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Ljubljana, 10.09.2004 | Slide 1 Groundwater Quality Assessment Determination of chemical status and assessment on individual sites Austrian experience in implementation of Directive 2000/60/EC requirements Andreas Scheidleder Umweltbundesamt – Austria andreas.scheidleder@umweltbundesamt.at
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Ljubljana, 10.09.2004 | Slide 2 General Remark The risk (quality) assessment is still in process and under discussion. No procedure and no significance level is fixed. Regulations on EC level are still under discussion.
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Ljubljana, 10.09.2004 | Slide 3 Risk (Quality) Assessment Development of national guidance document Risk assessment on the basis of existing data (according to WG 2.1 IMPRESS) Well-founded assumption that the current network was designed to be a representative network which was continuously adapted Development of reporting structure appropriate maps and tables Tested and discussed in a pilot study Preliminary assessment provided to Counties for comment, amendment and for approval
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Ljubljana, 10.09.2004 | Slide 4 Legal Background Federal Water Act Hydrography Act Ordinance for Water quality Monitoring Ordinance for Groundwater Threshold Levels
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Ljubljana, 10.09.2004 | Slide 5 Monitoring and Network Monitoring ~ 1800+250 sites (slight changes) 4 times per year ~ 100 parameters (in 3 blocks) Quality Assurance Programme Publication of data and information Network adaptation until end 2005
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Ljubljana, 10.09.2004 | Slide 6 Risk assessment 1. Characterisation
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Ljubljana, 10.09.2004 | Slide 7 Risk assessment 2. Assessment of network
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Ljubljana, 10.09.2004 | Slide 8 Risk assessment 2. Assessment of network Preliminary assessment - Federal Level Groundwater bodies - Representativity Index Ru Groups of groundwater bodies - Thiessen polygons Final assessment - County Level Local expertise (e.g. hydrogeology etc.) Network assessed as representative partially representative not representative
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Ljubljana, 10.09.2004 | Slide 9 Risk assessment 2. Assessment of network Cl … Classsites < 33 <= sites < 55 <= sites < 10sites >= 10 Ru < 50 %Cl 4 > 0 % 50 <= Ru < 70 Cl 4 = 0 % Cl 3 > 50 % Ru >= 70 % Cl 4 = 0 % Cl 3 <= 50 % Deviation classes from average Network representative Cl 4 … > 400% Network partially representative Cl 3 … 200-400 Network not representative
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Ljubljana, 10.09.2004 | Slide 10 Risk assessment 2. Assessment of network Local expertise on County level over-rules preliminary assessment at Federal level considering Art 5 Analyses e.g.: GW-flow direction, Point and diffuse sources of pollution, Soil characteristics, Overlying strata Sampling site density and spatial distribution Hydrogeological representativity
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Ljubljana, 10.09.2004 | Slide 11 Risk assessment 3. Assessment of quality data
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Ljubljana, 10.09.2004 | Slide 12 Risk assessment 3. Assessment of quality data Quality Assessment Method Representative Network National criteria Not Representative Network Analogy conclusion from impacts - Modelling approach Partially Representative Network Combined approach - Average of national criteria and modelling Trend assessment Method Upward trend exceeding 75 % of parametric value (DWD)
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Ljubljana, 10.09.2004 | Slide 13 Risk assessment 3. Assessment of quality data Relevant Parameters only those parameters where a national threshold value and a parametric value in the drinking water directive (DWD) is available: Nitrate Atrazin Desethylatrazin Cadmium Bentazone Focusing on the GW-body level only !
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Ljubljana, 10.09.2004 | Slide 14 Representative Network National quality assessment criteria Laid down in the Ordinance for Groundwater Threshold Levels GW-body is at risk when in the assessment period (2 years) at least 50 % (or 30 % - still in discussion) of sites are endangered. A site is endangered when arithmetic mean exceeds threshold value. (excluded: sites with geogen background) At least 5 values per site At least 5 sites per GW-body
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Ljubljana, 10.09.2004 | Slide 15 Trend assessment Statistical significant upward trend Risk if trendline exceeds 75% of the parametric value of the DWD (WFD, Art. 17) Assessment period 1997–2002 (min. 5 years) Minimum 3 sites per body Average of average Quarterly aggregated data Treatment of values < LOQ
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Ljubljana, 10.09.2004 | Slide 16 Not Representative Network Modelling approach Best possible cause-effect-relationship between influencing factors and GW-Quality Risk assessment based on analogy conclusions from influencing factors to GW-Quality At groupes of GW-bodies without sites and where the monitoring network is not representative Weighted multifactoral Regression Estimation of GW-body mean
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Ljubljana, 10.09.2004 | Slide 17 Modelling approach Influencing factors about 150 influencing factors
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Ljubljana, 10.09.2004 | Slide 18 Modelling approach Influencing factors ~ 150 factorsbodyMuni.site CORINE Landcover, X r500m Precipitation, GeologyX Share of soil permeability (1-3) (FAO) X X Inhabitants, cattles X Agricultural statistics 1999 X Impacts on water by land use activity (1-5)X Type of site, depth to GWX Distance between site and next contaminated site (oil, CHC, Metals) X Possible influences around the siteX
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Ljubljana, 10.09.2004 | Slide 19 Modelling approach Influencing factors about 150 influencing factors Significance - 25-35 Interpretability Relevance - 90 Stability & Plausibility influencing factors 10 influencing factors
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Ljubljana, 10.09.2004 | Slide 20 Modelling approach Influencing factors 10 influencing factors Geology, precipitation and altitude Soil storage capacity Impacting/reliefing factors from agricultural statistics (e.g.: barley, root crops, maize) Impacting/reliefing factors from CORINE Landcover (e.g.: agriculture, vineyards)
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Ljubljana, 10.09.2004 | Slide 21 Modelling approach Comparison between monitored and predicted values (nitrate)
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Ljubljana, 10.09.2004 | Slide 22 Partially Representative Network Combined approach If monitoring network is only partially representative: Average of national criteria and modelling
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Ljubljana, 10.09.2004 | Slide 23 Outlook – EC level Groundwater Directive still under discussion - Nothing fixed!! Expert meeting of Council Environment Group on 1st Sept 2004 Many countries against “one out all out” – to be discussed Assessment on site level triggering risk – to be discussed Values < LOQ ½ LOQ – to be discussed Boarder points should be fixed – flexibility with countries Length of time series for trend assessment Aggregation for trend assessment still open Consideration of background for assessing environmental significance (75% - trend) – to be discussed Methodology for establishing threshold values (BRIDGE) Still Discussion NOT Decision
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Ljubljana, 10.09.2004 | Slide 24 Outlook – EC level Summary of discussion by Presidency forwarded to Council Environment Group Open discussion in working party on environment Mid Oct – Start of discussion for common methodology on establishing threshold values WG 2C: Developing guidelines for status and trend assessment when GWD is legally binding
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Ljubljana, 10.09.2004 | Slide 25 Groundwater Quality Monitoring and Assessment (chemical status and assessment on individual sites) Austrian experience in implementation of Directive 2000/60/EC requirements Andreas Scheidleder Umweltbundesamt – Austria andreas.scheidleder@umweltbundesamt.at
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