A practical approach to account for the bioavailability of metals Bruce Brown WCA Environment REPRESENTING Eurometaux November 25 th 2010.

Slides:



Advertisements
Similar presentations
C OPPER AND N ICKEL TMDL D EVELOPMENT: L OWER S OUTH B AY.
Advertisements

Outcomes of The Living Murray Icon Sites Application Project Stuart Little Project Officer, The Living Murray Environmental Monitoring eWater CRC Participants.
Colour and the d block. UV / Vis frequencies are have photons with energies of the sort of values needed to promote electrons from their ground state.
Britannia Mine: Environmental Impact Study of Treated Effluent Discharge Lee Nikl.
STRATUS CONSULTING The Biotic Ligand Model: Unresolved Scientific Issues and Site- and Species-specific Effects on Predicted Cu Toxicity Jeffrey Morris,
HydroQual Capabilities for Pathways Analysis in Support of Natural Resource Damage Assessment.
Front page picture Change picture by marking Picture, right click and choose send to front. Click on the icon in the middle of the picture and locate the.
Katrien Delbeke, ECI, Frank Van Assche,IZA- Europe Frank Van Assche,IZA- Europe On behalf of the Eurometaux Water Project Team Accounting for bioavailability.
PROTECTFP Work Package 1:- results from questionnaire and overview of tools for chemical assessment.
Environmental risk assessment of chemicals Paul Howe Centre for Ecology & Hydrology, UK.
End of Waste: Supporting quality & sustainability? Roger Hoare Environment & Business Manager Environment Agency (England & Wales) 24 January 2013.
End of Waste – Experiences from the UK Roger Hoare, Environment Agency 3rd October 2013 Malta 2013 IMPEL Conference on Implementation and Enforcement of.
University of Southern California Center for Systems and Software Engineering ©USC-CSSE1 Ray Madachy, Ricardo Valerdi USC Center for Systems and Software.
The EU Water Framework Directive and Sediments The Water Framework Directive was transposed into law in EU Member States at the end of Nearly two.
WG 3: Impact assessment ► Conceptual framework for impact assessment for xenobiotics in the urban water cycle ► Biotests as analytical tool ► Are we measuring.
Heavy metals (Pb, Cd and Zn) levels in roadside soils in Nairobi County.
WORKING GROUP 4 KEY DISCUSSION RESULTS TOPICS 2 & 3 International Workshop on the Safe Disposal of Low Level Radioactive Waste 03 to 05 February 2015,
1 Incorporation of bioavailability Patrick Van Sprang – ARCHE OECD Workshop on Metals Specificities in Environmental Hazard Assessment, Paris, 7-8 september.
Teezle TMatics M2M Platform & Solutions Overview January 28 th, 2014.
Use of ochre products for remediation of metal-contaminated soils and waters Kate Heal School of GeoSciences University of Edinburgh
Applications of Bayesian sensitivity and uncertainty analysis to the statistical analysis of computer simulators for carbon dynamics Marc Kennedy Clive.
ENVS 355 Data, data, data Models, models, models Policy, policy, policy.
Analysis and Visualization Approaches to Assess UDU Capability Presented at MBSW May 2015 Jeff Hofer, Adam Rauk 1.
University of Sunderland COMM80 Risk Assessment of Systems ChangeUnit 13 Overview of Riskit*: The Method and its Techniques * Further information available.
A unifying model of cation binding by humic substances Class: Advanced Environmental Chemistry (II) Presented by: Chun-Pao Su (Robert) Date: 2/9/1999.
Key issues of measuring the effectiveness of compliance assurance Eugene Mazur OECD Environment Directorate.
S. Sauvé1,2, A. Dumestre1, M. McBride1 and W. Hendershot2
PROTECTFP PROTECT recommendations – application in practice.
Joint European Commission – IMPEL Seminar on Environmental Inspections Wednesday 17 November 2010 Hotel Le Meredien, Brussels 1.
Quantitative Assessment of Cumulative Impacts: Challenges and Progress Lauren Zeise Cal/EPA Office of Environmental Health Hazard Assessment CAPCOA Workshop:
Setting Standards: The Science of Water Quality Criteria EA Engineering, Science, and Technology ® Presented by: James B. Whitaker Review of Annex 1 of.
Initial considerations of trace metal bioavailability: some regulatory experiences E. Unsworth 1, A. Peters 1, J. Comloquoy 2, M. Campbell 2 1 Scottish.
1 TASK 3.2 C CMEP Mandate Mario Carere, Chiara Maggi, Bernd Gawlik, Valeria Dulio.
Katherine von Stackelberg, ScD E Risk Sciences, LLP Bioaccumulation and Potential Risk from Sediment- Associated Contaminants in.
1 Workshop on Metal bioavailability under the Water Framework Directive Jorge Rodriquez Romero & Madalina David DG Environment D2 Gerrit Niebeek – NL Graham.
John Batty DEFRA UK Bratislava November Legal Background For any given surface water body, applying the MAC-EQS means that the measured concentration.
International Office for Water Prioritisation of substances under the WFD: Compilation of the comments WG E (4), Brussels, 15-16/10/2008.
Alternative Tier 2 Process Model Refinement, Implementation and Validation PTAC: March 20, 2014.
Rocky Harris Defra UK Issue 6 Biodiversity accounts and indices.
Front page picture Change picture by marking Picture, right click and choose send to front. Click on the icon in the middle of the picture and locate the.
Metal bioavailability under the Water Framework Directive Implementation in monitoring and assessment frameworks Implementation of Bioavailability 1.
Patricia Gillis Copper Sensitivity in Glochidia: Assessing the Effect of Water Composition on the Sensitive Larvae of Freshwater Mussels.
Activity on bioavailability- based approaches for metals in US and Canada Chris Schlekat (Ni) Eric Van Genderen (Zn) Bob Dwyer (Cu) Bill Stubblefield (OSU)
Adam Peters and Graham Merrington, wca Chris Schlekat, NiPERA
Implementing risk assessment tools
Development of Compliance Tools for Metals
Principles and Key Issues
Technical guidance to implement bioavailability-based environmental quality standards for metals Graham Merrington October WG Chemicals 2014.
ASSESSING THE ENVIRONMENTAL CONSEQUENCE OF POTENTIAL MAJOR ACCIDENTS
Outline Introduction Extending the validated boundaries of the BLMs – Progress? Nickel Copper Zinc Future BLM/User-friendly tool boundaries Regulatory.
Stefano Polesello CNR-IRSA, Italy
European Commission DG ENV Unit C1 Water
Successfully implementing EQSbiota?
Developing guidance with Member State-regulators to implement bioavailability-based environmentally quality standards for metals. Graham Merrington WG.
Assessing the value of measured data Day 1.
Bioavailability and Metals Standards- Workshop
Nickel Risk Assessment
Commission report on Art. 8 WFD Monitoring programmes
Introduction- Link with WG E activity CMEP PLENARY MEETING-PRAGUE
Paul Whitehouse Environment Agency, UK
Refined determination of metal availability in sediments (Acid Volatile Sulphide measurements) Presentation for the CMA meeting Paris, 17 November 2006.
Paul Whitehouse Chair, EG-EQS
Annual Implementing bioavailability meeting
BLM project in the Nordic countries
BLModel boundaries BIOmet tool is a read across tool based on the ‘full BLM’, used for EQS compliance assessment. Number of EU waters fell outside of the.
Water Framework Directive 2000/60/EC
Summing up and next steps
Workshop on metals bioavailability under the Water Framework Directive
Incorporating metal bioavailability into permitting – UK experience
Statistical Methods for Assessing Compliance – case studies Task 3.1B
Presentation transcript:

A practical approach to account for the bioavailability of metals Bruce Brown WCA Environment REPRESENTING Eurometaux November 25 th 2010

Slide 2 Metals EQSs are Evolving Existing methods based on total concentrations are poor predictors of potential environmental risk Need to monitor dissolved metals Biotic Ligand Models (BLMs) developed which predict toxicity extremely well BLMs appear complicated to implement – but are not!

Slide 3 Why bother to account for bioavailability? Many new metals EQSs are based on high bioavailability Wide scale failure of EQSs derived for metals if only considering face-value comparison with monitoring data. Enables resources and money to be focussed at those sites at real risk of harm

Slide 4 Perceived practical limitations when using biotic ligand models (BLMs) in the WFD Complexity of models Input hungry Resource intensity Practical difficulties How to use the outputs?

Slide 5 Solutions to the practical problems of implementing bioavailability in a regulatory frameworks Development of screening tools – only 3 inputs for Cu, Ni, Zn – DOC, pH and Ca) Tiered compliance assessment for metals Full automation possible within laboratory analytical system e.g. UK Outputs can be expressed as either bioavailable metal or site specific EQS

Slide 6 Screening Tools Comparison of Ni screening tool performance against NiBLM performance (all concentrations in µg dissolved Ni l -1 ) data from sites across the England and Wales (n ≈ 112).

Slide 7 Limited input data Output 1: Bioavailability-based PNEC Output 2: Site-specific risk characterization

Slide 8 The Tiered Approach

Slide 9

Slide 10 Nickel - Great Britain (n = 183) 1. Comparison with generic (100% bioavailable) EQS 2. Use of screening tool FAIL Pass Percentage pass rate = 97 % (n =122) (n = 61) (n =6) (n =116)

Slide 11 Nickel - France (n = 249) 1. Comparison with generic (100% bioavailable) EQS 2. Use of screening tool FAIL Pass Percentage pass rate = 95 % (n =29) (n = 220) (n =12) (n =17)

Slide 12 Nickel - Austria (n = 1779) 1. Comparison with generic (100% bioavailable) EQS 2. Use of screening tool FAIL Pass Percentage pass rate = 91 % (n =646) (n = 1133) (n =158) (n = 488)

Slide 13 Data Requirements Typically DOC, pH & Ca as minimum Potential need for guidance on best practice for producing DOC data? Can estimate DOC from dissolved Fe or UV absorbance but adds uncertainty

Slide 14 DOC Estimation by UV

Slide 15 Summary Accounting for metal bioavailability provides a robust metric by which to assess potential risks – and is linked to biology! Bioavailability can be applied within a tiered approach Simplified screening tools are available that: –Process large numbers of samples –Have only 3 inputs (in the case of Cu, Ni and Zn) –Fully automated Accounting for bioavailability does NOT present significant practical challenges Some changes to routine monitoring requirements probably needed e.g. Dissolved metals and DOC Implementation Guidance next year?