Select Committee on Environmental Audit Minutes of Evidence


Memorandum by the Department for Environment, Food and Rural Affairs (Defra)

INTRODUCTION

  1.  This Memorandum sets out Defra's responses to the questions identified by the Committee for its inquiry into halting UK biodiversity loss. It is written from a UK perspective except in the case of devolved matters, where it is written from an England perspective.

POLICY AND PROGRESS

Q1  Is the Government on course to meet its 2010 biodiversity target?

  2.  There are two main targets. In 2001, EU Heads of Government adopted the target that "biodiversity decline should be halted with the aim of reaching this objective by 2010". In 2002, the UN World Summit on Sustainable Development endorsed the target agreed five months earlier by the Parties to the Convention on Biological Diversity (CBD) "to achieve by 2010 a significant reduction of the current rate of biodiversity loss at the global, regional and national level as a contribution to poverty alleviation and to the benefit of all life on Earth". There is no single agreed measure of biodiversity loss but, within the CBD, Parties have decided to use a broad framework of goals, sub-targets and indicators relating to seven focal areas of the Convention to assess progress towards the 2010 target. A similar framework of indicators has also been adopted by the European Council of Ministers for assessing the European target. Following this lead, we have developed a broad range of indicators to measure our performance, in addition to the more specific targets agreed for priority species and habitats in the UK Biodiversity Action Plan. We are on course to meet both versions of the 2010 target in some areas, not to meet it in some, and to exceed it in others by not only halting decline but reversing it.

  3.  The assessments since 2000 generally show marked improvements compared with longer term (ie 10-30 year) trends where comparable data exist. Of the 20 UK measures for which post-2000 assessments are now available, 12 show improvement, 7 show no change; and only one (the wintering waterbirds indicator) shows deterioration. Taken together, these show that the rapid declines in biodiversity during the last quarter of the 20th century have been substantially slowed and in some cases halted, and that spending and public engagement have increased.

  4.  In absolute terms, the EU target to halt the loss of biodiversity by 2010 will not be met—and was never realistically achievable in all areas and aspects. It has, however, acted as a call to arms, and has galvanised activity by both Governments and NGOs to tackle a range of the most urgent problems.

Q2  How effective is the biodiversity monitoring and reporting process? Are the biodiversity indicators meaningful? Is there adequate data upon which to define targets and to assess progress?

  5.  Very effective overall. The UK's biodiversity is more closely monitored than most, partly as a result of our long tradition of voluntary biological recording, and particularly in relation to relatively large and easy to count species (eg birds, bats, butterflies and vascular plants). Co-ordinating scattered and disparate records is still a challenge, which we are tackling through sponsorship of the National Biodiversity Network[1].

  6.  A major periodic survey of broad habitats, Countryside Survey[2], was completed in 2007 and is due to report later this year, but a significant gap remains in respect of some of the less widespread priority habitats, especially outside designated sites. We are addressing this with JNCC, Natural England and the Environment Agency by developing a surveillance strategy for UK terrestrial biodiversity, and Natural England is initiating a programme of habitat inventories. We are also investing in Local Record Centres, which are intended to fill in some of the gaps in our baseline data.

  7.  Monitoring is inherently more difficult and much more costly in the marine environment than it is on land, but we are making a significant investment to improve our marine biodiversity data. Our current monitoring programme was designed to comply with the sector-based requirements of national and international regulations. Given Government's desire to move towards an ecosystem-based approach to the management of the marine environment, we have recognised the need for greater integration of monitoring programmes to enable us to make robust assessments of the overall state of the marine ecosystem. We have initiated the UK Marine Monitoring and Assessment Strategy (UKMMAS) to achieve these goals. As part of this work, JNCC is leading the development of a coherent strategy for marine biodiversity monitoring, including a review of currently available indicators.

  8.  We already have a good set of indicators for terrestrial biodiversity, which have drawn on data from Government agencies and non-governmental and research organisations and are published in Biodiversity indicators in your pocket 2007[3]. There are 18 indicators, comprising 29 component measures covering various aspects of biodiversity. Individually, they show both recent and longer-term change. Collectively, they provide an overview of progress for biodiversity as a whole. Four of the indicators are still being developed, with the aim of publishing trends for all 18 in 2009.

  9.  Additionally, a wider range of state and response indicators are published within country-level biodiversity strategies (eg England Biodiversity Strategy[4]) and relevant pressure indicators are included within the set of UK Sustainable Development Indicators[5].

  10.  The 2004 PSA Targets on SSSI condition and Farmland Birds[6], and the 2007 PSA indicator on changes in wild breeding bird populations in England[7] are underpinned by robust data. The data underpinning the UK Biodiversity Action Plan targets published in November 2006 are more variable in quality, and we recognise that there are not yet adequate data to set targets for all of the 1,149 species on the UK list of priority species and habitats published in August 2007. A balance does, however, need to be struck between the resource spent on data collection and refinement and that spent on direct intervention to protect and enhance our biodiversity, and we think the current balance is about right.

Q3.  Are the policy and institutional frameworks effective at protecting biodiversity? Is biodiversity protection addressed effectively at local and regional levels? How successful has the UK Biodiversity Action Plan been? Does Conserving biodiversity—the UK approach address the need to have a joined-up approach to biodiversity protection with the devolved administrations?

  11.  We believe that the frameworks relating to protected sites are generally effective at protecting terrestrial biodiversity, and that progress has been made on those relating to the wider countryside.

  12.  The bringing together of the former agriculture and environment departments in 2001, and the subsequent creation of Natural England under the Natural Environment and Rural Communities (NERC) Act 2006 have enabled closer integration of biodiversity policy with policies for agriculture and wider countryside management. Agri-environment schemes contribute to biodiversity protection in a number of ways. In particular, Environmental Stewardship is a key Defra policy delivered by Natural England. Scheme options which have had particular benefits include those for hedgerow management, which have resulted in over 90,000 km of hedgerows under environmentally friendly management and 30,000 km of restored and newly planted hedgerows. In addition, the Hedgerows Regulations 1997 have helped to protect hedgerows of historical and biodiversity importance from removal. The Environmental Impact Assessment (Agriculture) (England) Regulations 2006 give protection to uncultivated land and semi-natural areas from agricultural improvement.

  13.  In respect of protected sites, the NERC Act closed the few remaining gaps in legislative provisions concerning damage to protected sites, by introducing new measures to cover third party damage. The emphasis now is on effective enforcement of the measures which are in place and promotion of positive site management.

  14.  In the wider countryside, the protection of biodiversity is one consideration amongst many. Three recent developments are important here. The first, introduced by the NERC Act, is the new duty on all public and statutory bodies—including local authorities—to integrate biodiversity into their decision making. We have published guidance for local authorities on this, and will be monitoring the effectiveness of their response. The second is the adoption of our innovative ecosystem-based approach to policy making (see Q4), which will enable biodiversity issues to be considered as an integral part of ecosystem services

  15.  The third development is the new Public Service Agreements (PSAs) which include the new Natural Environment PSA (PSA28)[8] to "Secure a healthy natural environment for today and the future". This agreement approaches the natural environment from a more holistic view and sets out what other Government departments have agreed to do in order to achieve the outcome of a "healthy natural environment". CLG, DfT and FCOM are formal delivery partners while others, including BERR, have significant contributions to make. The Delivery Agreement for PSA 28 identifies Natural England as the lead delivery agent for the England Biodiversity Strategy (EBS). This includes a role both in direct delivery, and in overseeing and facilitating delivery across the piece by a range of partners. As part of this role, NE is working with us to refine the structure of EBS implementation arrangements, in order to improve the integration of BAP delivery with work to embed proper consideration of biodiversity in all relevant sectors of policy and decision-making.

  16.  Funding has been secured for local and regional co-ordination of biodiversity activity; this will focus on supporting local and regional partnerships, delivering Biodiversity Action Plans at local and regional levels, reporting and monitoring progress and integrating biodiversity into regional and local policies. A local government performance indicator for biodiversity (the proportion of Local Sites under conservation management) is included within the basket of national indicators by which local authority performance will be measured7. The new local government inspection regime, Comprehensive Area Assessment, will monitor the delivery of the indicators focussing on those agreed in Local Area Agreements.

  17.  Future priorities include:

    —  the further integration of biodiversity into local and regional policies, processes and programmes, such as Community Strategies and Regional Spatial Strategies, facilitated by the NERC Act biodiversity duty;

    —  building partnerships at the local and regional level; and

    —  improving access to sources of advice, expertise and datasets for local and regional authorities.

  18.  The UKBAP has raised awareness of threats and helped coordinate and drive new conservation work at national and local levels. This has been achieved by identifying priorities for action and setting biological targets for the recovery of species and habitats, including those not subject to statutory protection. It has also been influential in attracting other sources of funding such as Landfill Tax and Lottery money.

  19.  The UKBAP has also engendered a strong partnership between the UK Government, Devolved Administrations, statutory agencies, local authorities and non-Governmental organisations, and this partnership has enabled us to make much more progress than would have been possible otherwise.

  20.  Success of the UKBAP in the marine environment has been more limited, primarily because the marine environment does not lend itself to local action (an important reason for the success of the UKBAP terrestrially). There are particular issues involved in taking effective action for some mobile priority species (eg sharks, skates, rays and deep water species), including achieving effective fisheries control measures beyond six nautical miles, where agreement is generally required at EU level. The development of the forthcoming EU Shark Plan of Action will provide a good opportunity for us to make progress here.

  21.  The draft Marine Bill contains integrated proposals to facilitate effective conservation management and improve the management of human activities in the marine environment. The Bill's proposals for Marine Protected Areas are covered under Q10 below, but the Bill also includes provisions for marine planning and licensing, new enforcement powers, and the creation of the Marine Management Organisation and Inshore Fisheries and Conservation Authorities, all of which will help to improve the management and conservation of marine biodiversity.

  22.  Conserving biodiversity—the UK approach[9] sets out our shared purpose in tackling the loss and restoration of biodiversity, the guiding principles that we will follow to achieve it, our priorities for action in the UK and internationally, and indicators to monitor the key issues on a UK basis.

  23.  Government responsibility for delivering biodiversity is devolved but it is recognised that knowledge and expertise on components of biodiversity are often relevant to more than one country and can be held by individuals or organisations (such as NGOs) who operate across the UK. To work efficiently and avoid unnecessary bureaucracy, the new framework clarifies that the emphasis for future work at UK level will be on co-ordination, information exchange, identification of research priorities and some reporting. JNCC has a key role in this respect.

Q4.  How well is biodiversity protection incorporated into the policy-making process? How well will the Ecosystem Approach Action Plan address this issue? Has there been enough progress in ensuring that the value of ecosystem services are reflected in decision-making?

  24.  Work to embed proper consideration of biodiversity in all relevant sectors of policy and decision-making is undertaken through the biodiversity or environment strategies of each of the four countries of the UK. Achievements in England include the establishment of the biodiversity performance indicator for local government, and the fourth Periodic Review of Water Prices, which has led to £500m of investment benefiting more than 170 water and wetland SSSIs damaged by sewage pollution and over-utilisation of water. Adequate integration of biodiversity protection into all relevant policy areas is a continuing priority.

  25.  Biodiversity protection has been incorporated into the Government's marine strategy, and key components of this are included within the draft Marine Bill. The Common Fisheries Policy, as written, is based on an ecosystems approach, and the UK Government is firmly committed to this.

  26.  Through its ecosystems approach action plan, Defra is committed to developing a more strategic approach to policy making on the natural environment, based on a number of core principles, including taking a more holistic approach to policy-making and delivery and ensuring that the value of ecosystem services is fully reflected in decision-making. The plan includes a range of actions with direct relevance to biodiversity.

  27.  On valuation, in particular, the plan sets out actions to:

    —  review existing policy and project appraisal tools to explore how the principles of an ecosystems approach, including the valuation of ecosystem services, could be incorporated;

    —  develop a benefits transfer strategy for use in valuing ecosystem services;

    —  promote the development of the existing Environmental Valuation Reference Inventory (EVRI) database to ensure that it captures studies on the valuation of ecosystem services most useful and relevant for benefits transfer, including from Defra-funded studies; and

    —  review work on non-economic and participatory valuation methodologies and produce guidelines on their use alongside economic valuation methodologies

  28.  Defra has published "An Introductory Guide to Valuing Ecosystem Services" to assist those involved in the decision-making process to take better account of the value of ecosystem services. We have also funded or supported a number of research projects on valuing ecosystems services.

  29.  Internationally, considerable progress is also being made through the G8 Potsdam initiative to produce a Stern-style review, called The Economics of Ecosystems and Biodiversity. The main aim of this project is to assess the value of the loss of biodiversity and the costs and benefits of actions to conserve it. It will use a range of mechanisms and will develop methodologies such as tracking the movement of biodiversity, measuring the change in its abundance and quality, and measuring the economic value that such changes represent. An initial report on this work was presented to the recent CBD Conference of the Parties in Bonn, and the UK announced a contribution of £100k towards the next phase of the work.

  30.  While more work is needed to refine and develop valuation methodologies, we have already started to use valuation tools in government policy. For example, work to value marine ecosystem services has been undertaken by Government, most recently as part of the impact assessment undertaken for the nature conservation provisions of the draft Marine Bill.

KEY THREATS

Q5.  What are the key drivers of biodiversity loss in the UK, and is the Government addressing them?

  31.  Detailed work has been done on reasons for adverse condition in the context of the SSSIs PSA target in England. The top ten reasons are: overgrazing (typically in the uplands), moor-burning, coastal squeeze, drainage, water pollution from agriculture and discharge, air pollution, undergrazing (typically in the lowlands), inappropriate scrub control and lack of appropriate forestry/woodland management (including management of deer grazing).

  32.  In the UKBAP 2005 reporting round[10], lead partners were asked to list the issues that were currently posing, or likely to pose, a significant threat to their species or habitat over the next 5 years. Key threats faced by priority habitats and species were: habitat loss (particularly due to agriculture or changes in management practices), infrastructure development (mainly housing infrastructure and development on the coast), and climate change.

  33.  In the marine environment, climate change and some fishing activities have a particularly adverse impact on biodiversity. Some fisheries stocks are not currently at full reproductive capacity, and levels of by-catch can impact on other marine species. Climate change is already starting to have a significant impact on some species (see Q7).

  34.  Action to address each of these drivers is being taken under the auspices of the UKBAP and the country biodiversity strategies.

Q6.  Will the Invasive Non-native Species Framework Strategy prove effective? Is there adequate regulation and resources to prevent further invasions and to undertake eradication programmes?

  35.  We are confident that the Invasive Non-native Species Framework Strategy will help. It is based on internationally agreed advice and principles, and has received widespread support from stakeholders. Its core premise is agreed under the Convention on Biological Diversity: of firstly seeking to prevent introductions; then swift action against those that are found early; and, finally, effective longer-term management of those that are already established. However, as we have acknowledged in the strategy, no system will be completely watertight because there is so much scope for invasive species to be introduced deliberately or accidentally through global trade and travel.

  36.  Work is in hand on making further use of existing regulatory powers to control what may be released or sold, but the scope for additional regulation needs to be balanced against the burdens it would impose. Success will also depend on other approaches such as changing behaviours, and improving understanding of the risks and the need for action against such species.

  37.  The plant health regime is a good example of an existing robust line of defence against the introduction of invasive non-native plant pests and the strategy will lay the foundation for better protection of our native wildlife in general. We intend to back up preventative measures with arrangements to instigate appropriate control actions much sooner in future. This could involve a range of bodies whose interests or responsibilities are relevant and may therefore be resourced in a number of ways. However, early action is more likely to succeed, will cost significantly less and will minimise any potential harm to native wildlife and habitats.

  38.  Eradication of established invasive species must be approached very carefully—particularly in terms of knowing the true size and extent of the problem, the effectiveness of control techniques and the likely response of the species to such action—in order to avoid unsustainable commitment of resources. For example, the policy review group that reported in 2003 estimated that eradicating Japanese knotweed in Britain would cost £1.56 billion. Priority will therefore need to be given to preventing as many future problems as possible through detection and rapid response, and to managing those species that have already become well established in a cost-effective and targeted way. The GB Programme Board will advise Government on the case for major or national eradication programmes in future.

Q7.  What impact will climate change have on UK biodiversity? How might the impacts of climate change be reduced? How can potential conflict between climate change mitigation and adaptation measures and biodiversity protection be effectively managed?

  39.  While we cannot be certain of the impacts climate change will have on UK biodiversity, we know that we are likely to face longer, hotter summers, wetter winters and more extreme weather events, and that there will be longer growing seasons for plants. These conditions could significantly affect species' ranges, preferred habitats and behaviour.

  40.  Many species are already showing evidence of northward extension in their distribution in the UK. We can use studies such as the MONARCH report which modelled the "climate space" of priority species identified in the UKBAP, using established climate change scenarios to indicate possible outcomes.

  41.  In the marine environment, it is predicted that climate change will lead to changes in temperature, pH level (ocean acidification), water circulation and sea level rise. Changes are likely to occur in the abundance and distribution of marine habitats and species. For example, recent warmer conditions appear to have led to changes in the distribution of fish prey species, which in turn have led to reduced breeding success in some seabird populations. Sea-level rise associated with climate change is likely to accelerate the rate of loss of coastal habitats around the UK. For example, it is estimated that an average of 100 ha of saltmarsh is being lost every year in the UK as a result of coastal squeeze. The vast majority of these losses are in the south and east of England where Government has established a target for the creation of at least 100 ha of intertidal habitat per year through the flood management programme to offset this impact and contribute to meeting biodiversity targets.

  42.  Increasing the resilience of species, habitats and ecosystems to climate change will help the widest range of biodiversity to survive its impacts and adapt. So we should seek to:

    —  conserve the range and ecological variability of habitats and species;

    —  maintain existing ecological networks;

    —  create buffer zones around high quality habitats; and

    —  take prompt action to control the spread of invasive species

  We are mainstreaming climate change across all the workstreams of the England Biodiversity Strategy so that consideration of the impacts of climate change becomes an integral part of all decisions made for biodiversity.

  43.  Our biodiversity plays an important role in helping mitigate against climate change with forests and peatlands providing carbon sinks. Adaptation for biodiversity will need to be a long term activity as our knowledge increases. It is difficult to predict the likely consequences of mitigation and adaptation measures in other sectors, but the key lies in ensuring that sustainable options are developed, for example in the area of renewable energy.

Q8.  DOES PLANNING POLICY ADEQUATELY PROTECT BIODIVERSITY? ARE EFFECTIVE MEASURES IN PLACE TO ENSURE THAT GOVERNMENT PLANS FOR HOUSING GROWTH (INCLUDING ECO-TOWNS) ENHANCE RATHER THAN DAMAGE BIODIVERSITY? SHOULD THERE BE A REVIEW OF GREENBELT POLICY, AND WHAT MIGHT THE CONSEQUENCES BE FOR BIODIVERSITY? DO GUIDELINES ENCOURAGING DEVELOPMENT ON BROWNFIELD SITES RISK DAMAGING BIODIVERSITY?

  44.  The Government's aim is that development should have minimal adverse impacts on biodiversity and enhance it wherever possible. The policy and legislative framework to enable this to happen is already largely in place, through PPS9 and accompanying guidance; the linked Government Circular on statutory obligations for biodiversity and geological conservation and their impact within the planning system; and the arrangements for appraising regional spatial strategies, local development documents and individual planning applications.

  45.  In practice, much depends on the relative weight afforded to these policies amongst the many others embodied in planning legislation and guidance. In a small, densely populated country, with continuing high levels of demand for housing and infrastructure development, it remains a challenge to achieve full integration of biodiversity conservation and enhancement with relevant social and economic considerations, as part of delivering sustainable development.

  46.  One of the problems we face is how to make it easier for developers to provide for biodiversity, in a meaningful way and at a sufficiently large scale, as a normal part of their work. This requires clarity at the outset about what is needed, and the cost and means of delivering it. To this end, we are undertaking research to assess the potential for making better use of biodiversity offsets (ie offsite compensation measures) which might have a role in reducing adverse impacts on the wider countryside.

  47.  The proposals for a Community Infrastructure Levy on new development could potentially make a significant contribution to minimising the impacts on biodiversity of housing and other new development. Green infrastructure, and its associated biodiversity, is an essential component of a good quality of life when communities grow and needs to be fully integrated into new development.

  48.  All New Growth Point (NGP) proposals are screened by NE and EA for their potential impacts on biodiversity; where impacts are potentially significant, appropriate conditions (eg necessary mitigation) are attached as part of the NGP designation. The consultation paper issued by CLG in April makes clear that eco-towns will be expected to "enhance the biodiversity value [of the locality], providing a variety of important habitats and inter-connecting wildlife corridors..." The proposed locations have themselves been subjected to exactly the same sort of "showstopper" review as proposed NGPs, with potential impacts on biodiversity one of the assessment criteria.

  49.  The Government is working with the Town and Country Planning Association (TCPA) on the practical application of the key sustainability criteria for eco-towns. TCPA are producing a series of guidance worksheets, including one on biodiversity, which will be available to all those involved with taking forward eco-town proposals.

  50.  In May 2007 the Planning White Paper, Planning for a Sustainable Future[11], reinforced the Government's commitment to the key principles of Green Belt policy set out in PPG2. The planning system exists to identify the most appropriate locations for development taking into account a wide range of considerations, and Green Belt policy is an important part of this.

  51.  While environmental enhancement is not the primary purpose of the green belt, there are examples of communities, local authorities and landowners working together to improve the environmental quality of green belt land, providing benefits for biodiversity. The Community Forests programme is a good example of this, and similar initiatives to provide opportunities for biodiversity, leisure, and healthy living in urban fringes are possible within current Green Belt policy.

  52.  Government's recent response to English Partnerships' recommendations on the National Brownfield Strategy[12] recognised that not all brownfield land is suitable for development purposes and that such sites can be important for biodiversity. The revised UK Biodiversity Action Plan list of priority species and habitats (approved by Ministers in August 2007) includes "Open Mosaic Habitats on Previously Developed Land" for the first time. We are currently commissioning research to:

    —  refine the definition for this new priority habitat to aid identification on the ground; and

    —  identify options for compiling an inventory of all the land in the UK that falls within that definition.

  This work, and the proposed BAP for this habitat type, will help avoid damage to those brownfield sites which are important for biodiversity.

RESOURCES

Q9.  Are there adequate resources for biodiversity protection and enhancement? Has the Government addressed the need to provide additional support for biodiversity protection in the UK Overseas Territories?

  53.  A report commissioned from external consultants and published in 2007[13] estimated current spend on the UKBAP in 2005-06 as £388m pa. Our biodiversity expenditure indicator[14] shows that since 2000-01 there has been a year on year increase in biodiversity expenditure from the public sector in real terms, resulting in an overall increase of 33 per cent. The lion's share of this comes from agri-environment expenditure; £2.9bn of agri-environment funding has been secured for England for the period 2007-13, much of which will be targeted at biodiversity. Statutory nature conservation agencies, and Forestry Commission are the other major public sector contributors, together with lottery funding. In addition, the private sector, in particular Wildlife and Countryside Link organisations, are major funders.

  54.  Where UK Overseas Territories (UKOTs) are included within the UK's ratification of a multilateral environmental agreement, they must be able to meet the obligations under that agreement. For the Convention on Biological Diversity, St Helena (and dependencies), Gibraltar, Cayman Islands and British Virgin Islands are the UKOTs included in the UK's ratification. One of the principles that govern the relationship between UKOTs and the UK Government is that Britain will continue to provide help to the UKOTs that need it. This is an important point, given the wide range in GDP between different UKOTs.

  55.  Defra has provided funding to a number of programmes in the UKOTs. Through the Darwin Initiative we have so far contributed in excess of £1.5m including £79k over the past year on two projects in Tristan da Cunha (enabling implementation of the CBD in the marine environment) and the Falkland Islands (conservation of freshwater fish). The new Darwin Round, announced at the recent CBD Conference of the Parties in Bonn, that it will give priority to applications for the UKOTs. Defra has supplemented its Darwin support indirectly through voluntary contributions made to international agreements, in particular the Agreement on the Conservation of Albatrosses and Petrels (ACAP), of which the UK was a founding member. We have given voluntary contributions to ACAP and we are also contributing towards the costs of an officer who will co-ordinate ACAP activities in the South Atlantic territories from a base in the Falkland Islands.

  56.  The Overseas Territories Environment Programme (OTEP) was established to help the UKOTs to implement their Environment Charters and environmental management more generally. It is jointly funded by FCO and DfID. In the first phase (2004-07), a total of £3m was spent on biodiversity conservation in the UKOTs; funding in the current phase is £0.5m pa from each department over the next three years. DfID, FCO and Defra officials consider annual OTEP applications for funding. The FCO portion of OTEP is a ring-fenced element within the larger Overseas Territories Programme Fund (OTPF), a £6.5m programme. Environmental projects can and have been funded from other parts of the OTPF.

PROTECTED AREAS

Q10.  Is the UK protected area network up to the job of maintaining biodiversity, now and into the future? Are arrangements to protect sites effective? Is more work needed to reduce habitat fragmentation and to link up those semi-natural habitat areas that remain?

  57.  A coherent network of protected areas is vital for conserving the best of our biodiversity, and is an integral component of the England Biodiversity Strategy. On land, designations include non-statutory local sites and local nature reserves, Sites of Special Scientific Interest (SSSIs), National Nature Reserves, European Sites (as part of the Natura 2000 network), and Ramsar Sites. While we expect to bring forward new national and European marine designations (see below), the extent of the suite of terrestrial and freshwater sites is now largely complete.

  58.  Natural England is developing a framework to assess the climate change resilience of SSSIs, which it plans to pilot this year and roll out across England in the two following years. We will consider the fitness for purpose of the protected areas network in the light of Natural England's work, but it seems likely that the existing network will still have a key role to play. Protected sites, supplemented by a broader mosaic of non-statutory local designations, already have the best potential to support the movement and changing distribution of species. We may need to build in the flexibility to adjust the conservation objectives and notified interests of existing sites, as well as developing landscape-scale responses to facilitate movement of species. We have commissioned research looking at such a broader `landscape scale' approach.

  59.  Protection for important and threatened marine habitats and species is not at the same level as terrestrial protection. However, the UK is committed by international agreements and EU Directives to establishing an ecologically coherent network of well-managed Marine Protected Areas (MPAs). A UK-wide vision for the network of MPAs (which will include Marine Conservation Zones and European marine sites) is being developed with the Devolved Administrations and the statutory nature conservation bodies. The proposals contained in the draft Marine Bill will play an important role in helping to deliver this vision.

  60.  The draft Marine Bill provides a power for Ministers to designate Marine Conservation Zones (MCZs) for the purpose of conserving marine flora, fauna and habitats. In particular, we want to designate areas which are important for rare and threatened species, and for habitats that best represent the biodiversity of UK waters. The network will be designed to deliver, together with our European sites, an ecologically coherent network of Marine Protected Areas, which are mutually supportive and which contribute to healthy marine ecosystems. The MCZ provisions in the draft Bill will not apply to the territorial waters of Scotland and Northern Ireland. Instead, those Devolved Administrations have announced their intention to legislate separately, and we are working with them to ensure the coherence of the overall network.

  61.  The protection of MCZs will largely be achieved through the marine licensing (and other existing) consent regimes, in the same way as for European marine sites. Levels of protection, and the management implications, will depend on the conservation objectives set for each site. Public authorities will be under a duty to further—or, where this is not practicable, least hinder—MCZ conservation objectives in carrying out their functions. They will not be able to license any activities that would hinder the achievement of an MCZ's conservation objectives, except in cases where there are no suitable alternatives, the damage to the environment will be outweighed by the public benefit, and the damage is compensated for. The Marine Management Organisation (and Welsh Ministers in Wales) will have powers to make conservation orders to protect MCZs from harmful activities which would otherwise be unregulated. Additionally, Inshore Fisheries and Conservation Authorities in England will be placed under a specific duty to ensure that conservation objectives for MCZs are furthered, such as by making fisheries byelaws where necessary.

  62.  On land, our emphasis is on both the protection and the enhancement of sites, and progress in improving their condition has been good. The condition of SSSIs, which include European sites, is one of the key indicators of the success of our biodiversity strategy. We are aiming to bring 95% of the area of SSSI land in England into favourable or recovering condition by December 2010. 82.9% of the SSSI area was in target condition by early June 2008—up from a baseline of only 56.9% five years earlier. Further progress relies on a partnership approach to positive site management. Stakeholders with major land-owning or managing responsibilities have recently agreed to delivery commitments which should bring at least a further 5% of SSSI land within target condition by March 2009. The challenge is to maintain that momentum as we work towards the 2010 target.

  63.  While management of special sites is a pre-requisite of securing future biodiversity, it is not sufficient on its own. Firstly, not all of the UK's priority species and habitats are found in designated areas; secondly, there is a need to buffer and link small sites to reduce the risks to survival faced by small, isolated populations; thirdly, studies of predicted responses of species and habitats to climate change suggest that most of the species that are currently the focus for conservation are likely to experience changes in the location and/or extent of areas across the UK where the climate will meet their requirements. This illustrates the need to reduce habitat fragmentation to facilitate species dispersal and establishment in new locations as the climate changes. The Wildlife Trusts and other NGOs have championed this work through their "living landscapes"[15] and "rebuilding biodiversity"[16] campaigns, which Government has welcomed and encouraged.

17 June 2007






1   http://www.nbn.org.uk/ Back

2   http://www.countrysidesurvey.org.uk/ Back

3   http://www.nbn.org.uk/ Back

4   http://www.defra.gov.uk/wildlife-countryside/biodiversity/biostrat/index.htm Back

5   http://www.sustainable-development.gov.uk/progress/data-resources/documents/sdiyp2007_a6.pdf Back

6   http://www.defra.gov.uk/corporate/busplan/spending-review/psa2004.htm Back

7   http://www.hm-treasury.gov.uk/media/1/3/pbr_csr07_psa28.pdf Back

8   http://www.communities.gov.uk/publications/localgovernment/nationalindicatorsupdate Back

9   http://www.defra.gov.uk/wildlife-countryside/pdfs/biodiversity/ConBioUK-Oct2007.pdf Back

10   http://www.ukbap.org.uk/library/Reporting2005/UKBAPReport05.pdf Back

11   www.communities.gov.uk/publications/planningandbuilding/planningsustainablefuture Back

12   http://www.communities.gov.uk/documents/planningandbuilding/doc/securingfuturebrownfield.doc Back

13   http://www.ukbap.org.uk/bapgrouppage.aspx?id=110 Back

14   http://www.jncc.gov.uk/pdf/2010-BIYP2007.pdf Back

15   http://www.wildlifetrusts.org/index.php?section=about:publications:free Back

16   (Living Landscapes, full report) Back


 
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