DOCSLIB.ORG

Nature Conservation

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Nature Conservation Nature Conservation Supplementary Planning Document (SPD) September 2016 Page 1 Nature Conservation Supplementary Planning Document Contact Information Robin Whitehouse Senior Planning Officer Tel: 01384 816810 Email: [email protected] Jo Bozdoganli Principal Planning Officer Tel: 01384 816489 E-mail: [email protected] Annette Roberts Planning Policy Manager Tel: 01384 814172 E-mail: [email protected] Helen Martin Head of Planning and Development Tel: 01384 814186 E-mail: [email protected] Postal Address: Strategic Planning and Historic Environment Service Planning and Development Place Directorate 4 Ednam Road Dudley West Midlands DY1 1HL Tel: 01384 814136 Email: [email protected] Page 2 Nature Conservation Supplementary Planning Document Contents Contact Information Tables 1– 4: Optimum Survey Times for Habitats and Specific Wildlife Species 1 – Introduction and Aims. 2 –Policy and Legislative Context 3 - Designated Nature Conservation Sites 4 – Identifying when a development proposal needs to be accompanied by an Ecological Survey 5 – Minimising unacceptable Nature Conservation impacts through Avoidance, Minimisation, Mitigation and Compensation 6 – A Step-by-Step guide to incorporating nature conservation and biodiversity enhancement features into new development proposals 7 – Good practice examples of nature conservation measures 8 – Geology and development (this chapter is taken directly from the 2006 Nature Conservation SPD as Geology was not subject to the 2016 review of SPD. Factual information, e.g. Policy Context, has been updated.) Appendices Appendix 1 – Key Planning Policies Appendix 2 – Suggested Content of Phase 1 Ecological Surveys Appendix 3 – List of Principal Native Trees, Shrubs and Climbers in keeping with the Local Character of Dudley (and link to non-native species) Appendix 4 –Nature Conservation Model Planning Conditions Appendix 5 – Hierarchy of designations Appendix 6 – Bibliography and references Appendix 7 - Glossary of Terms Page 3 Table 1 – Appropriate Survey Times for HABITATS Habitat type: Jan Feb March April May June July Aug Sep Oct Nov Dec Rivers, canals & ponds Appropriate timescale to undertake a Phase 1 Habitat Survey for this specific habitat type. Grassland & Marsh Reedbed and swamp Heathland Woodland & scrub Hedgerows General surveys: Site walkovers and scoping Site walkovers and scoping surveys (e.g. Habitat Survey assessments) can be undertaken at all times of year. surveys. Habitat survey assessments may highlight the need for more detailed surveys (e.g. Phase 1 Habitat Survey) to be undertaken which may be restricted to certain times of the year (see immediately above - optimum survey timescales for different habitat types). Assessing the potential of areas which could potentially have value for bat foraging and commuting habitat such as scrub and linear features such as hedgerows, fence lines, watercourses, woodland edges, field margins, etc can be undertaken at any time of year. Table 2 – Appropriate Survey Times for other ANIMAL AND PLANT SPECIES Page 4 Nature Conservation Supplementary Planning Document Species Jan Feb March April May June July Aug Sep Oct Nov Dec type: Birds Breeding Appropriate timescale to undertake a Phase 1 Survey for this specific animal species. Wintering Migratory Breeding bird species Survey time for migratory birds can extend to include June/July and August for Swifts. Perhaps even longer for such as House Martins and Swallows Swallows, Swifts and House Martins Reptiles Breeding Basking Great Breeding crested Habitat Appropriate timescale to undertake Phase 1 Survey: This type of survey can be undertaken until mid June (the newt survey period for ponds finishes in mid June) Habitat Appropriate time May to September when plant growth can be seen. Limited Habitat Suitability Index assessment can Suitability be carried out in other months. Index assessme nt for Great Crested Newts Page 5 Nature Conservation Supplementary Planning Document Badger Setts Habitat Water vole Presence Habitat Otter Presence Habitat Crayfish Luronium natans Lepidoptera Presence Habitat Date Waxcap, Olive Earthtongue and other significant fungi * Luronium natans – is a species of aquatic plant commonly known as the floating water-plantain. * Lepidoptera – is an order of insects that includes moths and butterflies. Page 6 Nature Conservation Supplementary Planning Document Table 3 –Appropriate Survey Times and assessment for BATS Type of bat survey or assessment: Jan Feb Mar April May June July Aug Sep Oct Nov Dec Winter Hibernation Survey including Appropriate Extend surveys of underground sites timescale to -ing undertake into Phase 1 survey. Inspection survey of existing buildings Appropriate timescale to undertake Phase 1 Survey: This type of survey can be undertaken all times of year and structures for presence of bat roosts. Roost assessment (trees/summer/winter) Appropriate timescale to undertake Phase 1 Survey: This type of survey can be undertaken all times of year Summer roosts survey Extend Appropriate timescale to -ing undertake Phase 1 survey. into Foraging and commuting habitat Extend Appropriate timescale to undertake Phase 1 survey (e.g. flight movements over green -ing survey. space areas, around woodland edges, into mature gardens, etc) Activity surveys (emergence from roost/ Appropriate timescale to undertake Phase 1 re-entry from roost/ transect) survey. Tree surveys for features used by Appropriate timescale to Extending into roosting bats (by observation from the undertake Phase 1 ground only) survey. Site walkovers and scoping surveys for Site walkovers and scoping surveys for bats can be carried out throughout the year. A site walkover & scoping bats survey may highlight the need for a more detailed survey (e.g. a Phase 1 Habitat Survey) to be undertaken which may be restricted to certain times of the year (see immediately above - optimum survey timescales) Inspection of bird and bat boxes for Appropriate timescale to undertake presence of roosting bats Phase 1 survey. Climbing tree surveys to assess Appropriate timescale to undertake Phase 1 features which have potential to be survey used by roosting bats Page 7 Nature Conservation Supplementary Planning Document Table 4 - Times of year that mitigation works can be undertaken specifically for BATS. (For example, if a bat roost is found within an existing building proposed for re-development/ demolition/ conversion and mitigation works need to be undertaken then the table below provides details of the timescales when the mitigation works can be undertaken for the specific bat roost type (e.g. summer or hibernation roost). Any mitigation works would need to be undertaken by a suitably qualified and experienced Ecological Consultant who is a licensed bat worker. Jan Feb Mar April May June July Aug Sep Oct Nov Dec Type of mitigation works: Mitigation works can be undertaken Timescale when mitigation works can be to a bat maternity and summer undertaken as bats will not be present in this type of roost environment during this Then from roosts until mid-May. timescale. the start of November. Mitigation works can be undertaken Timescale when mitigation works can be undertaken as bats will not be to a bat hibernation roost from present in this type of roost environment during this timescale. mid-March until the end of October. Bat roost mitigation can be a complicated process. Bat roost mitigation can be a complicated and project-specific process. Further guidance and examples of successful mitigation strategies can be found by referring to the Bat Conservation Trust and Government * websites. See Appendix 6 of this SPD. Further guidance and examples of successful mitigation strategies can be found by referring to the Bat Conservation Trust and Natural England web-sites. See Appendix 6 of this SPD. * All species of bats, their roosts and hibernation places are protected by United Kingdom and European Law. These places can include all sorts of buildings (new and old), bridges, trees and underground places. Page 8 Nature Conservation Supplementary Planning Document Table 5 – Optimal timescales for Badger Sett Closure and Artificial Sett Building Work Jan Feb Mar April May June July Aug Sep Oct Nov Dec Description: Timescale when Badger Sett Closure Sett Closure can take place. (1st July until 30th November) Artificial Artificial Badger Sett Building can take place throughout the year Sett Building Where a badger sett is present within a proposed development area it may be necessary to exclude badgers from a sett. A badger licence is required from Natural England to carry out such work. This licence should detail a method statement with mitigation and compensation measures. If a well-used sett is to be closed then it is likely an artificial sett will be required in compensation. Details of both sett closure and artificial sett building are provided above and below. Further information is also available from Natural England, the Badger Conservation Trust and information within Section 7 and Appendix 6 of this SPD. Page 9 Nature Conservation Supplementary Planning Document Badger Sett Closure Sett closure involves the installation of one-way badger gate across all holes of the sett and wire mesh across the surrounding area to prevent digging. The approach is to leave these gates open for the first seven days following installation to encourage badgers to leave the sett within these first days as the disturbance encourages them to move elsewhere. Following this
Load more

Recommended publications
  • A Literature Review of Urban Effects on Lowland Heaths and Their Wildlife
    Report Number 623 A literature review of urban effects on lowland heaths and their wildlife English Nature Research Reports working today for nature tomorrow English Nature Research Reports Number 623 A literature review of urban effects on lowland heaths and their wildlife J C Underhill-Day RSPB, Syldata Arne, Wareham Dorset BH20 5BJ Telephone: 01929 550969 email: [email protected] You may reproduce as many additional copies of this report as you like, provided such copies stipulate that copyright remains with English Nature, Northminster House, Peterborough PE1 1UA ISSN 0967-876X © Copyright English Nature 2005 Executive summary Introduction Heather clad lowland heath developed on light, freely draining, acid soils following prehistoric woodland clearance, and down the centuries, has been kept open by grazing, burning and cutting. As the economic value of these uses declined, considerable areas of heath were lost to agriculture, forestry, housing, roads, mineral working and other uses, and today, much of what is left is adjacent to built up areas, especially in Dorset. These lowland heathland fragments can be found across much of southern England on suitable soils. Much of the research on heathlands over the last twenty years has concentrated on the Dorset heaths, which are now almost all SSSIs and mostly within the Dorset Heathland SPA. While this report reflects the bias in the literature towards work in Dorset, the results have wide applicability to urban heathlands that are accessed by the surrounding urban populations for amenity and recreation whether in Dorset or elsewhere. This urban public access places considerable pressures on the heaths, for example through disturbance, wild fires, trampling, predation by domestic pets, pollution and enrichment.
    [Show full text]
  • Common Standards Monitoring Guidance for Lowland Heathland
    Common Standards Monitoring Guidance for Lowland Heathland Version February 2009 Updated from (February 2004) ISSN 1743-8160 (online) CSM Guidance for Lowland heathland Issue date: February 2009 Common Standards Monitoring Guidance for Lowland heathland 1 Introduction 1.1 Lowland heathland in England, Wales and Northern Ireland comprises a range of habitats characterised by the abundance of ericoids or gorse species. It occurs on generally nutrient-poor soils, usually below 300 m. Heathland in Scotland is rarely defined as lowland heathland; most Scottish heathland occurs above the upper limits of agricultural enclosure. However, some forms of heathland at low altitudes, similar in character to those in England, Wales and Northern Ireland and usually within the enclosed part of the landscape, do occur in Scotland, although mostly as small fragments. The most distinctive and extensive are the coastal heaths. 1.2 Lowland heathland includes dry, wet, humid, chalk/limestone, coastal and lichen heaths, and all successional stages from bare ground to shrubs. See Annex 1 for a full definition for CSM purposes of lowland heathlands in terms of components, Phase 1 habitat survey classes, NVC types and Annex I (Habitats Directive) equivalents, and section 2 below for more detailed descriptions. 1.3 Guidance on monitoring is summarised in table 1 (lowland dry heath) and table 2 (lowland wet heath). Upland heathland is covered by separate guidance, but the distinction between upland and lowland examples may sometimes be difficult. Heath vegetation on maritime cliff/slopes and dune heath are both included within the lowland heathland guidance but assessment of these types should be done in conjunction with the relevant coastal guidance section.
    [Show full text]
  • Lowland Heathland and Lowland Dry Acid Grassland in Oxfordshire
    LOWLAND HEATHLAND AND LOWLAND DRY ACID GRASSLAND IN OXFORDSHIRE UK Biodiversity Group - Priority Species associated with heathland 1. INTRODUCTION Nightjar Lowland heathland is characterised by the presence of species Linnet such as heather, bell heather, and gorse, and it is associated with Dingy mocha moth acidic, nutrient-poor soils. Acid grassland also occurs on Grey scalloped bar moth, nutrient-poor soils and is characterised by species such as common bent, sheep’s sorrel, heath bedstraw and tormentil. Parched acid grassland, which becomes excessively dry in Other Associated Species summer, may support a number of uncommon, ephemeral Tree pipit species, such as small cudweed. Stonechat Emperor moth Heathland and acid grassland are formed when forests on nutrient poor soils are cleared for agriculture. It requires White-line snout moth management to check scrub invasion and the subsequent Small red damselfly development of woodland, and to keep the nutrient content of Adder the soil low. In the past this management took the form of grazing, burning and gathering of heather and gorse, for such Blue fescue uses as fuel and thatch. Heathland is not only an important Heath cudweed habitat for wildlife but also forms a valuable part of the cultural Heather heritage of the U.K. Bell heather In Oxfordshire, heathland and acid grassland were never very Sphagnum mosses common and are now very rare habitats largely restricted to the sandy soils on the Corallian sandstone (where it forms a grassy Associated Habitats ‘Breckland’ type heath) and the clay-with-flints and pebbly Woodlands soils of the Chilterns plateau (where heather forms a mosaic with acid grassland).
    [Show full text]
  • Lowland Heathland and Dry Acid Grassland
    NORFOLK BIODIVERSITY ACTION PLAN Ref 1/H6 Tranche 1 Habitat Action Plan 6 Plan Author: Norfolk County Council LOWLAND HEATHLAND AND DRY ACID Plan Co-ordinator: Heathland BAP Topic GRASSLAND Group The UK BAP identifies heathland as consisting Plan Leader: Norfolk County of “an ericaceous layer of varying heights and Council structures, some areas of scattered trees and Date: Stage: scrub, areas of bare ground, gorse, wet heaths, 31 December 1998 Version 1 bogs and open water”. In Norfolk, heathland is April 2004 Version 2 much more of a mosaic, with acid grassland and 17 November 2011 Version 3 bracken often being significant elements. Even more distinctive are the heaths of the Brecks which include chalk grassland and little or no heather. In East Anglia, the typical lowland acid grassland community is NVC U1, comprising sheep’s-fescue Festuca ovina, common bent Agrostis capillaris and sheep’s sorrel Rumex acetosella. Other species may include wavy hair-grass Deschampsia flexuosa, heath bedstraw Galium saxatile and tormentil Potentilla erecta. 1., CURRENT STATUS National Status In England, only a sixth of the heathland present in 1800 now remains. The UK has about 95,000 ha of lowland heathland (58,000 ha of which are in England) representing about 20% of the international total of this habitat. As with other lowland semi-natural grassland types, acid grassland underwent substantial declines in the 20th century. Although there are no figures available on the current rate of loss, it is thought to be slowing. The decline is primarily the result of under-management, specifically under-grazing and abandonment.
    [Show full text]
  • East Devon Pebblebed Heaths Providing Space for Nature Biodiversity Audit 2016 Space for Nature Report: East Devon Pebblebed Heaths
    East Devon Pebblebed Heaths East Devon Pebblebed Providing Space for East Devon Nature Pebblebed Heaths Providing Space for Nature Dr. Samuel G. M. Bridgewater and Lesley M. Kerry Biodiversity Audit 2016 Site of Special Scientific Interest Special Area of Conservation Special Protection Area Biodiversity Audit 2016 Space for Nature Report: East Devon Pebblebed Heaths Contents Introduction by 22nd Baron Clinton . 4 Methodology . 23 Designations . 24 Acknowledgements . 6 European Legislation and European Protected Species and Habitats. 25 Summary . 7 Species of Principal Importance and Introduction . 11 Biodiversity Action Plan Priority Species . 25 Geology . 13 Birds of Conservation Concern . 26 Biodiversity studies . 13 Endangered, Nationally Notable and Nationally Scarce Species . 26 Vegetation . 13 The Nature of Devon: A Biodiversity Birds . 13 and Geodiversity Action Plan . 26 Mammals . 14 Reptiles . 14 Results and Discussion . 27 Butterflies. 14 Species diversity . 28 Odonata . 14 Heathland versus non-heathland specialists . 30 Other Invertebrates . 15 Conservation Designations . 31 Conservation Status . 15 Ecosystem Services . 31 Ownership of ‘the Commons’ and management . 16 Future Priorities . 32 Cultural Significance . 16 Vegetation and Plant Life . 33 Recreation . 16 Existing Condition of the SSSI . 35 Military training . 17 Brief characterisation of the vegetation Archaeology . 17 communities . 37 Threats . 18 The flora of the Pebblebed Heaths . 38 Military and recreational pressure . 18 Plants of conservation significance . 38 Climate Change . 18 Invasive Plants . 41 Acid and nitrogen deposition. 18 Funding and Management Change . 19 Appendix 1. List of Vascular Plant Species . 42 Management . 19 Appendix 2. List of Ferns, Horsetails and Clubmosses . 58 Scrub Clearance . 20 Grazing . 20 Appendix 3. List of Bryophytes . 58 Mowing and Flailing .
    [Show full text]
  • 17. Lowland Heathland
    CONTENTS © Natural England/Bob Gibbons Dorset heaths 17. Lowland heathland Climate Change Sensitivity: Medium 135 Climate Change Adaptation Manual Evidence to support nature conservation in a changing climate CONTENTS Introduction Lowland Heathland is sensitive to changes in hydrological conditions and the frequency of fires that may result from higher temperatures and more frequent droughts. Coastal and dune heathlands may be lost if sea levels rise significantly. Warmer temperatures could cause grass species to become more dominant as a result of increased nutrient availability, leading to a shift from heathland to acid grassland. Some heathland species currently restricted to southern England are likely to benefit from climate change, including the Dartford warbler which has already expanded its range. The fragmented nature of many heathland sites will increase their vulnerability to climate change. Heathland is also sensitive to potential indirect impacts of climate change such as increased recreational pressure, and extreme weather events such as flooding will impact on the ability to undertake restoration and maintenance work in the winter. Habitat Description Lowland heath developed following prehistoric woodland clearance, and has been kept open through the centuries by grazing, burning and cutting. As the economic value of these uses declined, a considerable area of heath was lost to agriculture, forestry, housing, mineral working and other uses. Heathland is described as a broadly open landscape on impoverished, acidic mineral and shallow peat soil, which is characterised by the presence of heathers and gorses at a cover of at least 25%. It includes both wet and dry heath, usually below 250 metres. Lowland heath grades into upland heath but is defined by the upper limit of agricultural enclosure and typically supports a range of birds, reptiles and invertebrates not found on upland heath.
    [Show full text]
  • Lowland Heathland
    UK Biodiversity Action Plan for Lowland Heathland Current Status Lowland heathland is characterised by the presence of plants such as heather, dwarf gorses, and cross- leaved heath and is generally found below 300 metres in altitude. Areas of good quality heathland should consist of an ericaceous layer of varying heights and structures, some areas of scattered trees and scrub, areas of bare ground, gorse, wet heaths, bogs and open water. The presence and numbers of characteristic birds, reptiles, invertebrates, vascular plants, bryophytes and lichens are important indicators of habitat quality. Lowland heathland is a priority for nature conservation because it is a rare and threatened habitat. In England only one sixth of the heathland present in 1800 now remains. The UK has some 58,000 ha of lowland heathland of which the largest proportion (55% ) is found in England. The most significant areas for lowland heathland include the counties of Hampshire, Cornwall, Dorset, Surrey, Devon, Staffordshire, Suffolk, Norfolk, Pembrokeshire, West Glamorgan and west Gwynedd. The UK has an important proportion (about 20%) of the international total of this habitat. Current factors affecting the habitat In the past heathland was lost primarily to agriculture, forestry, mineral extraction and development. Uncontrolled burning has also been a particular threat to bryophyte and lichen-rich heathland. The main factors affecting the habitat at present are: • Encroachment of trees and scrub and the simplification of vegetation structure due to a lack of conservation management such as light grazing, controlled burning and cutting. • Nutrient enrichment, particularly deposition of nitrogen compounds emitted from intensive livestock farming, or from other sources.
    [Show full text]
  • Region 3 North-East Scotland: Cape Wrath to St. Cyrus
    Coasts and seas of the United Kingdom Region 3 North-east Scotland: Cape Wrath to St. Cyrus edited by J.H. Barne, C.F. Robson, S.S. Kaznowska, J.P. Doody & N.C. Davidson Joint Nature Conservation Committee Monkstone House, City Road Peterborough PE1 1JY UK ©JNCC 1996 This volume has been produced by the Coastal Directories Project of the JNCC on behalf of the project Steering Group JNCC Coastal Directories Project Team Project directors Dr J.P. Doody, Dr N.C. Davidson Project management and co-ordination J.H. Barne, C.F. Robson Editing and publication S.S. Kaznowska, J.C. Brooksbank, F.J. Wright Administration & editorial assistance C.A. Smith, R. Keddie, E. Leck, S. Palasiuk, J. Plaza, N.M. Stevenson The project receives guidance from a Steering Group which has more than 200 members. More detailed information and advice comes from the members of the Core Steering Group, which is composed as follows: Dr J.M. Baxter Scottish Natural Heritage R.J. Bleakley Department of the Environment, Northern Ireland R. Bradley The Association of Sea Fisheries Committees of England and Wales Dr J.P. Doody Joint Nature Conservation Committee B. Empson Environment Agency Dr K. Hiscock Joint Nature Conservation Committee C. Gilbert Kent County Council & National Coasts and Estuaries Advisory Group Prof. S.J. Lockwood MAFF Directorate of Fisheries Research C.R. Macduff-Duncan Esso UK (on behalf of the UK Offshore Operators Association) Dr D.J. Murison Scottish Office Agriculture, Environment and Fisheries Department Dr H.J. Prosser Welsh Office Dr J.S. Pullen WWF UK (Worldwide Fund for Nature) N.
    [Show full text]
  • Restoration Management Plan
    BIFFA WASTE SERVICES ATTLEBRIDGE LANDFILL SITE REEPHAM ROAD, ATTLEBRIDGE, NORFOLK RESTORATION MANAGEMENT PLAN October 2016 bright & associates landscape and environmental consultants CONTENTS 1. INTRODUCTION ............................................................................... 1 1.1. PREFACE ................................................................................................... 1 1.2. APPOINTMENT AND SCOPE OF WORK ................................................... 1 1.3. DEFINITIONS ............................................................................................. 2 2. CURRENT SITE SITUATION ........................................................... 3 2.1. SITE REVIEW (AUGUST 2016) .................................................................. 3 2.2. AREAS 1 TO 11 .......................................................................................... 3 3. FUTURE RESTORATION MANAGEMENT ..................................... 4 DRAWINGS Drawing No. AT1073-D1v2, (Computer Ref. A5039001), Current Situation (2016) and Direct Management Actions APPENDICES Appendix 1 Modifications to the Approved Restoration Scheme and Submission of Restoration Management Plan, prepared by Bright & Associates for Biffa Waste Services, December 2012 Biffa Waste Services Attlebridge Landfill Site, Norfolk, Restoration Management Plan (dated October 2016) 1. INTRODUCTION 1.1. PREFACE 1.1.1. Attlebridge Landfill (the Site) is located c.2.5km north-west of the village of Taverham in Norfolk and is operated by Biffa Waste Services
    [Show full text]
  • County Wildlife Sites Criteria for Cornwall
    Heading County Wildife Site Criteria for Cornwall Environmental Records Centre for Cornwall and the Isles of Scilly Acknowledgements We are very grateful to all those who provided comments during the production of this document. We are very lucky in Cornwall to have so many deeply committed, skilled and knowledgeable recorders and wildlife enthusiasts. ERCCIS and Cornwall Wildlife Trust (2010) County Wildlife Site criteria for Cornwall Written by Paul McCartney Edited by Victoria Whitehouse, Cheryl Marriott and Fay Robinson Designed by Sheila McCann-Downes Drawings by Sarah McCartney Photography by Liz Cox, Alex Howie, Sheila McCann-Downes Copies can be obtained from: ERCCIS c/o Cornwall Wildlife Trust Five Acres Allet Truro TR4 9DJ [email protected] County Wildife Site Criteria for Cornwall Page ii COUNTY WILDLIFE SITE CRITERIA FOR CORNWALL CONTENTS 1 Introduction 1 2 Context and Background 2 2.1 Cornwall’s Biological Heritage 2 2.2 Sites of National and International Importance 2 2.3 Sites of Local Importance 3 2.4 Background to County Wildlife Sites in Cornwall 3 3 County Wildlife Site Selection 4 3.1 The Role of Ratcliffe’s Primary and Secondary Attributes 4 3.1.1 Application of Ratcliffe’s Primary Attributes 5 3.1.2 Application of Ratcliffe’s Secondary Attributes 6 3.2 Guiding Principles for County Wildlife Site Selection 7 3.3 Procedures for County Wildlife Site Selection 8 3.4 Site Boundaries 9 4 Criteria for County Wildlife Site Selection in Cornwall 10 4.1 Criteria for BAP Priority Habitats 12 4.2 Criteria for Local
    [Show full text]
  • Local Biodiversity Action Plan
    Tunbridge Wells Local Biodiversity Action Plan Part 2 – Proposed Actions October 2008 Tunbridge Wells Borough Local Biodiversity Action Plan – Part 2 Objectives And Actions INTRODUCTION This part of the Local Biodiversity Action Plan (LBAP) sets out the overall Objectives and Actions of the Plan to support the LBAP as a whole as well as specific Objectives and Actions for each of the identified habitats. All will be reviewed annually by the LBAP Steering Group to monitor progress and consider changes with a full review of the whole plan in 5 years. The Actions are naturally focused on the works of Tunbridge Wells Borough Council and its close partners but should not been seen as exhaustive and will compliment work being carried out elsewhere by the Council and others. It is hoped that the actions and partners listed will expand as the partnerships strengthens overtime but it is not the intention of this plan to list all actions of all partners. The Actions proposed should be taken as a guide only and should not prevent the Council or partners taking advantage of unforeseen opportunities that support the habitat objectives or other wider biodiversity objectives. A number of Actions have very specific targets or are part of ongoing work but some are indicative of potential future projects being dependant upon internal and/or external funding or partnership projects but can also be used to influence others. These potential future projects will be actively investigated during the coming year to see if they can be turned into specific actions. Mapping is provided for some habitats under Detailed Habitat Information but this is provisional only as much of the data is incomplete or requires more detailed investigations.
    [Show full text]
  • A Field Survey to Evaluate the Outcome of Higher Level Stewardship Options on Lowland Heathland
    Natural England Commissioned Report - ESME Heathland Project A field survey to evaluate the outcome of Higher Level Stewardship options on lowland heathland A report to Natural England June 2017 Dr Eleanor Hewins Hewins Ecology Dr Giles Groome Ecological Consultant Jon Mellings Ecological Consultant Dr Isabel Alonso Natural England – Project management Natural England Commissioned Report - ESME Heathland Project Natural England is responsible for delivering a programme of monitoring and evaluation, working closely with Defra, the Forestry Commission, the Environment Agency and Historic England to meet the requirements of schemes delivered and funded through the Rural Development Programme for England (RDPE). The Heathland ESME project was part of this programme. Natural England Commissioned Report - ESME Heathland Project Contents Executive summary .......................................................................................................................................... 7 1 Introduction ............................................................................................................................................. 9 Background .............................................................................................................................................. 9 Project aims ............................................................................................................................................ 10 2 Methods ................................................................................................................................................
    [Show full text]