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GROUNDWATER VULNERABILITY MAPS FOR PESTICIDES FOR FLANDERS
GROUNDWATER VULNERABILITY MAPS FOR PESTICIDES FOR FLANDERS
Jef Dams, Ingeborg Joris*, Jan Bronders, Aäron TrippaerDirk Vanden Boer, Griet Heuvelmans
Contact: *[email protected]
INTRODUCTION
» VMM (Flanders Environment Agency) is responsible forwater quality monitoring and status reporting in Flanders (N-Belgium)
» Frequent detects of PPPs and metabolites in (shallow) groundwater
2
2014
Pesticides in Flemish groundwater
INTRODUCTION
» Develop a tool to calculate groundwater vulnerability maps for PPPs» Substance-specific» As much as possible process-based (incl. saturated zone)» Making optimal use of available datasets and models» At different scales (Flanders and local)
» Use of this tool: 1. support monitoring strategies2. management of sensitive zones such as drinking water capture zones
3
Aim of the study
INTRODUCTION
Definitions groundwater vulnerability
4
Factors taken into account in assessing vulnerability
Europe US-EPA
Subsoil characteristics Intrinsic vulnerability Aquifer sensitivity or intrinsic susceptibility
Subsoil characteristics + substanceproperties
Specific vulnerability
Subsoil characteristics + substanceproperties + application
Risk Aquifer vulnerability
Groundwater vulnerability NRC (1993): “the tendency of or likelihood for contaminants to reach a specific positon in the groundwater system after introduction at some location above the uppermost aquifer”
Vulnerability saturated zone:- Fast spreading lower concentrations- Low spreading higher concentrations
OVERVIEW METHODOLOGY
5
Tool for vulnerability maps
Flanders-scale Local-scale
Hybrid method Process based method
Leaching calculations Leaching calculations
Indices for saturated zoneFlowpath calculations
Simulation scales
METHODOLOGYLEACHING
» Hydrological model SWAP» Pesticide fate model PEARL
Leaching to groundwater - GeoPEARL
Groundwater depth(4 classes)
Soil map(536 units)
Land-use
METHODOLOGYFLANDERS-SCALE
Hybrid approach
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Leaching concentrations
Indices for saturated zone
Thickness of phreatic layer
Conductivity of phreatic layer
P90-concentrations over 20-yr period
+
» Leaching» process-based calculations
(GeoPEARL)» Saturated zone
» Indices
METHODOLOGYLOCAL SCALE
» Leaching concentrations with time from GeoPEARL
» Input to 1D-transport calculations along flowlines with F-LEACH (analytical solution of CDE taking into account sorption and degradation)
» Concentration at the receptor (screen) is calculated as a function of time
» For each of the grid cells in the capture zone 3 assessments are made:
1. Max. conc. at the receptor relative to applied dose2. Time of breakthrough at the receptor3. Ratio of mass reaching the receptor to mass
applied
» Vulnerability map for the capture zone indicating the critical zones contributing most to the PPP load in the well
Process based approach
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1D-transport alongflowline with
sorption/degradation(analytic)
GeoPEARL
MODPATH
(Brouyère et al., 2011)
METHODOLGYIMPLEMENTATION
Python tool
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RESULTS
» Example:» Vulnerability of phreatic groundwater in Flanders for pesticide x» Settings: properties of pesticide x (molmas, Koc, DT50,..) and typical application dose and
time, applied on entire Flanders as if maize
Flanders-scale
10
Conc
.[µ
g/l]
P90Leaching concentration
groundwater-vulnerability class
Vuln
erab
ility
Cl
ass
[-]
RESULTS
» Example:» vulnerability of pesticide x for a drinking water well in Western part of Flanders» Settings: pesticide properties and typical application data, applied on the whole entire
withdrawal area as if maize
Locale-scale
11 Pumping wells
Max. conc. relative to applied dose
Breakthrough time Ratio of mass reaching the receptor to mass applied
CONCLUSIONS
» Specific vulnerability for PPPs in Flanders/local scale to assist monitoring strategies
» Due to data constrains hybrid approach at Flanders-scale
» Local scale process based approach
12
More informationIngeborg Joris [email protected] Dams [email protected]
VITO, Environmental Modelling UnitTeam Water management & TechnologyVITO NV | Boeretang 200 | B-2400 Mol | Belgium