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Pest Risk Analysis Research in Europe
:Developments from EU project PRATIQUE
Alan MacLeod
Pest Risk Analyst
PRA Workshop
Brasilia
March 2012
Outline
• Introduction to Fera
• PRATIQUE
– Datasets
– Consistency
– Mapping
– Factors that ease eradication
– Computer Assisted PRA (CAPRA)
• Work in China & Russia
What is Fera?
• A government science agency which provides the UK’s food and environment sectors with:-
• expert scientific advice
• regulatory services
• applied research facilities and
• emergency responsiveness
National Assembly for Wales, Agriculture Department
Forestry Commission
- Forest Research
UK
London
•York
Contingency Response
Policy
Plant health and Seeds
Inspections
Bee Disease
Pest Risk Analysis
Diagnosis and
Taxonomy
Containment and
Eradication
Seed Listing and
marketing
Pollinator Research
National reference laboratory
Phytophthera
Plant Clinic
National Bee Unit
Plant Breeders
Rights
Plant Protection
Pesticide Usage
Biorefining
Operator Exposure
Pesticide Fate
Environmental Risk
Ecotoxicology Usage Surveys
Wildlife Poisoning
Natural products
Ecochemistry Nano
materials
Risk Assessment
Environmental Risk
Badgers and TB
Bird Strike Control
NonNative Species
Secretariat
Rabies in Wildlife
Vaccine Deployment
Wildl ife Damage
Control Methods
Fertility Control
Welfare
Bird Radar
Wind Farm EIA
Disease Dynamics
Invasive Species
Population Monitoring
Eradication Programmes
Wildlife Management
Proficiency testing
Food Authenticity
Food Contaminants
Environmental Contaminants
Pesticides
Veterinary medicines
Packaging
Testing Standards
Mycotoxins National
Reference Laboratory
Chemical residues
Food Safety
Advice from “farm to fork”
Animal feed
Genetically modified
organisms
Plant Health Plant Protection
Animal welfare &
wildlife diseases Microbiology
food chain hazards
Food chain contaminants Food additives
Food authenticity,
Novel foods
PRATIQUE: Permission granted to a ship or boat to
use a port on satisfying the local quarantine
regulations or on producing a clean bill of health
Acknowledgments 6 European research institutes (Fera, CIRAD, INRA, JKI, LEI, PPI)
5 European universities (IBOT, Imperial, UNIFR, UPAD, WU)
2 international organisations (CABI & EPPO)
2 partners from outside Europe (CRCNPB & Bio-Protection)
Food and Environment Research Agency
PRATIQUE: Key partner skills
Natural scientists
• Entomologists
• Plant pathologists
• Ecologists
• Phytosanitary experts
• Plant protection
managers
Social scientists
• Economists
Engineering
• Risk analysts
• Computer
scientists
• To enhance PRA techniques for the EU / EPPO
(i) by assembling datasets required for PRA for
the whole EU (27 countries)
(ii) by conducting multi-disciplinary research to
enhance techniques
(iii) by providing a user friendly decision support
system
PRATIQUE Aims
What is the PRA area?
Why did PRA in Europe need
enhancing?
1. PRA is a young area of study (first schemes developed only in 1990s)
2. Lack of data to analyse the risks posed by pests to countries in the EU or EPPO
3. Developments outside of PRA can be applied in PRA
4. PRA procedures are complex* for the risk analysts and the decision makers. Tools needed which brings all factors together
*EPPO PRA scheme (2009): over 50 questions, 5 level risk rating, 3 levels
of uncertainty - no mechanisms to combine ratings and derive risk
• Whilst there is a history of plant health*, formal
pest risk analysis is relatively young
• ISPM No. 2 Guidelines for PRA (1996)
• ISPM No. 11 PRA (more detail)(2004)
– tells us what to do but not how
– “Climatic modelling systems may be used…” (2.2.2.2)
– “There are analytical techniques which can be used in
consultation with experts in economics….” (2.3.2.3)
• As well as standards, need tools and resources
1. Young discipline
* MacLeod et al. (2010) Food Security, 2, 49-70
2. Lack of Data for PRA
• PRA quality is highly dependent on data
• EU and EPPO need to produce PRAs relevant for all member states
• Data from some member states difficult to obtain
• Language barriers
• Crop, pathway, and impacts-related data often very difficult to obtain
Wrote to EU Member States
• Collected electronic / web accessible data
sources (e.g. Crop / pest distribution)
• Import data, other economic datasets, yields…
• PRA area data e.g. land use, climate data, soil
types, …
• Pest management data
• Reviewed datasets
Datasets on imports, production, &
economics
Datasets relating to climate, soils…
Dataset quality and usefulness evaluations Dataset
Categories
Total
evaluated
Data rating
(overall)
Total
retained
A B C D U
Pests in the current area
of distribution 236 50 61 53 70 2 166
Pathways and economic
datasets 118 5 37 38 16 22 96
Area under consideration
for the PRA (land use
etc)
266 30 105 91 27 13 239
Pest management 155 24 66 28 8 29 147
Score Definition
A Essential, high quality and widely applicable
B Good quality but applicable to specific regions
C Narrow or very limited usefulness or overlap with categories A or B.
D Unreliable, contain too many errors or are generally irrelevant
U Cannot currently be assessed due to a language barrier
Data sets linked to computer
assisted PRA (CAPRA)
3. To enhance techniques
• Consistency
• Mapping
• Spread
• Economic impact
Consistency
• Reviewed 43 schemes & guidelines seeking best practice on ensuring consistency: – Biosecurity and plant health standards
– PRA schemes
– Weed risk analysis schemes
– Animal health schemes
• Consistency in risk rating more likely if: – use a clear and structured framework – ask unambiguous questions – obtain responses from groups of assessors – provide examples to help guide risk rating, e.g. CFIA – mechanism to combine risk elements (risk matrices)
EPPO (2009) PRA Scheme - Format
• Series of questions: Categorisation (19)
Entry (14)
Establishment (15)
Spread (3)
Impacts (16)
Risk management (44)
• Explanatory Notes
• Responses required: 5 level risk rating
3 level uncertainty score
Written justification
• No method for summarising
each section or overall risk
and uncertainty
Consistency
Revised EPPO scheme • To improve structure
• Reword some questions = clearer meaning
• Provide biological examples for rating guidance at 5 levels for each question
• A visualiser developed to review questions
• Mechanism to combine risk elements
• Matrix models provided to summarise risk and
uncertainty from many questions and sub-questions
PRAs can be long
documents
Qualitative Impact Assessment Methods: Visualiser to
review responses to questions
• Each question’s risk
rating from very low (1)
to very high risk (5) is
put on the graph as a
bubble
• The larger the size of
the bubble, the greater
the uncertainty
• Each cluster of
questions has the same
colour
• A bar marks the
summarised rating
(here for entry) of the
expert(s)
• Visualisation of the
author’s judgment, no
modelling!
Qualitative Impact Assessment Methods: Visualiser to
review responses to questions
• Each question’s risk
rating from very low (1)
to very high risk (5) is
put on the graph as a
bubble
• The larger the size of
the bubble, the greater
the uncertainty
• Each cluster of
questions has the same
colour
• A bar marks the
summarised rating
(here for entry) of the
expert(s)
• Visualisation of the
author’s judgment, no
modelling!
Consistency
Was no mechanism to combine factors that contributed to risk (risk elements)
Examined the concept of risk matrix
Used in USA & Australia
Risk matrix
Likelihood of introduction
Establishment
Low Medium High
Entry
Low Low Low Medium
Medium Low Medium High
High Medium High High
Matrix model for Entry (does not show uncertainty)
Risk matrix with uncertainty
Likelihood of introduction
Establishment
Low Medium High
Entry
Low Low Low Medium
Medium Low Medium High
High Medium High High
High
Low
Med
ium
Hig
h
Low Medium
Entr
y
Establishment
Uncertainty distributions
Very Unlikely
Unlikely
Moderately likely
Likely
Very likely
The distributed scores/ratings corresponding to the three levels of uncertainty
Very Unlikely / Minimal (Score / rating of 1)
Low Medium High
Unlikely / Minor (Score/ rating of 2)
Low Medium High
Moderately Likely / Moderate (Score / rating of 3)
Low Medium High
Likely / Major (Score / rating of 4)
Low Medium High
Very Likely / Massive (Score / rating of 5)
Low Medium High
The distributed scores/ratings corresponding to the three levels of uncertainty
Very Unlikely / Minimal (Score / rating of 1)
Low Medium High
Unlikely / Minor (Score/ rating of 2)
Low Medium High
Moderately Likely / Moderate (Score / rating of 3)
Low Medium High
The distributed scores/ratings corresponding to the three levels of uncertainty
Very Unlikely / Minimal (Score / rating of 1)
Low Medium High
Unlikely / Minor (Score/ rating of 2)
Low Medium High
Moderately Likely / Moderate (Score / rating of 3)
Low Medium High
Likely / Major (Score / rating of 4)
Low Medium High
Very Likely / Massive (Score / rating of 5)
Low Medium High
Uncertainty rating
Qu
estio
n/
risk e
lem
en
t sco
re
Low uncertainty: 90%
confidence that rating is
correct
Medium: 50% confidence
that rating is correct
High uncertainty: 35%
confidence that rating is
correct
(after Intergovernmental
Panel on Climate Change,
2005)
Assignment based on the
beta & truncated normal
distribution
Matrix model with uncertainty
Matrix models
Have generic models for
• Entry
• Establishment
• Spread
• Impact
Could combine likelihood of entry, establishment, spread and impact to show overall pest risk
Loss of detail when combine all elements
Can be difficult to agree how to combine elements (low likelihood : high impact)
Risk mapping
Global Annual Degree Days base 10°C (from Baker, 2002)
Maps can help risk assessors
World Potato Production (from Monfreda et al., 2008)
Why do we need a DSS for risk
mapping?
• General maps of climate, current pest distribution, crop
distribution or other factors do not directly indicate pest risk
• Risk maps can be very useful in PRA but guidance is
needed :
– To advise when appropriate to map (may not be needed)
– May be inappropriate to map predictions (data problems)
– Mapping requires significant modelling and mapping
skills, resources and time
– Maps can be created by a confusingly wide variety of
methods
– Maps can produce misleading results
Climatic mapping: Models
• Inductive techniques – Maxent
– Diva-GIS (BIOCLIM / DOMAIN)
– OpenModeller (8 algorithms)
– DK-GARP
– OM-GARP
– BIOCLIM
– Environmental Distance (~ DOMAIN)
– Envelope Score
– Support Vector Machine (SVM)
– Climate Space Model (CSM)
– Artificial Neural Network (ANN)
– CLIMEX match climates
• Deductive techniques NAPPFAST: Phenology and
Generic Infection Models
Diva-GIS (Ecocrop) [Based on species’ physiological characteristics]
• Integrated techniques CLIMEX compare locations
Climatic Mapping DSS
Asks questions to help decide if should map, and is so what
technique to use
Is it appropriate to map climatic suitability? (sub questions)
What type of organism is being assessed and what are the key
climatic factors affecting distribution?
How much information is available on the climatic responses of
the pest?
What category of location data is available?
Based on the type of organism, the information available on its
climatic responses and the category of location data, how
well is each climatic mapping method likely to perform?
Pest location data category
N Pest location data category Availability
1 Native range locations only
2 Native plus exotic range locations
3 Locations biased to the periphery of the range
4 Locations biased to the centre of the range
5 Few location data points
6 Very few location data points
7 Erroneous locations included
8 Locations influenced by natural barriers
9 Locations influenced by seasonal invasion
10 Distribution constrained by hosts
11 Regional distribution data only
12 Locations influenced by climate change
13 Location category unknown
Climate
Response
Information
Availability
Location Data Category
Methods + ++ +++ 1 2 3 4 5 6 7 8 9 10 11 12 13
Phenology
models
CLIMEX
match
CLIMEX
compare
Regression
models
KEY
Climatic response rating or location data category irrelevant to model
functioning Method poorly adapted to climatic response or location data category - results
very difficult to interpret Method moderately well adapted to climatic response or location data
category - results moderately difficult to interpret Method well adapted to climatic response or location data category - results
relatively straightforward to interpret
“Traffic Lights” to summarise performance of
different model based on availability of data on
the pest’s distribution and responses to climate
Area of potential establishment for
Diabrotica virgifera virgifera
Hosts Climatic suitability Area of potential
establishment & =
Area at highest risk
Sandy soils Host distribution Maize output not on
sandy soils Total maize output
Climate suitability Maize output not on
sandy soils Area at highest risk
& =
& =
Climatic Mapping: Tutorials and
manuals
• How to run several models,
e.g. Diva-GIS, Maxent,
Openmodeller Desktop and
CLIMEX,
• How to compare model
outputs
• How to interpret the results
Risk Mapping Conclusions
• The PRATIQUE DSS enables assessors to create
and combine maps to display:
– the area of potential establishment
– the area where plants are at highest risk (i.e areas
most suitable for the pest and of highest "value")
• useful for prioritising surveillance programmes
• Link to spread models
• Link to economic models
Spread: generic spread models
created
• Spatial process (spatial explicit) models
Radial rate expansion
Radial rate expansion (random entry point)
Dispersal kernel
Spread models for Diabrotica
Radial expansion model
Dispersal kernel model
Diabrotica v. virgifera spread 1992-2011
Spread – example result
Dispersal kernel model
Showing A. glabripennis spread
from 4 outbreak sites over 30
years.
Based on Climex model
Colours: % population
abundance
white < 10-6 %,
yellow,
orange
red > 10%
2
1
2
2
2
11
1
2
1
2
1
1
p
u
r
p
p
p
purf
Establishment: A. glabripennis
(Years for development, Climex)
4+ or not possible 4 years 3 years 2 years 1 year Years for development
Economic modelling
• Simple qualitative approach
• More complex quantitative approach
– Partial budgeting
– markets based (partial equilibrium)
Analysis of previous eradication
efforts
• > 170 campaigns (102 species)
(41 invertebrate species, 26 pathogens, 27 plant species)
• For each campaign ask 96 questions
• Seek to identify factors for eradication success
• Linear mixed effect models (LMMS) & classification and
regression trees (CART) applied
FINDINGS
• Small infestations (< 4,000 ha) are easier to eradicate
• Eradications in man-made habitats are more successful
• Natural habitats provide a major challenge
• Fungi most difficult to eradicate
Pluess et al. 2012. Biological Invasions, DOI 10.1007/s10530-011-0160-
4. Provide a user friendly DSS
• Previous EPPO Scheme (2009) difficult to use
• For the analyst – Many questions (most detailed system)
– Some seem repetitive
– Difficult interface
– Difficult to make consistent judgements
– Difficult to summarise
• For the decision maker – Lengthy documents produced
– Difficult to focus on key elements
User friendly DSS
• PRATIQUE provided
• a computerised EPPO PRA scheme incorporating PRATIQUE outputs
• Revised structure
• Reworded questions
• Rating guidance
• Links to datasets
• Guidance documents
• Can share PRA document (for group work)
EPPO Computerised PRA Scheme
(CAPRA)
Experimental studies
Sentinel trees in Asia
• To produce a dataset of potential Asian pests of
selected woody plants not yet introduced into Europe
Beijing suburban area
Continental conditions
Fuyang, nr. Hangzhou
Warm and humid climate
(Dr. Fan Jian-tin;
Zhejiang Forestry University)
Sentinel trees in Asia
Beijing
• 400 seedlings of 4 species exported
• 177 seedlings survived after a long stay in customs
• planted in a semi-urban nursery 5th May 2007
Abies alba- 60
Quercus suber- 50
Quercus ilex- 48
Cupressus sempervirens- 19
•Monthly survey
•No serious insect damage
observed until June 2008
•Alternaria sp. found on Abies
•Unidentified fungi on
Quercus and Cupressus
Sentinel trees in Asia
Hangzhou
• 598 young trees of 7 species planted
• Each 1m – 1.5m tall
• planted in a forestry region May 2008 •More than 50 species of
insects during summer 2000
Most yet unidentified
Some highly damaging
e.g. tussock moth on oaks
Arboreta Surveys
• Far East Russia (Siberia): surveys of pests on
European trees and shrubs in arboreta
Harsh Siberian climate
not suitable for many
European plants
Maritime climate
Novel method to obtain lists of potential
plant pests before introduction
• Sentinels in China colonised by:
97 insect species
24 symptomatic infections
• Russian arboreta
Of the many insect species, 30 high risk species
identified
106 symptomatic infections and 75 fungal species
on 56 woody plants
• BUT significant identification problems
• Future International Plant Sentinel Network?
Comparison of methods
Arboreta Sentinel trees
Logistics - “Simple” - Complicated
No. of plant species - Many - Few
Statistics - Poor - Robust
Weaknesses - No seedling pests - No mature tree pests
- Mostly foliage pests
- Lethal pests - Travel and plantation
difficult to assess stress
Complementary methods
Both require strong local links !
Thank you Obrigado
Food and Environment Research Agency, Sand Hutton, York, YO41 1LZ
Food and Environment Research Agency
Ecological activities occur across various temporal and spatial scales
Millennia
Centuries
Years
Months
Days
Hours
cm m km 100 km 1,000 km
Landscape evolution
Impacts of Invasive species
Forests develop
El Nino events
Adapted from Turner, Dale & Gardner (1989) Landscape Ecology 3 (3/4) 245-252
Climate change
Local land use change
Trees grow
Annual crops Where risk assessors
aim to inform All year round crops
The scale at which much field research is performed
Infection