Renewables Action Plan: Strategic Environmental Assessment

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2. ENVIRONMENTAL CONTEXT

Relationship with other plans, programmes or strategies ( PPS) and environmental objectives

2.1 The Environmental Assessment (Scotland) Act 2005 requires that the Environmental Report includes an outline of the relationships between the RAP and other relevant plans, programmes or strategies ( PPS). It is particularly important to consider how environmental protection objectives should be taken into account in the preparation of the policy.

2.2 This section summarises these issues and describes the policy context within which the RAP will operate, and the constraints and targets that this context imposes.

2.3 The plans, programmes, strategies and their environmental objectives, which together form the context for this SEA, are summarised in Table 3 below.

Table 3: Summary of key relevant environmental objectives

Topic area

Relevant plans, programmes and strategies

Key objectives of relevance to the SEA of the RAP

Climate (including energy)

  • Kyoto Protocol (1997)
  • Stern Report (2006) 1
  • Changing Our Ways - Scotland's Climate Change Programme (2006)
  • Climate Change Bill (as introduced)
  • Adapting Our Ways: Managing Scotland's Climate Risk: Consultation to inform Scotland's Climate Change Adaptation Framework
  • UK Energy White Paper. Our energy future - creating a low carbon economy (2003)
  • DECC Energy NPS
  • EU Biomass Action Plan
  • FREDS (2008) Scotland's Renewable Heat Strategy: Recommendations to Scottish Ministers.
  • Biomass Action Plan for Scotland (2007)
  • Energy Efficiency and Microgeneration: achieving a Low Carbon Future: A Strategy for Scotland (2007) (Draft Strategy)
  • Scottish Planning Policy 6 Renewable Energy (currently being updated to form part of the consolidated Scottish Planning Policy)
  • These environmental objectives aim to reduce emissions of greenhouse gases in order to increase climate change mitigation, and are the key drivers underpinning development of the RAP.
  • The broader commitments to climate change are supported by a specific emphasis on reducing greenhouse gas emissions from the energy and transport sectors.
  • The Climate Change (Scotland) Bill particularly emphasises the importance of energy efficiency and renewable heat in maximising the contribution of the energy sector to these ambitious targets.

Air quality

  • EC Directive on Air Pollution 2008
  • The Air Quality Strategy for England, Scotland, Wales and Northern Ireland. Working Together for Clean Air (2007)
  • Air quality objectives aim to ensure that targets are not exceeded.
  • Priority is given to areas where there are concentrations of air pollution at present (Air Quality Management Areas). Most of these areas have been declared as a result of transport sector emissions.
  • The Air Quality Strategy introduces new policy framework for tackling fine particles and identifies potential new national policy measures which modelling indicates could give further health benefits and move closer towards meeting the Strategy's objectives.
  • The extent to which the RAP supports these objectives has been considered in the SEA, with a particular focus on the biomass sector.

Population and human health

  • Scottish Executive (2003) Improving Health in Scotland - The Challenge
  • UK Fuel Poverty Strategy (Fourth Annual Progress Report, 2006)
  • Key relevant priorities focus on alleviating fuel poverty, including through the renewables sector.
  • Health objectives, particularly those associated with respiratory disease arising from air pollution, are also relevant.
  • The RAP has a role to play in supporting broader objectives to improve health and quality of life.

Biodiversity, flora and fauna

  • Council Directive 79/409/ EEC on the conservation of wild birds
  • Council Directive 92/43/ EEC the conservation of natural habitats and of wild fauna and flora
  • Nature Conservation (Scotland ) Act 2004
  • Scotland's Biodiversity - It's In Your Hands. A strategy for the conservation and enhancement of biodiversity in Scotland (2004)
  • Priorities aim to protect and enhance biodiversity at a landscape scale.
  • Particular protection is afforded to species and habitats that are designated under the Birds and Habitats Directives, although national, regional and local designations and the broader natural environment are also given appropriate levels of protection, recognising their role as part of habitat networks.
  • The Nature Conservation (Scotland) Act 2004 introduced a 'duty to further the conservation of biodiversity' for all pubic bodies, and sets out more specific provisions within this (e.g. for SSSIs). Also states a requirement for the preparation of a Scottish Biodiversity Strategy, to which all public bodies should pay regard.
  • Direct and indirect effects from biomass (key to delivery of the 11% renewable heat target) are considered within the assessment.

Soil

  • EU Thematic Strategy for Soil Protection (2005)
  • Scottish Soil Framework 2009
  • Emphasises the importance of soil in fulfilling a range of functions, including biomass production.
  • Based on analysis of soil resources in Scotland, priority is given to protection of soil stability, quality and functionality.
  • The overall aim is to promote the sustainable management and protection of soils, in balance with the economic, social and environmental needs of Scotland.
  • The role of peatland in carbon storage is of particular relevance to the RAP.

Water

  • Water Framework Directive 2000/60/ EC
  • Water Environment and Water Services (Scotland) Act 2003 ( WEWS Act)
  • SEPA (2008) Draft River Basin Management Plans Scotland River Basin District / Solway Tweed River Basin District,
  • The Water Environment (Controlled Activities) (Scotland) Regulations 2005
  • Scottish Executive Environment Group (2002) Scotland's Bathing Waters A Strategy for Improvement
  • Scottish Marine Bill (as introduced) 2009
  • Objectives are based on the EC Water Framework Directive, which seeks to ensure that water bodies reach good ecological status by 2015.
  • Emerging River Basin Management Plans provide a more detailed interpretation of the measures required to achieve this.
  • The SEA has explored the relationship between the RAP and wider objectives to improve the condition of the water environment.

Material assets

  • National Waste Management Plan (Scotland) Regulations 2007
  • Waste Framework Directive (2008/98/ EC) 2
  • National Waste Plan (2003) (under review)
  • Consultation Paper on Potential Legislation Measures to Implement Zero Waste (2008)
  • Key policies relate to increasing sustainable waste management and promoting sustainable transport options.
  • Relevant objectives include reducing the share of waste that is disposed of in landfill sites, promoting energy from waste schemes, and using technological advancement to complement other measures that aim to reduce greenhouse gas emissions from the transport sector.
  • Further objectives of relevance relate to the agricultural sector and rural development more broadly. They emphasise the importance of integrated and innovative approaches to rural areas which support communities.

Cultural heritage

  • Scottish Historic Environment Policy ( SHEP) (October 2008)
  • Protected sites and buildings form a focus for historic environment policies.
  • At the same time, policy objectives recognise the importance of the broader environment as a cultural heritage resource.
  • Potential for direct and indirect cumulative cultural heritage effects arising from key elements of the RAP have been explored within the SEA.

Landscape

  • Council of Europe, European Landscape Convention 2000
  • SNH Natural Heritage Futures (2002)
  • Scottish Landscape Forum Report to Ministers 'Scotland's Living Landscapes: Places for People
  • Policy objectives aim to protect landscape quality and distinctiveness.
  • Some landscapes are recognised as being particularly important as a result of their unique qualities for which they have been formally designated for protection.
  • However, more recent policy objectives emphasise the importance of respecting and enhancing where possible broader (non-designated) landscapes.
  • The potential for direct and indirect cumulative effects arising from the RAP, and in particular its emphasis on biomass, have been explored within the SEA.

Environmental baseline

2.4 The Environmental Assessment (Scotland) Act 2005 Schedule 3 requires that the Environmental Report includes a description of the relevant aspects of the current state of the environment and the likely evolution thereof without implementation of the PPS, and "the environmental characteristics of areas likely to be significantly affected." This section therefore begins to describe the environmental context within which the RAP will operate and the constraints and targets that this context infers.

2.5 In order to define the current state of the environment with a view to informing the SEA, the review has focused on thematic information, with more detailed spatial analysis not having been necessary given the thematic and high level character of the RAP itself. Much of the relevant environmental information was referred to within the RAP Consultation Document that was published in 2008. The following data sources have been used to inform the assessment.

Table 3: Baseline data sources

Topic area

Baseline data sources

Climate

  • UKCIP02 scenarios / UKCIP09 when available 3
  • SNIFFER 2006 Online Handbook of Climate Trends across Scotland 4
  • NETCEN data on greenhouse gas emissions
  • SEPA State of Scotland's Environment 2006
  • Renewable Heat Group (2008) Scotland's Renewable Heat Strategy: Recommendations to Scottish Ministers 5
  • Scottish Government, (2008) Mitigating Against Climate Change in Scotland: Identification and Initial Assessment of Policy Options 6
  • Greenhouse Gas Inventories for England, Scotland, Wales and Northern Ireland 7
  • Woodfuel Task Force, (2007) Increasing the Supply of Wood for Renewable Energy in Scotland 8
  • Scottish Government (2008) Woodfuel Taskforce Report Response 9
  • Scottish Government (2006) Review of Greenhouse Gas Life Cycle Emissions, Air Pollution Impacts and Economics of Biomass Production and Consumption in Scotland 10
  • Scottish Government Energy Trends
  • RCEP report on Biomass as a Renewable Energy Source 11

Air quality

  • AEA, (2008) Measurement and Modelling of Fine Particulate Emissions ( PM10 and PM2.5) from Wood-Burning Biomass Boilers, Prepared for the Scottish Government 12
  • SEPA State of Scotland's Environment (2006)
  • Number and location of Air Quality Management areas in Scotland

Population and human health

  • Scottish Index of Multiple Deprivation 2006
  • Scottish Health Survey Data

Biodiversity, flora and fauna

  • Statutory Designated Sites
  • SBAP / SNH / JNCC data - key protected species and habitats, declining species and habitats under pressure
  • Countryside Survey 2003
  • SNH Natural Heritage Futures, Natural Heritage Trends
  • Site Condition Monitoring Data (2005)
  • SEPA State of Scotland's Environment (2006)
  • Rural Scotland Key Facts 2008 (Scottish Government)

Soil

  • SEPA State of Scotland's Environment: Soil Report (2006)
  • Scotland's Soil Resource - Current State and Threats (2006)

Water

  • Main rivers and associated biodiversity designations
  • River Water Quality (Length of Poor and Seriously Polluted Rivers in Scotland 1995-2005) ( SEPA)
  • SEPA National Water Quality Classification 2005 ( SEPA)
  • SEPA River Basin Management Plans (2008)
  • SEPA State of Scotland's Environment (2006)
  • SEPA Indicative River and Coastal Flood Map (Scotland) (2006)

Material assets

  • SEPA waste data e.g. recycling and composting rates, and waste data digest 8.
  • Scottish Government Key Waste Statistics (from Scottish Household Survey) 13
  • Scottish Government, Key Transport Statistics (2008)

Cultural heritage

  • World Heritage Sites, Listed Buildings, Scheduled Ancient Monuments, Conservation Areas, Inventory of Historic Gardens and Designed Landscapes (Historic Scotland)
  • Information for Scotland's Historic Environment Audit (2007)

Landscape

  • National Scenic Areas, SNH Wild Land Areas of Search, National Parks, and local landscape designations
  • SNH Natural Heritage Futures Prospectus

2.6 Sufficient data was available to allow for accurate and comprehensive characterisation of the environmental baseline and this information was used to directly inform the assessment. The following paragraphs describe the current state of Scotland's environment, in terms of issues which are most likely to be significantly affected by the RAP.

Climatic Factors

Climate change and its environmental effects

2.7 The long-term increase in temperatures in the UK and Scotland has accelerated over the past three years, and "there is now evidence that human activities are having a discernable impact on the global climate."14 The UKCIP02 15 climate change scenarios predict that by the 2080s temperatures will rise by up to 3.5 o in the summer and 2.5 o in the winter, and that there will also be changes in precipitation, snowfall (up to a 90% reduction), seasonality, cloud cover, humidity, wind speeds, soil moisture, extreme weather (especially changes in rainfall) and sea levels as a result of climate change. Spatial patterns of climate change within Scotland are predicted to vary. For example, summer rainfall is expected to reduce by 10% in most of the country except the north west, and much more substantial increases in spring and autumn rainfall in the south west and north east of the country are envisaged. Further evidence of Scottish climate change has been provided in research by SNIFFER. 16 This includes data showing a 25% reduction in frost days since 1961, a shorter snow season and a lengthened growing season. Many of these trends appear to be most significant in north and west regions of Scotland.

2.8 A wide range of environmental resources are vulnerable to the impacts of climate change. For example, the RSPB recently provided an introduction to emerging research on the ability of birds in Europe to adapt to climate change. 17 Similarly recent research has emerged from Forest Research. 18 This predicts significant landscape and biodiversity changes leading to the use of new species and structures of woodland planting. Whilst productivity of forestry is expected to increase, the suitability and resilience of different tree species will change, and there will be growing threats to woodlands from drought, insect, disease and wind damage. The research supports the broader Forestry Commission target of increasing forestry coverage of Scotland from 17% to 25% by 2050, as a means of reducing woodland fragmentation and supporting habitat networks.

2.9 The Marine Climate Change Impacts Project report for 2007-2008 showed that 2006 was the second warmest year in UK coastal waters since records began in 1870. Seven of the ten warmest years occurred in the last decade. 19 There are predictions of fewer, but more severe storms for coastal areas and an increase in coastal erosion with implications for 12% of Scotland's coastline. Climate change is likely to reduce the breeding success and survival of some seabirds, whilst there has been an increase in the abundance of some warm water invertebrates and alga that have extended their range to parts of Northern Scotland. Lower rates of sea level rise are predicted for Scotland as compared to the more significant issues arising for the south of England. They are currently expected to be confined to 0-60cm by 2080.

Energy

2.10 The energy sector accounts for a large share of climate change causing emissions. Statistics show that since 1990 net greenhouse gas emissions in Scotland have decreased by 13.4%. In 2006 around 80% of emissions were CO2 whilst other greenhouse gases ( GHGs) accounted for the remaining 20%. The former decreased between 1990 and 2006 by 6.8%, compared with a decline of 31.9% of other GHGs. There was a 5.4% increase in net GHG emissions between 2005 and 2006. In 2006, Scotland's major power stations and energy intensive industrial installations accounted for around 40% of Scotland's greenhouse gas emissions, and fall within the scope of the EU Emissions Trading Scheme, often described as the traded sector. Transport generated around 25% with heat accounting for 16%, of which domestic heat made up almost 13%.

2.11 As an end-use, it is estimated that heat currently accounts for around 50 per cent of total energy consumption in Scotland, with a broadly even split of the remaining 50 per cent between transport and electricity. This demonstrates the significance of the proposed additional policies that relate specifically to heat.

2.12 As outlined in the Scottish Government is committed to working towards the achievement of 20% of total energy use coming from renewables in 2020. To achieve this objective, individual 2020 targets for renewable electricity, heat and transport have bee put in place:

  • Electricity: Achieve 50% of gross electricity consumption from renewable sources by 2020, with an interim target of 31% by 2011. In 2007, renewable electricity generation accounted for 20.1% per cent of gross electricity consumption in Scotland.
  • Transport: To achieve a 10% target for renewable transport by 2020, in alignment with a mandatory 10% EU target set for each Member State. It is estimated that renewable transport fuels accounted for around 1% of fuel consumption in 2007.
  • Heat: 11% of heat usage to be supplied from renewable sources by 2020. It is estimated that renewable heat currently accounts for 1.4% of forecast total heat consumption in 2020

2.13 Taking into account the environmental baseline and review of existing environmental objectives, the key questions to be considered under this heading are:

  • Will the plan contribute to climate change mitigation by helping to reduce greenhouse gas emissions?
  • Will the plan help to achieve adaptation to climate change?

Air

2.14 Air pollution can have repercussions for many aspects of quality of life, including human health and biodiversity. Air quality objectives outlined in the Air Quality Strategy for England, Scotland, Wales and Northern Ireland have been met over much of the country, but there are still a number of pollution hotspots in some urban areas where objectives for nitrogen dioxide and particles continue to be exceeded. In Scotland, the energy sector and transport are the key sources of air pollution.

2.15 Local Air Quality Management Areas ( AQMAs) have been declared in Aberdeen, Edinburgh, Dundee, Falkirk, Fife, Glasgow, Midlothian, Perth and Kinross, Renfrewshire and South Lanarkshire. 20 All but two of these have been declared as a result of transport related emissions of nitrogen dioxide and/or particles. The local authorities concerned are developing action plans outlining how they intend to tackle the issues identified. Further advice on air quality and planning can be found in the Local Air Quality Management Policy Guidance published by the Scottish Government in February 2009:

2.16 Taking into account the environmental baseline and review of existing environmental objectives, the key questions to be considered under this heading are:

  • Will the plan have adverse effects on air quality?
  • Is the plan likely to have any specific implications for existing AQMAs?

Population and health

2.17 Air pollution reduces average life expectancy 21 and is estimated to result in more than 32,000 deaths annually in the UK. Asthma and wheezing problems are persistent and more prevalent in deprived households in Scotland. 22 The RAP is also potentially relevant to the well being of the population more generally, with the renewables sector as a whole having the potential to help provide a more diverse and affordable supply of energy. A household is considered to be in fuel poverty where 10% or more of household income is spent in fuel. This is a significant problem in Scotland.

2.18 Taking into account the environmental baseline and review of existing environmental objectives, the key questions to be considered under this heading are:

  • Will the plan avoid generating adverse effects on health arising from environmental pollution?
  • Will the plan support the broader aim of reducing fuel poverty?

Biodiversity, flora and fauna

2.19 Of the UKBAP priority habitats and species found in Scotland, in 2005 around 33% of habitats and 32% of species were stable or are improving, whilst 30% of habitats and 14% of species were in decline 23. The condition of the remainder was unknown, unclear or fluctuating. SNH undertakes monitoring of the condition of Scotland's designated sites. Figures produced in 2006 24 show that 71% of the sites monitored were found to be in favourable or 'unfavourable recovering' condition. Further restoration and enhancement will therefore be required to meet the stated targets of achieving favourable condition in 80% of sites by 2008 and 95% by 2010.

2.20 SEPA provided further information on the current state of Scottish biodiversity in its 2006 State of the Environment Report. It noted that climate change is already having an impact on biodiversity, and that other processes including urbanisation, land use change and the spread of non-native species will make it difficult to reach stated biodiversity targets. 25SNH's natural heritage trends reports identified loss of neutral grassland, particularly in the uplands and islands, dwarf shrub heath, acid grassland and bog as key problems. This was confirmed by the broader Countryside Survey 2003, which monitored change in groups of habitats between 1990 and 1998, and showed that there was a substantial decrease in semi natural habitats in Scotland in this period (-88,000 hectares).

2.21 Climate change is likely to exacerbate established pressures on biodiversity resources, and therefore has the potential to increasingly compromise site based conservation measures. As a result, there has been a growing emphasis on the development of broader scale measures for protection and conservation including the commitment in the Scottish Biodiversity Strategy to removing barriers to species movement and dispersal and positively improving connections between habitats. Data gathered for UKCIP under the MONARCH project 26 provide further insights into the likely repercussions of climate change for the natural environment. Although it is predicted that most species will find 'suitable climate space' when climate change affects their habitats, the northern range margins of species are predicted to move northwards, and some species will take over areas where others had previously been important (e.g. spread of bracken and western gorse into montane / upland heath habitats). The Central Highlands was one of four case studies for this research, demonstrating problems such as loss of suitable climate space for dwarf shrub land cover and, conversely, a large increase in the area which is suitable for neutral grassland. The modelling also showed that changes affecting the canopy and ground flora will have eventual implications for the composition and structure of the woodland.

2.22 Taking into account the environmental baseline and review of existing environmental objectives, the key questions to be considered under this heading are:

  • Will the plan have effects on protected sites or species?
  • Will the plan impact on wider habitat networks including woodlands?

Soil

2.23 Scotland's soils are diverse and differ markedly from the rest of the UK. Soils provide a range of services, acting as a carbon sink, supporting agriculture, contributing to water quality and flow, and sustaining landscape character and biodiversity. The Scottish Soil Framework summarises research in 2006 27 prioritising challenges to soil in Scotland as follows:

1. Climate change and loss of organic matter are the most significant threats to the functioning of Scottish soils.

2. Construction (sealing), loss of biodiversity and acidifying and eutrophying deposition also represent significant threats to soil function.

3. Threats most commonly associated with cultivation (erosion, loss of structure, compaction) were not considered to present particularly high risks at a national scale. However, these can be locally significant, for example in peatland areas or those rich in known and unknown archaeological features as well as impacting on water quality.

4. Threats from contamination by heavy metals or by land management were also noted, but regarded as more locally significant than a national issue.

2.24 The biodiversity of Scotland's soils was described in the 2006 research (Towers et al, 2006) as a 'true scientific frontier'. It is widely recognised that some specifically Scottish habitats, such as Scots pine woodland, machair and deep peat have unique soil characteristics. Some soil organisms are included within BAPs as protected species, including fungi and ephemeral soil dwellers, but much more research is required to allow the ecological value of soil in Scotland to be fully understood.

2.25 Soils form an important and integral element of landscapes, with varying soil properties supporting different patterns of vegetation. Damage to soil, particularly that caused by changes to moisture content, contamination and invasive species will have repercussions for both biodiversity and landscape 28 and there is also growing concern that these problems could be exacerbated by climate change. Linking with air pollution issues, acidification and nutrient enrichment continue to affect both soil and water resources, and this in turn can have significant repercussions for biodiversity. Although key pollutants are in decline, 29 acidification is particularly problematic in upland areas including the small areas of the Cairngorms, Galloway and the western and central Highlands where there are also potentially high value ecosystems. SEPA has emphasised that biological recovery from acidification is slow and could be hindered to some extent by climate change as a result of the long timescales required. 30

2.26 The Scottish Soil Framework Consultation Document proposed mechanisms to address the key threats to soils nationally. 31 Soils are closely linked with climatic conditions, and climate change will have a range of effects on its organic composition. The Parliamentary Office of Science and Technology reported in 2006 32 that 2.2 million tonnes of topsoil has been eroded in the UK, with mapping suggesting that in Scotland upland erosion is an issue in the Highlands including parts of Caithness and Sutherland, and the Cairngorms. Water erosion is a problem in the coastal parts of Tayside. It is estimated that 44% of arable land in Scotland is at risk of water erosion, and that 20% of upland peat, shallow and rocky soils are eroding. Urban soil degradation through sealing and contamination is an issue throughout the UK, with planning potentially playing a role in mitigation such as separation of construction, demolition and excavation waste and topsoil for recycling, and use of permeable paving and vegetated roods to reduce potential for flooding.

2.27 Taking into account the environmental baseline and review of existing environmental objectives, the key question to be considered under this heading are:

  • Will the plan result in damage to soil, including soil sealing, erosion, pollution or nutrient depletion?

Water

2.28 Scotland's freshwater resources range from coastal rivers to standing water bodies (such as peaty lochs and lowland lochs), fen and raised bog wetlands. 33 The water environment supports a wide range of migratory waders and wildfowl, fish, seabirds, seals, whales and dolphins. 34 Marine and freshwater biodiversity has improved following the decline of heavy industry and improved regulatory regimes. However, some key species remain a concern: the Scottish Biodiversity Strategy notes that 50% of native freshwater species in Scotland were thought to have declined in 2000. Scotland's freshwater and sea lochs are internationally important in terms of biodiversity.

2.29 SEPA's draft River Basin Management Plans ( RBMPs) for the Scotland and Solway-Tweed River Basin Districts 35 set out key pressures and risks on the water environment within their respective areas, including.

  • Abstraction and flow regulation from a range of activities including hydropower, water supply and agriculture;
  • Point and diffuse pollution from agriculture, sewage disposal, forestry, urban development, mining and quarrying and aquaculture are also recorded;
  • Morphological change from agriculture and forestry;
  • Non-native invasive species from recreational, sporting and leisure activities.

2.30 Scotland's coasts and seascapes are of significant value as a result of their scenic and ecological qualities. SNH note the outstanding character and great diversity of the coast, ranging from broad machair plains to shifting dunes, sandy beaches, and several hundred uninhabited islands. The rocks and landforms of the coast form important habitats and are important geological resources in their own right. Scotland's marine biodiversity is remarkably diverse, supporting many mammals including common and grey seals, whales, dolphins, harbour porpoises, otters, sharks and turtles, seabirds, and migratory bird species, and many fish species. Seabed composition and plant life and micro-organisms contribute to this diversity and richness. 36

2.31 Taking into account the environmental baseline and review of existing environmental objectives, the key questions to be considered under this heading are:

  • Will the plan result in acidification, eutrophication or other contamination of water bodies?
  • Will the plan result in a significant depletion of water resources, through planting or abstraction required?

Material Assets: Transportation

2.32 Scotland has a lower rate of car ownership than the rest of the UK with 51 as compared to 58 vehicles per 100 population. 37 The car is the mode of transport for over three quarters of total distance travelled. Travel distance overall has grown in Scotland, from an average of 4652 miles annually in 1985/6 to 7376 miles annually in 2005/6. The proportion of car use as part of the total has also grown over the same period. In terms of freight transport, 172.4 million tonnes of freight were transported by road in Scotland in 2006. This represented a steady increase between 1997 and 2006, whilst rail borne freight increased more substantially over the same period from 7.04 mtonnes in 1997 to 12.96 mtonnes in 2006. There was a steady decline in road traffic accident injuries and deaths in the same period.

2.33 Taking into account the environmental baseline and review of existing environmental objectives, the key questions to be considered under this heading are:

  • Will the plan generate significant additional road based transport movements?
  • Will the plan put pressure on existing transport infrastructure capacity?
  • Is the plan expected to make best use of sustainable modes of transport?

Material Assets: Waste Management

2.34 SEPA's waste data digest for 2006) 38 shows that total waste arising in Scotland increased in Scotland by 18% between 2004/5 and 2006/7. Of this, construction and demolition waste arisings grew most significantly, whilst growth in household waste was relatively consistent. Commercial waste arising fell in the same period, by 21%. At the same time, however, rates of recycling grew significantly between 20002/3 and 2006/7, and there were particularly high increases in recycling of some specific materials including plastics, soils and rubble, steel and aluminium cans and wood. There has also been a major increase in municipal waste which has been composted, by 420% between 2002/3 and 2006/7, with a large proportion of composted material arising from green waste. The total amount of biodegradeable waste disposed of in landfill sites (a key source of methane emissions) decreased steadily from 1.89 million tonnes in 2002/3 to 1.47 million tonnes in 2006/7, thereby exceeding national targets.

2.35 Taking into account the environmental baseline and review of existing environmental objectives, the key questions to be considered under this heading are:

  • Will the plan contribute to the aim of reducing waste and / or promoting its sustainable management?

Cultural Heritage, including architectural and archaeological heritage

2.36 The historic environment can be threatened by inappropriate development; economic decline, loss of viable use, population change and neglect in general. These issues are of relevance to both designated and non-designated sites. Land use change potentially arising from renewable energy generation, biomass and biofuel planting, could have implications for the historic environment.

2.37 Scotland has five World Heritage Sites (New Lanark, Edinburgh Old and New Towns, the Heart of Neolithic Orkney, St. Kilda and most recently the Antonine Wall). There are also 47,368 listed buildings and 628 conservation areas. The actual extent of archaeological remains in Scotland is unknown, with around 8,000 Scheduled Monuments representing only a small proportion of the 260,000 sites and monuments for which there are records, and the many more unrecorded sites and unknown resources throughout the country. Scotland's heritage designations are often supported by their landscape setting, and landscapes are imbued with cultural heritage value and significance. As noted above, the EC Landscape Convention notes the importance of recognising that landscapes are a product of the relationship between people and nature.

2.38 Information produced for the Scottish Historic Environment Audit 39 ( SHEA) includes a review of Ancient Woodland in Scotland, reflecting their combined cultural and natural heritage value. This draws on the Ancient Woodland Inventory compiled by SNH, which focuses on the continuing existence of woodland from 1759. At present Historic Scotland reports that there are 352,766 hectares of ancient woodland in Scotland, including ancient woodland of semi natural origin, long-established woodland of plantation origins and other (as included on the Roy map of 1750). These are distributed throughout the country, but are particularly concentrated in Lowland Scotland, and along the length of the east coast from the Lothians to the just north of the Dornoch Firth. Despite long term decline and fragmentation and their biodiversity value, ancient woodlands do not have statutory protection. However, they often overlap with other environmental protection measures such as SSSIs, allowing for ongoing monitoring of their condition in many cases and providing partial protection. They can provide uniquely diverse habitats in many cases. Planted Ancient Woodland Sites ( PAWS) are also a priority for restructuring and enhancement throughout the country, with enhancement measures being taken forward to reverse the negative effects of previous commercial conifer planting and improve their natural and cultural heritage value.

2.39 Taking into account the environmental baseline and review of existing environmental objectives, the key questions to be considered under this heading are:

  • Is the plan likely to generate significant effects on the historic environment by resulting in the loss of or damage to key resources?
  • Could the policy generate adverse effects on the setting of protected historic sites and buildings?
  • Does the plan provide an opportunity to enhance (where appropriate) the historic environment?

Landscape

2.40 Mapping of landscape character at a national level shows the dramatic variation between mountainous moorland areas in the north and west Highlands and Islands and the southern uplands, and the rivers, valleys, hills, farmland and urban areas in the lowlands. Scotland has 40 National Scenic Areas ( NSAs) covering more than 1 million hectares (12.7% of Scotland). These areas are of the highest landscape quality, reflecting nationally significant scenic value.

2.41 The European Landscape Convention ( ELC) calls for a broader approach to landscape protection and enhancement (going beyond designated areas), and states that landscapes across Europe are being transformed as a result of a number of factors, including settlement expansion, transport and infrastructure and the economy. 40 The Scottish Landscape Forum 41 has highlighted the following key issues for Scotland's landscapes:

  • Poor settings of urban and peri-urban communities, impinging on well-being and quality of life;
  • Loss of diversity in the landscape and dilution or erosion of distinctive character;
  • Generally poor standards of design;
  • Decline and loss of natural and cultural heritage features;
  • Attrition of undeveloped, remote and wild countryside, and coasts;
  • Erosion of rural character of Lowland Scotland - loss of features, intrusion of noise and artificial light reducing tranquillity, suburbanisation; and
  • Direct and indirect impacts of climate change, with the latter arising from mitigation action (e.g. increased renewable energy generation).

2.42 These pressures vary between different landscape settings. Collectively, the series of landscape character assessments prepared by SNH provides a useful 'snapshot' of the characteristics of Scotland's landscapes and this is translated to a strategic level in SNH's Natural Heritage Futures Statements. As part of this, SNH prepared an assessment of Scotland's landscapes that sets out nationally significant resources, pressures and opportunities 42. The report notes that landscapes are constantly evolving, but that forces for change vary between gradual natural processes and human activity that results in more pronounced and often negative change. Key challenges include land use change, incremental change arising from development and changes in perceptions. The different qualities of regional landscapes are set out, and it is emphasised that some areas are much more vulnerable to specific types of change than others (e.g. transitional landscapes, strategic transport corridors etc).

2.43 Landscape vulnerability arises from a complex combination of sensitivity and distinguishing characteristics, historic and projected change and levels of activity or pressure. Further examination of these varying sensitivities and pressures for change can be used to help provide a clearer national spatial perspective on landscape management issues that can in turn inform the assessment of the REF.

2.44 SNH policy on wild land 43 reflects on wildness in Scotland's countryside, and supports the policy approach within National Planning Policy Guideline ( NPPG)14, which introduced this as a nation-wide consideration for land use planning. SNH emphasises the need for a protective approach to wild land - in terms of the provisions of the planning system and in relation to broader land use. The paper distinguishes between 'wildness' - the quality enjoyed - and 'wild land' the places where wildness is best expressed. It also notes that wild land is not necessarily confined to remote areas of the north and west, also being found closer to settlements. The policy explains that experiences of wildness and wild land vary depending on individuals' experiences, perceptions and preferences, but notes that in many cases it can be inspirational as it supports feelings of engagement with nature, solitude and sanctuary and is valued as a quality in its own right. There are also strong cultural meanings and resources underlying many areas of wild land.

2.45 SNH state that the value of wild land in Scotland rests on five main factors: scarcity; intrinsic quality; potential for nature; economic and accessibility. It sets out key pressures for change, including hydropower, afforestation; bulldozed roads; and access for outdoor recreation. It maps wild land, based on areas of land which have their remotest point 2, 5 or 8km from public roads. This shows the importance of wild land in the north of Scotland (Cairngorms, the Monadhliath; Knoydart; Ben Dearg, east of Loch Broom and its hinterland, Ben Alder, the west Inverness-shire glens to Kintail block, Black Mount - Etive, and the Fisherfield Forest in Wester Ross). In the south sufficiently extensive areas of wild land are limited to the Merrick block, which has being changed by extensive afforestation. Application of more stringent criteria for defining land significantly reduces its extent. NSA designation covers most but not all of the key areas of wild land.

2.46 SNH also produced interim guidance on impact assessment in relation to Wild Land, although this is due to be updated. 44 The guidance notes that there is increasing pressure on this diminishing resource as a result of a range of developments and land management activities. It also notes that although impact assessment guidance covers wild land to some extent, it does not reflect broader values and subjective experiences associated with wild land.

2.47 The Scottish Landscape Forum ( SLF) summarised research demonstrating the value of landscapes to Scotland. 45 Public benefits include improved health and wellbeing, community regeneration, enjoyment and recreation, education, tourism and rural diversification. Further, the Forum emphasised the economic value of landscapes as a result of their role in stimulating investment and retaining employers and employees, and use in marketing for tourism but also in terms of traditional products.

2.48 Taking into account the environmental baseline and review of existing environmental objectives, the key questions to be considered under this heading are:

  • Is the plan likely to generate adverse effects on landscapes by changing their character or visual qualities?
  • Is the plan likely to affect any particularly valuable or sensitive landscapes?

Likely evolution in the absence of the RAP

2.49 In the absence of the RAP, it is expected that the existing environmental trends noted above would continue. However, although much of the RAP sets a framework for future action, it is important to note that the plan as a whole will ultimately deliver a significant shift towards increasing the share of Scotland's energy that is produced from renewable sources. In the absence of such a policy it is possible that the total contribution of renewable energy in Scotland to meeting climate change targets may not be met, with substantially reduced benefits for the environment as a whole. However, some renewable energy development may nevertheless be expected, perhaps focusing on a less diverse range of technologies than that which is supported by the RAP. Further significant effects from these ongoing development proposals are not expected, however, given that consenting and regulatory regimes already exist which should ensure that protection of environmental quality at the local level is achieved.

Summary of relevant environmental problems

2.50 It is important for the SEA of the RAP to focus on the environmental problems which are most relevant to its proposals and in particular the specific target of increasing the share of heat which is delivered by renewable technologies. Based on the evidence above, a number of key environmental problems are summarised in Table 4 below.

Table 4: Summary of environmental problems relevant to the RAP

Problem

Supporting data

Implications for the RAP

Growing impact of climate change arising from greenhouse gas emissions

UKCIP02 scenarios and associated interpretative research e.g. SNIFFER Handbook

The RAP should maximise the contribution of the energy sector to climate change mitigation, whilst also taking into account the need to advance effective adaptation measures over the long term. There is potential for the RAP to generate further emissions, e.g. by disturbing soils with high carbon content.

Air pollution arising from the energy and transport sectors

Ongoing monitoring associated with agreed targets for air quality and AQMAs

The RAP has the potential to contribute positively or negatively to the objective of improving air quality. Specific issues around biomass technologies and air quality have been considered within the SEA.

Health problems arising from air pollution

Health Statistics

The RAP should avoid making recommendations that could increase risks to health as a result of air pollution (see above). The SEA s potential effects of the RAP on health.

Growing levels of fuel poverty

Social Statistics

The RAP can link a climate change driven policy agenda with national level concerns regarding fuel poverty.

Long term effects of climate change on biodiversity

Climate change data as noted above, with sector specific reports (e.g. MONARCH)

The RAP could help to reduce this environmental problem as a result of its contribution to climate change mitigation. However, inappropriate policy or proposals could exacerbate this issue.

Condition of protected habitats and species

Site condition monitoring

Some components of the RAP have the potential to increase pressure on some protected sites and species. The SEA has therefore explored how these effects can be avoided.

Damage to soil resources, arising from land use change

Data gathered to inform the Scottish Soil Framework

Proposals within the RAP could exacerbate existing soil quality and stability issues, including biomass feedstock planting and harvesting. The SEA has explored this in further detail.

Share of waterbodies that are not expected to reach good ecological status by 2015

Data gathered as part of the RBMP process

Some aspects of the RAP have the potential to conflict with the emerging priorities defined within RBMPs. These could include water pollution and effects on the water table arising from different planting regimes for biomass feedstocks.

Continuing need to promote the waste hierarchy as a means of reducing resource use and emissions from the sector

SEPA Waste Digest

The RAP has a role to play in contributing to sustainable waste management through energy from waste proposals that in turn contribute to renewable heat. These have been considered within the SEA in relation to the broader context of the waste hierarchy.

Loss of, damage to, or changes to the setting of cultural heritage resources, including known and unknown, protected and unprotected resources

Information currently being gathered to inform the Scottish Historic Environment Audit

The proposals within the RAP could directly or indirectly impact on cultural heritage resources. The SEA has therefore explored the risks arising from policy proposals and scope for mitigation.

Impacts on landscapes arising from land use change and forestry expansion

SNH Natural Heritage Futures

The RAP may directly or indirectly increase rates of land use change which in turn could affect landscape quality. The SEA has explored the specific effects arising from biomass planting with a view to informing the development of this aspect of the RAP.

2.51 This evaluation of the environmental context within which the RAP sits has shown that there are a range of environmental problems and policy objectives, which the plan can seek to address. The SEA has provided an opportunity to define how the content of the RAP can maximise its positive contribution to global and national objectives relating to climate change and wider environmental protection, whilst avoiding generating adverse effects on some more locally significant resources.

Page updated: Wednesday, July 01, 2009