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Transcript of Development of an integrated database for the management of accidental spills (DIMAS) Katrien Arijs...
Development of an integrated database for the management of
accidental spills (DIMAS)
Katrien Arijs Bram Versonnen Marnix Vangheluwe
Jan MeesWard VandenbergheDaphne CuvelierBart Vanhoorne
Colin JanssenAn Ghekiere
VLIZ
Supported by the Federal Science Policy
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Overview DIMAS project
Background
Objectives
Phases– Selection of substances
– Data collection
– Evaluation & interpretation
– Relational database
Data treatment & modelling
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Background
Accidents on sea
– prompt reaction: importance of immediate and accurate information on environmental partitioning, bioavailability and (eco)toxicity
– need for impact analysis tools
Currently: GESAMP, IMDG → limited use
– data not specifically marine
– long term effects?
=> expert judgement currently, slow reaction
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Objectives Objective DIMAS: development of an easy to interpret, reliable, up-
to-date database with data specifically for the marine environment
Involvement of different stakeholders → users committee
4 phases:
– Phase I: identification of compounds lists, transport data, criteria, 100 000 → 5 000 → 250
– Phase II: data collection phys-chem, ecotox (freshwater + marine), human
– Phase III: evaluation and interpretation data quality, freshwater → marine
– Phase IV: relational database, GUI and modelling reliable, simple, expandable, pictograms
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Selection substances (1)
Tiered approach
– Started with NSDB/IMDG/ESIS → IMDG, structure NSDB: 15,000 to 100,000 compounds
– Selection 2,000-3,000 substances:• IMDG: P, PP, ●
• COMMPS
• Ecotox
• Gesamp
• Priority substances EU (ESIS)
• …
– Further selection: intrinsic properties, expert judgement, input users committee, TRANSPORT DATA (RAMA)
– Validated against transport data from harbours
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Website(www.vliz.be/projects/dimas/)
Selection substances (2)
Selection of compounds
COMMPS Dump sites
EcotoxGesamp bulk-
packagedAnnex I
67-548-EECOSPAR
Den Haag Helcom Priority EU UNECE POP
ED NorthIMDG marine
pollutants
Involvementin spills
Lists and databanks
Initial list (5,000 compounds)
Final list (250 compounds)
Properties, expert judge-ment, transport, OSPAR dynamec, …
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Data gathering Physico-chemical data
– ECB-ESIS: • RAR European Commission
• IUCLID Chemical Data sheet
– NSDB
– peer reviewed literature
Ecotoxicological data– ECB-ESIS (RAR)
– US-EPA ECOTOX database (only peer reviewed data)
– ED-North database & UGent ECOTOX database
– peer reviewed literature
Human toxicological data– UGent ECOTOX database
– ECB-ESIS
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Data gathering: ecotox Water / sediment
Saltwater / freshwater
Acute / chronic toxicity
Different trophic levels:– fish– plants– algae– invertebrates
Different endpoints:– mortality– growth– reproduction– other
Data: few or none up to tens of papersE.g. cereals, cocos-oil (no data)
↔ anilin:• Water: > 60 acute, > 10 chronic• Sediment: some
− micro-organisms − other
NOT ENOUGH DATA!!
read across
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Phase III-IV
Data evaluation: quality data ecotox: ‘data reliability & relevance’
– Detailed quality screening of marine data (high relevance)
– Rough quality screening of freshwater data (lower relevance)
→ quality score depending on data source
e.g. RAR: reliable, EPA: not fully verifiable
Database– Input/storage data
– Lay-out database + output
– ‘modelling’: environmental concentrations, effect concentrations
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
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Data treatment, ‘modelling’ After data are entered in the database, exposure & effect
modelling is carried out
Exposure: environmental partitioning modelling (Mackay)– estimate of compound concentration in different compartments after an
accidental spill;
– based on amount of compound spilled & physico-chemical properties;
– can be automated (advantage when database is updated).
Effect: expressed as Potentially Affected Fraction (PAF)– estimate of % species that will be affected at a certain environmental
concentration;
– based on SSD (Species Sensitivity Distribution) approach with a log-logistic model fitted to the data;
– can be calculated for acute and chronic data;
– can be automated (advantage when database is updated);
– easy to interpret.
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Exposure modelling (1) Mackay level I: estimates the equilibrium partitioning of a quantity of
organic chemical between the different compartments (marine-specific environment was used → no soil compartment)
Input: amount of compound spilled & physico-chemical parameters of the compound
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Exposure modelling (2) Output: partitioning
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
Effect modelling (1)
Gather + input all toxicity data
Assess quality (reliability and relevance)
Bring data to same level / units (e.g. LC50, NOEC)
Order data (LC50, NOEC)
Plot cumulative number of species (%) against endpoint (LC50, NOEC)
Fit curve (log-logistic)
Read % of species affected at given (estimated) water concentration after spill
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
PAF 23%
Daphnia
Microcystis
Pimephales
10000 100000
g/l)
Species Sensitivity Distribution (SSD)
0%
20%
40%
60%
80%
100%
10 100 1000
Concentration (
Cum
ulat
ive
prob
abili
ty
Concentration 1 mg/L
Effect modelling (2)
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Low risk (< 5% PAF): < 1,500 mg/L
Attention (5-25% PAF): 1,500-3,000 mg/L
Major risk (> 25% PAF): > 3,000 mg/L
Example: acute effects acetonitrile
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .Conclusion
Integrated and multi-disciplinary database embedded in a fully web-enabled searching graphical user interface:
http://www.vliz.be/projects/dimas/
This tool will increase transparency and allow for rapid communication in case of an accidental spill
First beneficiaries: people directly involved in the first phase of a contingency plan
Final indirect beneficiaries: general public, who will be better informed and ultimately better protected
VLIZ
EURAS
Rijvisschestraat 118, Box 3,9052 Gent, Belgium
Tel.: +32 (9) 257 13 99
Fax: +32 (9) 257 13 98
www.euras.be
LETAE
J. Plateaustraat 229000 Gent, Belgium
Tel.: +32 (9) 264 37 75
Fax: +32 (9) 264 37 66
www.milieutox.ugent.be
VLIZ
Pakhuizen 45-528400 Oostende, Belgium
Tel.: +32 (59) 34 21 30
Fax: +32 (59) 34 21 31
www.vliz.be
http://www.vliz.be/projects/dimas