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The right evidence for the job
Data and uncertainty in ecological assessment of
air pollution
Susan Zappala; Susan.Zappala@jncc.gov.uk
Routes to Clean Air 2019; IAQM
Overview
• JNCC’s role
• Risk to UK ecosystems from air pollution
• Assessing these effects
• Data and evidence
• Uncertainty
• Examples of ecosystem effects
• From the literature
• In the field
• UK Projects to address these issues
JNCC’s Role
• Provide evidence and advice on, e.g.:
• air pollution impacts on the natural environment;
• monitoring and assessing impacts;
• links between biodiversity and air quality policy; and
• research requirements.
• Site condition guidance
• UK co-ordination (eg Inter-agency Air Pollution Group)
• International collaboration
Air Pollution Effects on Ecosystems
N Critical load exceedance
SACs (2015-2017)
SAC A/SSSI
England 94.9 87.1
Wales 94.9 97.7
Scotland 80.6 72.9
NI 98.0 87.2
UK 89.7 85.8
Percentage of sites with
nutrient N CL exceedance
2015-2017
NH3 Critical level
exceedance (2014-16)
Rowe et al 2019 - Defra Critical Load Exceedance Trends Report
Exceedance (µg m-3)
No Exceedance
Lower plant critical level
Higher plant critical level
Assessment Data
Assessment
decision
Habitat
Sensitivity
(Benchmarks)
Conservation
Objectives
Ecological
monitoring
data
Predicted
magnitude of
change from
proposal Background
Air Quality
Historical
pollution
Confounding
factors
Challenges for Interpreting
Assessment Data
• Data availability
• Data applicability
• Model uncertainty
• Other pollutions
sources and
confounding factors
• Cumulative/ additive
emission source
effects
• Country-specific
requirements
Reasonable
Scientific Doubt
Data availability
and applicability
Nationally
applicable, Publicly
available data
Site specific,
Variable availability
Highly specific,
limited availability
National evidence/
modelling
Site specific
monitoring data
Detailed study data
Identifying Issues:
Common Indicators of nitrogen deposition effects
Response variable Acid
grassland
Bog Upland
heath
Lowland
heath
Sand
dunes
Species composition     
Total species richness     
Bryophyte species
richness

Lichen species richness  
Forb species richness  
Graminoid species
richness
 
Caporn et al 2016; NECR210
Relating air quality to
ecosystem damage: Lichen
Bosanquet 2019; Transect studies; Natural Resources Wales Report 298
Nitrogen sensitive Usnea and Evernia
Centre of Dinefwr Deer Park
Nitrogen tolerant Xanthoria
Gelli-aur College Farm (ca 3.5km)
Acute Effects: Lower Plants
Images: Áine O’Reilly, NIEA/DAERA 2019
Healthy Sphagnum Impacted Sphagnum
Ammonia 8 to14 µg m-3
Ballynahone Bog, Northern Ireland
Pinking of Cladonia
Ammonia 8 µg m-3
Acute Effects: Higher Plants
Áine O’Reilly, NIEA/DAERA 2019
Algae on Heather
Ammonia 8 to14 µg m-3
Ballynahone Bog,
Northern Ireland
Algal Slime on Trees
Ammonia 33 µg m-3
Moninea Bog,
Northern Ireland
Sutton 2007; Moninea Bog Assessment
Long-term Effects: Habitat
Increasing N deposition correlated with reductions in
species richness and changes in species composition
Caporn et al 2016; NECR210
Longterm Effects: Habitat
• Response of species
richness of N
deposition is curved for
many habitats.
• Bogs do not have
curvilinear response
• Sharp losses below
lower end of habitat
specific critical load.
• Losses continue
beyond upper end of
critical load range.
Caporn et al 2016; NECR210
Longterm Effects: Habitat
Control
8 kg N ha-1 y-1
Whim Bog, Scotland; Wet deposition nutrient experiment
with thanks to Netty van Dyjk for experiment data; Images Susan Zappala 2019
Nitrate plus PK
32 kg N ha-1 y-1
Ammonia plus PK
64 kg N ha-1 y-1
Indirect Effects
• Effects on feeding and
breeding habitat
• Reduced quality of
larval food
• Increased frost damage
• Increased sensitivity to
other factors
• Climate change
• Temperature
• Drought
www.apis.ac.uk; Calluna frost damage
Allan Drewitt 2014; High Brown Fritillary Butterfly
Including uncertainty: NDF
Jones et al 2016; JNCC report 579: Nitrogen Decision Framework
Nitrogen Decision Framework
Jones et al 2016; JNCC report 579: Nitrogen Decision Framework
Uncertainty and
Exceedance
Jones et al 2016; JNCC report 579: Nitrogen Decision Framework
Looking forward
• Air Pollution Information System (www.apis.ac.uk)
• Review of ecosystem effects gallery
• Nitrogen Decision Framework pilots and evaluations
• Towards the development of a Nitrogen Deposition Framework for vegetation
assessment in Scotland.
• Strategic thinking
• Northern Ireland Making Ammonia Visible
• Clean Air for Scotland Review
• Clean Air Zone Framework for Wales programme
• Defra Clean Air Strategy (England)
• New techniques
• Earth observation data, UAVs, meta-analyses
• Improved habitat mapping
• Data portals
Stay connected
• www.jncc.gov.uk
www.linkedin.com/company/jncc
www.facebook.com/JNCCUK
twitter.com/JNCC_UK
• Susan.Zappala@jncc.gov.uk

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The right evidence for the job: Evidence and challenge in ecological assessment - Susan Zappala

  • 1. The right evidence for the job Data and uncertainty in ecological assessment of air pollution Susan Zappala; Susan.Zappala@jncc.gov.uk Routes to Clean Air 2019; IAQM
  • 2. Overview • JNCC’s role • Risk to UK ecosystems from air pollution • Assessing these effects • Data and evidence • Uncertainty • Examples of ecosystem effects • From the literature • In the field • UK Projects to address these issues
  • 3. JNCC’s Role • Provide evidence and advice on, e.g.: • air pollution impacts on the natural environment; • monitoring and assessing impacts; • links between biodiversity and air quality policy; and • research requirements. • Site condition guidance • UK co-ordination (eg Inter-agency Air Pollution Group) • International collaboration
  • 4. Air Pollution Effects on Ecosystems N Critical load exceedance SACs (2015-2017) SAC A/SSSI England 94.9 87.1 Wales 94.9 97.7 Scotland 80.6 72.9 NI 98.0 87.2 UK 89.7 85.8 Percentage of sites with nutrient N CL exceedance 2015-2017 NH3 Critical level exceedance (2014-16) Rowe et al 2019 - Defra Critical Load Exceedance Trends Report Exceedance (µg m-3) No Exceedance Lower plant critical level Higher plant critical level
  • 6. Challenges for Interpreting Assessment Data • Data availability • Data applicability • Model uncertainty • Other pollutions sources and confounding factors • Cumulative/ additive emission source effects • Country-specific requirements Reasonable Scientific Doubt Data availability and applicability Nationally applicable, Publicly available data Site specific, Variable availability Highly specific, limited availability National evidence/ modelling Site specific monitoring data Detailed study data
  • 7. Identifying Issues: Common Indicators of nitrogen deposition effects Response variable Acid grassland Bog Upland heath Lowland heath Sand dunes Species composition      Total species richness      Bryophyte species richness  Lichen species richness   Forb species richness   Graminoid species richness   Caporn et al 2016; NECR210
  • 8. Relating air quality to ecosystem damage: Lichen Bosanquet 2019; Transect studies; Natural Resources Wales Report 298 Nitrogen sensitive Usnea and Evernia Centre of Dinefwr Deer Park Nitrogen tolerant Xanthoria Gelli-aur College Farm (ca 3.5km)
  • 9. Acute Effects: Lower Plants Images: Áine O’Reilly, NIEA/DAERA 2019 Healthy Sphagnum Impacted Sphagnum Ammonia 8 to14 µg m-3 Ballynahone Bog, Northern Ireland Pinking of Cladonia Ammonia 8 µg m-3
  • 10. Acute Effects: Higher Plants Áine O’Reilly, NIEA/DAERA 2019 Algae on Heather Ammonia 8 to14 µg m-3 Ballynahone Bog, Northern Ireland Algal Slime on Trees Ammonia 33 µg m-3 Moninea Bog, Northern Ireland Sutton 2007; Moninea Bog Assessment
  • 11. Long-term Effects: Habitat Increasing N deposition correlated with reductions in species richness and changes in species composition Caporn et al 2016; NECR210
  • 12. Longterm Effects: Habitat • Response of species richness of N deposition is curved for many habitats. • Bogs do not have curvilinear response • Sharp losses below lower end of habitat specific critical load. • Losses continue beyond upper end of critical load range. Caporn et al 2016; NECR210
  • 13. Longterm Effects: Habitat Control 8 kg N ha-1 y-1 Whim Bog, Scotland; Wet deposition nutrient experiment with thanks to Netty van Dyjk for experiment data; Images Susan Zappala 2019 Nitrate plus PK 32 kg N ha-1 y-1 Ammonia plus PK 64 kg N ha-1 y-1
  • 14. Indirect Effects • Effects on feeding and breeding habitat • Reduced quality of larval food • Increased frost damage • Increased sensitivity to other factors • Climate change • Temperature • Drought www.apis.ac.uk; Calluna frost damage Allan Drewitt 2014; High Brown Fritillary Butterfly
  • 15. Including uncertainty: NDF Jones et al 2016; JNCC report 579: Nitrogen Decision Framework
  • 16. Nitrogen Decision Framework Jones et al 2016; JNCC report 579: Nitrogen Decision Framework
  • 17. Uncertainty and Exceedance Jones et al 2016; JNCC report 579: Nitrogen Decision Framework
  • 18. Looking forward • Air Pollution Information System (www.apis.ac.uk) • Review of ecosystem effects gallery • Nitrogen Decision Framework pilots and evaluations • Towards the development of a Nitrogen Deposition Framework for vegetation assessment in Scotland. • Strategic thinking • Northern Ireland Making Ammonia Visible • Clean Air for Scotland Review • Clean Air Zone Framework for Wales programme • Defra Clean Air Strategy (England) • New techniques • Earth observation data, UAVs, meta-analyses • Improved habitat mapping • Data portals