Www.geology.sk 29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013 Health risk estimate for groundwater and soil contamination in the.

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29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013 Health risk estimate for groundwater and soil contamination in the Slovak Republic – a convenient tool for identification of risk areas 1 Fajčíková K., 1 Cvečková V., 1 Rapant S. 1 State Geological Institute of D. Štúr, Mlynská dolina 1, Bratislava, Slovak Republic

Origin of this research has gone with new idea to find mechanism for map visualization of quantitative assessment of health risks from contamination of geological environment in the Slovak Republic by combining international principles and methodology of health risk assessment with methodological procedures used in environmental geochemistry that would be easy to understand and usefull in decision make process 29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013

Objective of the work was based on this idea and includes: Quantitative estimation of health risk to residents living in the Slovak Republic of exposure to contaminated groundwater (adult population) and soils (adult and child population) Identification of potential risk areas within the country based on map visualization. 29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013

Background of the work Identification and characterization of:  distribution of chemicals in groundwater and soils,  contamination of geological environment and sources of contamination, Within environmental-geochemical mapping programme in the Slovak Republic at:  national level – Geochemical Atlases of the Slovak Republic at the scale 1: ,  regional level – environmental-geochemical maps of selected regions at the scale 1: th International conference SEGH, 8-12 July Toulouse, FRANCE 2013

Sources of groundwater and soil contamination in the Slovak Republic: Background of the work Main geogenic (natural) sources Main anthropogenic sources Geogenic-anthropogenic sources (e.g. historical mining areas) 29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013  specific rock types and associated mineralization occurrences and ore deposits (e.g. hydrothermal vein mineralization associated with granitoids and metamorphic rocks, low- sulphide mineralization associated with Neogene volcanics, Paleozoic sediment-hosted mineralizations) Increased groundwater and soil contents of potentially toxic elements: As, Pb, Zn, Cu, Hg, Sb  Mining activities, Metallurgy, Agriculture, Waste industry, Other industrial activities (chemical industry, refineries etc.), Transport etc. Increased groundwater and soil contents of various chemical elements / components: As, Cd, Hg, Pb, Ni, Fe, Mn, Al, Zn, Cu, Cr, NO 3 -, SO 4 2-, NH 4 + etc.

Background of the work Output: Environmental – geochemical regionalization of the Slovak Republic (Rapant et al. 2004) 29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013

Background of the work Data source for health risk estimate for groundwater and soil contamination in the Slovak Republic 29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013 Datasets of groundwater samples and soil samples were transformed in mean values of respective chemical elements and components for single administrative units of the Slovak Republic (municipalities, districts, regions) based on grid data interpolation - calculation of arithmetic means for grid cells falling into bounds of every single administrative unit

29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013 Example for surface distribution of arsenic in groundwater in municipalities of the Slovak Republic Background of the work

29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013 Background of the work Example for surface distribution of arsenic in soils in municipalities of the Slovak Republic

Mean values for Slovak municipalities for following contaminants with defined toxicity data were included in calculation of health risk estimates: Groundwater – As, Ba, Cd, Cu, F, Hg, Mn, NO3, Pb, Sb, Se, Zn Soils - As, B, Ba, Be, Cd, Cu, F, Hg, Mn, Mo, Ni, Pb, Sb, Se, Zn Data evaluation Exposure assessment Toxicity assessment (IRIS database) Risk characterization Chronic effects: principle of REFERENCE DOSE (RfD) was applied („existence of „safe“ dose) Carcinogenic effects: principle of cancer slope factor (CSF) was applied („no dose is safe“) CHRONIC RISK CANCER RISK RISC Workbench – software used for calculations Health risk estimate – US EPA methodology Groundwater and soil contents (C) – specific value, Other exposure data – model values for (US EPA) Exposure route - ingestion 29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013

Analyzed media ParameterValueUnitReference BW Body weight70kgUS EPA, 1991 AT*Averaged exposure period - cancer risk25 550dayUS EPA, 1989a Groundwater AT*Averaged exposure period - chronic risk25 550dayUS EPA, 1989a CWGroundwater concentration of chemicalSpecific locallymg l -1 IRDaily water intake2l day -1 US EPA, 1989b EFExposure frequency365day year -1 US EPA, 1989a EDExposure duration70yearUS EPA, 1989a Soils AT*Averaged exposure period - chronic risk23360dayUS EPA, 1989a CSSoil concentration of chemicalSpecific locallymg kg -1 IRDaily soil intake50mg day -1 US EPA, 1991 FI Fraction ingested from contaminated source 1-US EPA, 1991 EFExposure frequency40day year -1 US EPA, 1999b EDExposure duration64yearUS EPA, 1991 CFConversion factor10 -6 kg mg -1 US EPA, 1989a Input exposure parameters were following: for adult population Health risk estimate 29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013

Analyzed media ParameterValueUnitReference BW Body weight15kgUS EPA, 1991 AT*Averaged exposure period - Chronic risk2190dayUS EPA, 1989a Soils CSSoil concentration of chemicalSpecific locallymg kg -1 IRDaily soil intake100mg day -1 US EPA, 1991 FIFraction ingested from contaminated source1-US EPA, 1991 EFExposure frequency120day year -1 US EPA, 1999b EDExposure duration6yearUS EPA, 1991 CFConversion factor10 -6 kg mg -1 US EPA, 1989a for child population Input exposure parameters were following: Health risk estimate 29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013

Health risk estimate Database of Integrated Risk Information System (IRIS) was used for definition of input toxicity parameters: Chronic risk: reference doses Cancer risk: Arsenic as known human carcinogen - cancer slope factor for arsenic 1.5 mg.kg -1 -day ElementRfDConfidence As0.0003medium B0.2high Ba0.2medium Be0.002low-medium Cd gw high Cd soil 0.001high Cu0.04- F0.06high Hg Mn0.14medium Mo0.005medium Ni0.02medium NO 3 1.6high Pb Sb0.0004low Se0.005high Zn0.3medium - high 29 th International conference SEGH, 8-12 July Toulouse, FRANCE 2013