Zinc…essential for life Correction for natural background in risk assessment Example: Zinc Frank Van Assche International Zinc Association 168 Avenue de Tervueren 1150 Brussels Zinc…essential for life Regulatory context • A risk assessment on zinc and 5 zinc compounds was made under EU regulation 793/93/EC – Rapporteur country: The Netherlands – Published: ECB 2008 • Zinc case was first on essential element with significant background – Development of RA methodology needed • Effects assessments concluded at SIAM 20 (2005) Zinc is a natural element AIR: 40 - 100 ng Zn/m3 SOIL: 25-200 mg Zn/kg DW WATER: 3 - 40 µg Zn/l BIOMASS: 25200 µg Zn/g DW 3 Zinc Background (µg Zn (total)/l): variability in surface waters – – – – EU - lowland range: EU rivers in mineralised areas: N-American mountain streams: N-American Great lakes: (dissolved) – Coastal waters: – Open ocean: – FOREGS : EU « stream waters » (dissolved) • 10P • 50P • 90P 3 – 40 40 - >200 < 10 < 0.3 0.5 – 1 0.001-0.06 0.7 2.7 18 4 The Optimal Concentration range for Essential Elements deficiency Optimal dose toxicity 5 The Optimal Concentration range for Essential Elements depends on BG Shift to higher sensitivity Shift to lower sensitivity deficiency Optimal dose toxicity 6 Zinc…essential for life Background may be significant in metals RA • For some metals natural background can be significant – as compared to derived PECs and PNECs – because of conditioning/acclimatisation • background needs to be integrated in quantitative risk assessment. Zinc…essential for life Definition of natural background range for RA purposes (zinc case, µg total Zn/l) • Zuurdeeg (1999): – 4 µg/l and 35 µg/l (EU lowland brooks in unpolluted areas in Northern Europe) – geometric mean: 12 µg/l - taken as the “best estimate” for the natural BG concentration in fresh surface waters • EU countries: lower end of observed ranges: 3 µg Zn/l • EU RA – 12µg total Zn/l as “best-estimate” mean value (4.5 µg dissolved) – 3 µg total Zn/l as “lower limit” conservative value (1.1 µg/l dissolved) – Confirmed by FOREGS (2006) • BG can be defined based on measured data in “unpolluted” areas relevant for the assessment Zinc…essential for life Integration of background in the EU zinc RA • To integrate natural BG in the EU RA, 2 specific approaches were developed: – selection of ecotoxicity data on (BG-) relevancy criteria – Application of the “added risk” approach Zinc…essential for life 1) Selection of ecotoxicity data on (BG-) relevancy criteria • “Zinc background” criterion to select ecotoxicity data for relevancy for EU waters – to account for conditioning of test organisms to natural (EU-relevant) Zn BG • a minimum value for relevant background zinc concentration (dissolved) was set at “around 1 µg/l” (cfr EU relevant range) • Maximum value: ~25 µg Zn/l • ensure test data (for PNEC setting) are relevant for EU aquatic ecosystems. Sensitivity to zinc as function of BG Culture conditions species < 2 µg Zn/l 2 < [Zn] < 50 µg Zn/l >50 µg Zn/l Ephydatia : 3.3 Daphnia magna : 59 Selenastrum c. : 8 Ceriodaphnia: 31 N-American Great Lakes 8 Ephydatia : 34 Daphnia magna : 365 Selenastrum c. : 37 Chroococcus: 200 Synecoccus: 390 Dreissenia: 400 Potamopyrgus: 75 Hyallella: 42 Phoxinus: 50 Salmo: 210 European lowland rivers 10 36 +/- 5 2.5 100 +/- 3 17 Corbicula: 25 Salvenilus: 530 Jordanella: 51 Pimephales : 78 corresponding ecosystem Number of species NOECs Mean NOEC (µg Zn/l) HC5 (µg Zn/l) Hormidium : 1000 Scenedesmus: 1400 Mineralised areas 2 1175 +/- 1 / Zinc…essential for life 2) The “added risk” approach (after Struijs et al 1997) • Only the antropogenic part of PEC and PNEC is considered for RA – “PECadd” and “PNECadd” – Background is assumed not to contribute to toxicity (essentiality!) • The added risk concept was applied at 2 levels of the zinc RA: – Conversion of NOEC values to “NOECadd” values – Conversion of monitored PEC values into PECadd. Zinc…essential for life Conversion of NOEC values to “NOECadd” values • if NOEC based on measured zinc concentration • subtraction of (estimated) background • NOECtotal (measured) – BG = NOECadd. – correction not required in case the test medium was reconstituted water (without zinc background), or, in case of natural waters, if the (estimated) background was very low. • If NOEC based on a nominally added concentration • corresponds directly with a NOECadd. • HC5/PNEC derived from NOECadd values: HC5/PNECadd Zinc…essential for life Conversion of monitored PEC values into PECadd • If measured concentrations: correction for (estimated) background: PEC – BG = PECadd . – Often significant for zinc (BG vs total). – 12µg/l and 3µg/l (Total Zn)) applied as a mean and worst case estimate, resp. Water Measured concentration Background PECadd (µg Zn total/l) (µg Zn total/l) 3 12 6 (specified) 30 21 22 (µg Zn total/l) River A 33 River B 28 • If modelled emissions: directly PECadd Zinc…essential for life conclusions • For some metals, background can be significant and needs integration in RA – At level of data selection: setting relevancy criterion corresponding to the area – At level of PEC/PNEC: e.g. by applying the added risk approach • Corrections at level of PNECadd, PECadd – Background can be measured in (relatively) unpolluted waters Integrating background in RA: case zinc Effect assessment Selection of ecotoxicity values for relevancy to EU environment, criterion: natural zinc background Exposure assessment Measured zinc concentrations in EU waters NOEC values relevant for the EU environment Conversion to NOECadd values Subtraction of (estimated) natural background Species sensitivity distribution PNECadd PECadd Zinc…essential for life drawbacks • Main difficulty is defining a realistic natural background at the local/regional scale. – information is often lacking – generalisations may often fail to capture variability at the local and temporal scale. • Especially in areas where water quality is influenced by specific metal-enriched geology, the natural background should be assessed in a more precise way, since it can as such result in significant exceedance of the PNEC.
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