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Vendredi 18 mai 2013 Integrated approach on global groundwater contamination of the area of the Dreieckland (F, CH, D) in an urban multisite context Susanne SCHOMBURGK, BRGM, D3E/EVE ([email protected])
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Page 1: Integrated approach on global groundwater contamination of ... · Integrated approach on global groundwater contamination of the area of the Dreieckland (F, CH, D) in an urban multisite

Vendredi 18 mai 2013

Integrated approach on global groundwater contamination of the area of the Dreieckland (F, CH, D) in an urban multisite context

Susanne SCHOMBURGK, BRGM, D3E/EVE ([email protected])

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Vendredi 18 mai 2013

BRGM-D3E

> 2> 2

Framework & issueThe europeen Water Framework Directive impose to establish the statusand to identify the most important pressures and their impact ongroundwater ressources (and the risk on their users/consumers).

>The densely industrialized area of the « Dreieckland » (=triangle of three countries) is affected by various pollutions in relation with several dumps, suspected having received hazardous waste of the chemical industrie of the Basel region (Switzerland) in the 50ies and 60ies

>After the first inventories of dumps in the Alsace region (ADEME/BRGM), several dumps have been classified to could likely contain waste that should be examined by priority 1.

>2005 to 2007, a first step of the impact assessment of groundwater quality downstream of these dumps has been realized by the public services BRGM and ADEME

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Vendredi 18 mai 2013

BRGM-D3E

> 3

Localisation of the area and aquifer of concern“Operational monitoring permits to establish the status of those bodies identified as being at risk of failing to meet their environmental objectives, and assess any changes in the status of such bodies resulting from the programs of measures.”

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> 4Vendredi 18 mai 2013

The challenges- An important but vulnerable groundwater body forming a water ressource that has to be protected because of the important uses (high density of groundwater wells), in particular by the GFD, Water management plan of the zone Ill-Rhine

- The chemical industry dump of the 50ies and 60ies from pharmaceuticaland agropharmaceutical-chemistry, as well as dye industry sludge and production waste with (often unknown) complexe chemistry with very little historical information about it.

- Very little knowledge of occurrence, nature, environmental fate and behavior (persistance, adsorption, etc.) and (eco)toxicity of these organic and organometallic compounds

- A mixture of aromatic amines, chlorobenzenes, sulfones, barbiturics, Halogenated volatile organic compound, nitro and/or chloro-(polyaromatics), heavy metals (Cu, Hg etc.), polar solvents, ...

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BRGM-D3E

> 5

Methodologie of the impact statement Step 1: Inventory of the zone of suspicion and the existing groundwater well network

- Dumps classed by envir. risk and GW-well network

- Classified industries and their GW-well network

- Former industries (closed, classed by contamination risk)

proposed network for the impact statement

Suisse

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Bourgfelden Lache LanghagBourgfelden Lache LanghagBourgfelden Lache LanghagBourgfelden Lache LanghagBourgfelden Lache LanghagBourgfelden Lache LanghagBourgfelden Lache LanghagBourgfelden Lache LanghagBourgfelden Lache LanghagALS-I-680324ALS-I-680324ALS-I-680324ALS-I-680324ALS-I-680324ALS-I-680324ALS-I-680324ALS-I-680324ALS-I-680324

Anc grav Durrenwaechter Bourgfelden stadeAnc grav Durrenwaechter Bourgfelden stadeAnc grav Durrenwaechter Bourgfelden stadeAnc grav Durrenwaechter Bourgfelden stadeAnc grav Durrenwaechter Bourgfelden stadeAnc grav Durrenwaechter Bourgfelden stadeAnc grav Durrenwaechter Bourgfelden stadeAnc grav Durrenwaechter Bourgfelden stadeAnc grav Durrenwaechter Bourgfelden stadeALS-I-680272ALS-I-680272ALS-I-680272ALS-I-680272ALS-I-680272ALS-I-680272ALS-I-680272ALS-I-680272ALS-I-680272

Kies AG LacheKies AG LacheKies AG LacheKies AG LacheKies AG LacheKies AG LacheKies AG LacheKies AG LacheKies AG LacheALS-I-680481ALS-I-680481ALS-I-680481ALS-I-680481ALS-I-680481ALS-I-680481ALS-I-680481ALS-I-680481ALS-I-680481

Rohkies EichhagRohkies EichhagRohkies EichhagRohkies EichhagRohkies EichhagRohkies EichhagRohkies EichhagRohkies EichhagRohkies EichhagALS-I-680299ALS-I-680299ALS-I-680299ALS-I-680299ALS-I-680299ALS-I-680299ALS-I-680299ALS-I-680299ALS-I-680299

Plate forme TIR / anc. décharge ville de BâlePlate forme TIR / anc. décharge ville de BâlePlate forme TIR / anc. décharge ville de BâlePlate forme TIR / anc. décharge ville de BâlePlate forme TIR / anc. décharge ville de BâlePlate forme TIR / anc. décharge ville de BâlePlate forme TIR / anc. décharge ville de BâlePlate forme TIR / anc. décharge ville de BâlePlate forme TIR / anc. décharge ville de BâleALS-I-680270ALS-I-680270ALS-I-680270ALS-I-680270ALS-I-680270ALS-I-680270ALS-I-680270ALS-I-680270ALS-I-680270

ancienne gravière proche stadeancienne gravière proche stadeancienne gravière proche stadeancienne gravière proche stadeancienne gravière proche stadeancienne gravière proche stadeancienne gravière proche stadeancienne gravière proche stadeancienne gravière proche stadeALS-I-680457ALS-I-680457ALS-I-680457ALS-I-680457ALS-I-680457ALS-I-680457ALS-I-680457ALS-I-680457ALS-I-680457

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Grav Durrenwaechter Bourgfelden nord RN266Grav Durrenwaechter Bourgfelden nord RN266Grav Durrenwaechter Bourgfelden nord RN266Grav Durrenwaechter Bourgfelden nord RN266Grav Durrenwaechter Bourgfelden nord RN266Grav Durrenwaechter Bourgfelden nord RN266Grav Durrenwaechter Bourgfelden nord RN266Grav Durrenwaechter Bourgfelden nord RN266Grav Durrenwaechter Bourgfelden nord RN266ALS-I-680271ALS-I-680271ALS-I-680271ALS-I-680271ALS-I-680271ALS-I-680271ALS-I-680271ALS-I-680271ALS-I-680271

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Grande sablière de Saint LouisGrande sablière de Saint LouisGrande sablière de Saint LouisGrande sablière de Saint LouisGrande sablière de Saint LouisGrande sablière de Saint LouisGrande sablière de Saint LouisGrande sablière de Saint LouisGrande sablière de Saint LouisALS-I-680323ALS-I-680323ALS-I-680323ALS-I-680323ALS-I-680323ALS-I-680323ALS-I-680323ALS-I-680323ALS-I-680323

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Sites Basias : risque COHV

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Décharges par Priorité

non définiedanger fortdanger moyen à fortdanger moyen

PP AEP éloignéPP AEP rapproché

Surveillance pour un constat d'impact du Dreieckland

Campagne d'analyse 2007

limite de la nappe d'Alsace

Décharges piézo de surveillance

IC piézo de surveillance

Isopièze Basses Eaux

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AEP non utilisées en 2005

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> 6Vendredi 18 mai 2013

Novoday

« International custom Platform »

How does a former dump look like today?

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> 7Vendredi 18 mai 2013

An example of a former gravel pit filled with hazardous wastes from the industrie and machefer in the 50ies wastes had been dumped in the open pit where groundwater outcrops

Core drilling (next slide)

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vendredi 24 mai 2013Vendredi 18 mai 2013

14 m thick waste layer include 4 m in the aquifer (saturated zone)

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> 9Vendredi 18 mai 2013

Dump Muttenz

Hazardous wasteExcavation by The LettenLandfill (2007)

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BRGM-D3E

> 10

Method of the impact assessment> Step 2: two groundwater

sampling campaigns of about ten observation wells, for low and high groundwater levels, chosen from existing and accessible points downstream of the former dumps.

Step 3: analysis of water samples by semi-quantitativ « screening ». The analysis of organic compounds, focused on volatile compounds, by the analysis method of « purge and trap- GC/MS » (not detected by screening).

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BRGM-D3E

> 11

Step 3 : Analytical results- In 2005, 40 % of compounds had

been identified,

60 % are non identified (with a proposition of corresponding chemical group)

- In 2007, 80 % of compounds had been identified

Many compounds could be in relation to pharmaceutical industry

BUT: 18 compounds > 1µg/L are non identified

FAMILLE Grands Groupes

Phar

ma Chimie non pharma

(plastique, solvants, agroalim, textiles…)

Hyd

roca

rbur

e et

grad

atio

n

Pest

icid

es

AlcaneAlceneAlcynes

Butyle

Pesticide chloré /

thiophosphate Pestic. Ou dégradéAlcool x x x

Cetone x x xEster x x x

Phtalates xx

xAmines

aromatiques x

Amides xBenzoyles

Nitrile x?x

thiophosphate

Medicaments

AmidesSucre

ThioesterEpoxyde x

Amines

contenu dans le temoin d'essai

Pharmaceutique x

Organophosphatesx

(contient du soufre)x

x

Am

ines

x

x

Alc

ool,

Cet

ones

,

x x

x

x x

Hyd

roca

rbur

es

x

Tria

zine

s

x

Phosphore?

Thiol

Phenol polyaromatique

Composé halogénés non aromatiques

Triazines

tert.-Butyle cyclohexanol

KWS/Alcynes

Aromatiques

Vendredi 18 mai 2013

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BRGM-D3E

> 12

Results : Downstream of several dumps, traces of compounds from chemical and pharmaceutic industry, with concentrations > 1 µg/L. BUT: Many of these compounds without any toxicity reference values.

Année Konz. Komponenten_Name No BSS substances sans certitude Groupe

2007 27.21 inconnu 04465x0115??? aromatische chlorierte Verbindung mit

Schwefel Aromatique2006 25.000 inconnu 04465x0115 Propanoic acid, 2-propenylester Hydrocarbures dégradé2006 21.800 inconnu 04465x0115 Pyrazine, 6-chloro-3-(2,4-dichlorophenocyl) Hydrocarbures dégradé2006 8.730 inconnu 04465x0115 Propanoic acid, 2-propenylester Hydrocarbures dégradé2007 6.72 inconnu 04465x0115 Isomeres zu 51.95???

2007 6.66

Dichlorophenoxyderivat (Abfallprodukt bei der Herstellung eines

Phenoxyessigsäureherbizids?) 04465x0115 Amines aromatiques?2006 5.370 inconnu 04465x0115 Pentanoic acid, 3-oxo, methyl ester Hydrocarbures dégradé2006 5.170 Crotetamid 04465x0115 traceur chimie pharmaceutique2006 5.070 Tributylphosphat 04458x0124 Organophosphates2006 4.810 inconnu 04465x0115 11 Ethyl-9-methyl-azatric… Amines 2007 3.99 Benzotriazol 04458x0124 Triazine2007 3.98 inconnu 04465x0115 ??? inconnu

2007 3.94 inconnu 04465x0115??? Strukturell ähnlich zu 46.72 - enthält

Chlor contient Chlore2006 3.730 inconnu 04465x0115 Benzene, Ethylpentamethyl-…. Aromatique2007 3.29 inconnu 04465x0115 Phenol, 2-methoxysulfonyl? Amine aromatique2006 3.000 Triphenylphosphin-Derivat 04465x0089 Phosphore?2007 2.5 Methyliertes Benzotriazol 04458x0124 Triazine

2007 2.03

Dichlorophenoxyderivat (Abfallprodukt bei der Herstellung eines

Phenoxyessigsäureherbizids?) 04465x0115 Amines aromatiques?2007 1.96 inconnu 04465x0115 ??? inconnu2007 1.81 Chloriertes Keton oder Ester 04465x0205 Cétone, Ester2007 1.8 inconnu 04465x0115 Isomeres von 41.87 - Chinolinderivat? ?

2007 1.71 Chloro-amino-benzensulfonalkylderivat

04465x0115 Amine2007 1.58 inconnu 04465x0115 ??? inconnu2007 1.54 p-Toluensulfonamide 04458x0124 Amide

2007 1.51 inconnu 04465x0115 ??? aromatische chlorierte Verbindung mit Schwefel- entspricht 46.24 mit Methylgruppe Aromatique

2007 1.48 inconnu 04458x0087 ??? inconnu

2007 1.46

Barbiturat (Der wahre Gehalt kann 5 bis 10 mal höher sein - nicht alle Barbiturate

sind mittels GC/MS nachweisbar) 04465x0205 Barbiturique2007 1.37 inconnu 04465x0115 ??? inconnu2007 1.19 inconnu 04465x0115 ??? inconnu2007 1.14 Propylester unspezifisch 04465x0115 Ester2007 1.14 inconnu 04465x0205 ??? inconnu

2007 1.12 Chloro-amino-benzensulfonamidderivat

04465x0115 Amide

Various sources : actual industrial activities, former dumps, agriculture - identified with degradation of hydrocarbons, pesticides and pharmaceutical products

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BRGM-D3E

> 13

Cross-frontier relationships – pressure on IGDRB

IGDRB represents the chemical and pharmaceutical industry of Basel (Switzerland)*

L’ADEMEPublic service under the supervision of the ministeries of environment and education, intervene also in financing of studies and rehabilitation of former dumps

The DREAL represents the state and controles the classified industry in environmental questions (BUT only in France)

Organisms like Greenpeace, environmental associations (NGO)

Localpresse

The mayors of the towns of the Dreieckland (Switzerland and France)

Prefect Represents the state in the région

Vendredi 18 mai 2013

*IGDRB has been created to assess and to remediate to the hazardous wastes in the Dreieckland.

Two dump has been remediated in 2011

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Remediation and management of mesuresToday, the dumps of the area of concern in the north of the Dreieckland is not treated… because:

- The concentrations are generally very low (traces), even after high groundwater levels ;- The downstream impact seems to be limited, because the wells further downstream don’t show comparable concentrations;- The most important concentrations found are in the actual industrial area (mixture of sources).

> 14

BUT: actual lack of de toxicity/ drinking water standards for many substancesTest of the RANKING methode (source : University of Strasbourg, IFARE (2007): impossible because of very low concentrations AND the need of a very high pumping rate to reach GW under the dumps (Rhine Alluvions are very pervious and importante thickness of Gwbody

Vendredi 18 mai 2013

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BRGM-D3E

> 15

Cross-border relationships between Préfect-IGDRB and remediation- IGDRB financed the risk assessment in 2001 - 2008 (ANTEA, Daniel

Hube) especially for two dumps, today entirely cleaned up: the polluted soil with about 50.000 tons of waste and toxic substances, treated in specialized centers. The oldest of these wastes stayed since the 50ies in these dumps.

- Not responsible by law, le IGDRB accepted though to take in a volonteer way the necessary steps to pay more than 26 M€ to clean up these former dumps and to reaforest the area with native plants.

- The monitoring of the groundwater will be maintained until 2015.

Vendredi 18 mai 2013

Pressure by Greenpeace Suisse in 2005 ….

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> 16Vendredi 18 mai 2013

Global approach,

• concerns public (health, environment, water ressources policies) and private(industries, regional and local development,…) stakeholders,

• promotes a better understanding of the role and mission of stakeholders in the common interest,

• defines viable and realistic remediation goals taking into account the global contamination background (concentrations and fluxes),

• contributes to enhanced knowledges and survey on global contamination (soil, groundwater, ambient air) and exposure,

• complementery to site-specific approach by defining 1) the backgrounds levels , 2) the stakeholder involved, 3) the action priorities in remediation and/or assessment on former contaminated sites onto the area in concern 4) contribute to the management of groundwater ressource in urban area with dense industrials networks.

(Original) Global approach / (traditional) site specific approach

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> 17Vendredi 18 mai 2013

Screening is a analytical tool efficient for global approaches

Completed the identification of compounds in concern for risk assessement and remediation option appraisal when lacks on historical information occur (reduction of uncertainties). This approach is helpfull for risk assessment when exposure calculation based on targeted pollutant conduct to uncertainties,

A better understanding of the behavior and the possible degradation of organic compounds by the identification of metabolites,

Benefit of screening in the location of pollutions sources and responsabilities: fingerprinting of the typical chemical composition of the sources,

Controlling the completeness and the sufficiency of applied standard operating procedures and analytical chains (Quality assurance / Quality control).

500 – 700 € HT per sample (specialized Universities, Laboratory …)

Page 18: Integrated approach on global groundwater contamination of ... · Integrated approach on global groundwater contamination of the area of the Dreieckland (F, CH, D) in an urban multisite

> 18Jeudi 11 avril 2013

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