❖ Fits national reporting requirements by identifying all Priority Habitats (now Habitats of Principal Importance in England) and Annex I habitats in the UK
❖ Totally objective hierarchy❖ Provides contextual information through secondary
codes❖ Designed to be used in a database and GIS environment❖ Can be translated into other habitat classifications
readily
Ease of Use❖ Simple coding system designed to be memorable❖ Switch from Phase 1 should be fast❖ Top levels of hierarchy do not require high level of
botanical expertise❖ A habitat key and field manual to aid correct
identification and allocate all appropriate secondary codes
TimelineWinter 16/17 Analysis of feedback from Implementation Panel and fieldworkWinter 16/17 Development of field key and manual version 1Late Spring 17 Draft system for use in the field by all interestedAutumn 17 Feedback from usersWinter 17/18 Incorporation of feedbackSpring 18 Final online publication
Recognition❖ By working with CIEEM, JNCC, NE, SNH, NRW, DoENI,
LERCs and NBN Trust we aim to achieve ‘approved status’.
❖ The system can also be translated to other classifications in use.
❖ Ultimately it should be adopted as the recognised habitat classification in the UK.
Bill Butcher and Jo Treweek (eCountability)Lisa Norton (Centre for Ecology and Hydrology)Bob Edmonds (SLR Consulting Ltd)Pete Carey (Bodsey Ecology Limited)
CIEEM Member Feedback168 Members responded to an open questionnaire
Photo by permission of SLR Consulting Ltd
Photo: Pete Carey
UK HAB: s1a Open mosaic habitats on previously developed land
UK HAB: t1b Limestone pavement
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Collaboration between research community, consultancies and LERCs
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Modelling using LERC Data
®
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The Confluence Model
Demand
Supply
Use
When expressed spatially: • Use is the intersection of demand and supply • Deficit is where demand exceeds supply and • Current Redundancy is where supply currently exceeds demand
SPADES® uses the Confluence Model for Access to Nature, Recreation and Air Quality services.
Hegetschweiler et al (2017)
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Access to Nature –Brighton Case Study
Principal Benefits of this service:
Mental Health
Principal Beneficiaries of this service:
Residents
Health services
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Air Quality –Case Study, London
Principal Benefits of this service:
Physical Health(Mortality and Morbidity, Respiratory Disease)
Principal Beneficiaries of this service:
Residents in and near the development
Health services
Employers
Developers
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Surface Runoff –Case Study, London
Principal Benefits of this service:
Reduction of surface flooding risk
Principal Beneficiaries of this service:
Residents in and near the development.
Developers
Local drainage authorities
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Urban Temperature Liverpool Case Study
Principal Benefits of this service:
Physical Health (Mortality)
Principal Beneficiaries of this service:
Residents in and near the development.
Health services
Employers
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Net Gain Objective for Natural Capital
Source: Natural Capital Committee
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LERCs and Natural Capital
• Partnerships with organisations and volunteers at local level ESSENTIAL to generate quality data for assessments
• Patching together variable national datasets does not generate result of adequate quality
• Species and habitat data needed
• Need to adopt national standards, while encouraging local innovation
• Collaboration potential with researchers and consultancies for powerful modelling based on LERC data
• Potential for new LERC income streams to fund improved data collection & collation
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41© Alister Hayes
Natural Capital, Ecosystem Services and Local Environmental Records Centres
Jo Treweek/Bill Butcher eCountability