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Habitats Directive: Air Quality and
Ecological Impact Assessment
Natural England’s View
Alastair Burn
CIEEM/IAQM Workshop, July 2015
Air pollution risk to England’s Natura 2000 sites
SACs
Source: UK CL Focal Centre, 2015
• 96% SACs and 91% SSSIs in England exceed
critical loads
• Biodiversity 2020 - air pollution as threat to
biodiversity.
• UK Biodiversity Indicators – Indicator B5a:
ecological impacts of air pollution
• Habitats Directive reporting – air pollution
category - threat & pressure
Regulation of sources
Main sources of nitrogen deposition are NOx from
combustion (traffic/industry) and NH3 (mostly from
agriculture); although the relative importance will
depend on location
Regulatory decisions need to be made in the context
of:
•wide range of impacts/ sources
•high background levels of nitrogen deposition
•air quality impacts not reflected in assessment of
site condition
•uncertainties in risk assessment
Uncertainties in air quality risk assessment
Natural England’s actions to improve our ability to
address air pollution impacts
To support regulatory decision-making and to reduce some of the
uncertainties we are :
1. Improving our approach to assessing site condition
2. Developing tools to tackle unregulated sources
3. Developing an holistic approach to deal with the range of
impacts at a site (Site Nitrogen Action Plans)
1. Improving assessment of site condition
• Joint work with JNCC, NRW, SNH & NIEA.
• To develop a Decision Framework that provides a means of attributing nitrogen
deposition as a contributory factor to unfavourable condition on protected sites.
• The framework incorporates both national/research information and site based
information, including:
• the N deposition at the site and a measure of its certainty
• how the deposition relates to the critical load range for that habitat and a
measure of certainty around that critical load range
• site-based evidence of N impact.
2. Tackling unregulated sources
Through the Rural Development Programme for England:
•Countryside Stewardship Scheme –incentives include capital
grants for woodland (buffer) creation, slurry store covers,
reduced fertiliser input
•Countryside Productivity Scheme –grants towards eg innovative
equipment for slurry management, managing ammonia
emissions
•Nitrogen-use-efficiency Integrated Project – advice and
incentive for investment in equipment and innovative technology
to reduce N losses
© Natural England/ Peter Roworth
3. Dealing with a range of impacts: Site Nitrogen
Action Plans
Environmental Impact Assessment
• Important to recognise the potential impacts on ecosystems
• Consider the full range of sources associated with a development
• Check the habitat type and notified features
• Use best available information in assessments and relevant
benchmarks:
– Air Pollution Information System (www.apis.ac.uk)
Alistair Burn  - Natural England's View

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Alistair Burn - Natural England's View

  • 1.   Habitats Directive: Air Quality and Ecological Impact Assessment Natural England’s View Alastair Burn CIEEM/IAQM Workshop, July 2015
  • 2. Air pollution risk to England’s Natura 2000 sites SACs Source: UK CL Focal Centre, 2015 • 96% SACs and 91% SSSIs in England exceed critical loads • Biodiversity 2020 - air pollution as threat to biodiversity. • UK Biodiversity Indicators – Indicator B5a: ecological impacts of air pollution • Habitats Directive reporting – air pollution category - threat & pressure
  • 3. Regulation of sources Main sources of nitrogen deposition are NOx from combustion (traffic/industry) and NH3 (mostly from agriculture); although the relative importance will depend on location Regulatory decisions need to be made in the context of: •wide range of impacts/ sources •high background levels of nitrogen deposition •air quality impacts not reflected in assessment of site condition •uncertainties in risk assessment
  • 4. Uncertainties in air quality risk assessment
  • 5. Natural England’s actions to improve our ability to address air pollution impacts To support regulatory decision-making and to reduce some of the uncertainties we are : 1. Improving our approach to assessing site condition 2. Developing tools to tackle unregulated sources 3. Developing an holistic approach to deal with the range of impacts at a site (Site Nitrogen Action Plans)
  • 6. 1. Improving assessment of site condition • Joint work with JNCC, NRW, SNH & NIEA. • To develop a Decision Framework that provides a means of attributing nitrogen deposition as a contributory factor to unfavourable condition on protected sites. • The framework incorporates both national/research information and site based information, including: • the N deposition at the site and a measure of its certainty • how the deposition relates to the critical load range for that habitat and a measure of certainty around that critical load range • site-based evidence of N impact.
  • 7. 2. Tackling unregulated sources Through the Rural Development Programme for England: •Countryside Stewardship Scheme –incentives include capital grants for woodland (buffer) creation, slurry store covers, reduced fertiliser input •Countryside Productivity Scheme –grants towards eg innovative equipment for slurry management, managing ammonia emissions •Nitrogen-use-efficiency Integrated Project – advice and incentive for investment in equipment and innovative technology to reduce N losses
  • 8. © Natural England/ Peter Roworth 3. Dealing with a range of impacts: Site Nitrogen Action Plans
  • 9. Environmental Impact Assessment • Important to recognise the potential impacts on ecosystems • Consider the full range of sources associated with a development • Check the habitat type and notified features • Use best available information in assessments and relevant benchmarks: – Air Pollution Information System (www.apis.ac.uk)

Editor's Notes

  1. Natural England’s role in determining objectives for sites and advising on impacts. As well as on-site management. 96% of SENSITIVE SACs, 93% SPAs , 91% of SSSIs In a large number of semi-natural habitats over large areas of England and the UK, the current deposition of ammonia/nitrogen from the atmosphere is above the critical loads for the protection of the ecosystem. Including designated sites. The critical load is the amount of pollutant below which significant harmful effects on specified sensitive elements of the environment do not occur according to current knowledge. This has significant implications for Biodiversity 2020 delivery and compliance with the Habitats Directive.
  2. SOx, O3, VOCs and heavy metals. But our focus is on N.
  3. The framework will provide a practical methodology for assessing the impacts of N deposition on protected sites in an objective way
  4. CPS – below EPR size threshold farms only
  5. Walton Moss
  6. Meanwhile it is important that regulators developers & consultants recognise the potential impacts, and use relevant info in assessments: APIS and SRCLs EIAs