presentatie detectie puur product linksa asse belgium
DESCRIPTION
The subject site is located in Asse, Belgium and was used for fabrication and storage of glues and tar containing asphalt products. Due to a fire, a distillation unit of 30 tonnes and a filled storage tank of app. 40 m³ taroil were destroyed.The Public Waste Agency of Flanders (OVAM) is responsible for the clean-up of the site. An excavation of the superficial DNAPL contamination has already been executed. However, the DNAPL of tar products on the clay-layer at a depth of 14 to 15 m bls still needs corrective action. Commissioned by OVAM, a pilot for in-situ chemical oxidation (ISCO) with Fenton’s Reagens has been executed on the site. A reasonable reduction of the contaminant load (app. 90%) was obtained.In order to make a well-founded BATNEEC-evaluation, the DNAPL is further characterized in detail, as the exact volume/proportion and contaminant load will determine the final remediation costs. This characterisation is obtained by using the Rapid Optical Screening Tool (ROST™) of Fugro. ROST™ detects aromatic hydrocarbons by means of a Laser Induced Fluorescence (LIF) technique.TRANSCRIPT
Localisation and remediation of a DNAPL-contamination of PAH’s at
the former Asphaltco site
Karel Van Nieuwenhove, Koen Meskens (Soresma nv),
Frank Pels (HMVT),Koen Janssens (OVAM)
Summary of presentation
» Introduction› Site description
› Characterization of the contamination
› Site Development Plans
› Already executed remediation
› Remediation of the second DNAPL
» Further characterization of the contamination: detection by ROST› Principle
› Results:
› Hydro geological build-up of the underground
› Semi-quantitative determination of the contamination
» Site remediation: Pilot test› Materials and methods
› Results
› Conclusions
» Future perspectives
Site description
» Location: Belgium, Asse, Molenstraat 48-50
» History:
› < 1900: horticulture
› 1912-1920: production of glues
› 1920-1986: fabrication of glues and tar containing asphalt products (Asphaltco)
› 1985-1997: several companies and illegal dumps
› 2005: demolition of the site
» Calamity: fire
› 1942
› Destruction of distillation unit of 30 tonnes and filled storage tank of app. 40m³ tar oil
› Extinguished with foam containing tetrachloromethane
INTRODUCTION
maaiveld
kleilid van Asse
12 -14 m
7 m
14 m
pilot
Characterization of the contamination
» Contamination in soil and groundwater
› PAH
› Mineral oil
› Benzene
› Phenols and cresols
» DNAPL’s of tar
› 7.0 m bgl (Lid Van Onderdijke)
› 14.0 m bgl (Klei van Asse)
INTRODUCTION
Site Development Plans
» Acquired by the local community
» Fire department, youth house, sport tracks,...
» Local depot for busses (De Lijn)
» Large parking lot for the train station
» OVAM will remediate the site
Introduction
Already executed remediation
» Demolition of the site (2005)
› Cost: 500.000 euro
» Remediation of the dumping ground (2006)
› Cost: 950.000 euro
» Excavation contamination until 5.0-6.0 m bgl (2007)
› Total cost excavation (removal and remediation of contaminated soil): 8.150.000 euro
Introduction
Remediation of the second DNAPL
Remedial Action Plan originally said:
» Combination of steam injection and ElectricalResistance Heating
» Followed by In-situ Chemical Oxidation
OVAM chose to directly perform a pilot study for ISCO
Introduction
Further characterization of the contamination
» Determination optimal location pilot test
» More detailed delineation of the DNAPL zone
By
» Camera probing
» ROST probing
Camera probing
» The camera probe is inserted in the underground by means of regularprobing equipment.
» Simultaneously video-recordings are made from the underground.
» The camera probe consists of:• Stainless steel tubing (Ø 44 mm, ca 1 m)
• Saphire sight flow glass: 5 by 7 mm
• Behind which a lamp, a mirror and a camera are placed.
• Viewed 100 times enlarged on the monitor
» Grain size and colour of the soil, oilparticles, gasbubbles but alsocontamination like tar are visible
Further characterization of contamination
tar
Cameraprobing – examples
Further characterization of contamination
ROST probing
» Principle: ROST = Rapid Optical Screening Tool
Further characterization of contamination
Principle (2)
Further characterization of contamination
Results:
» Semi-quantitative determination of the contamination
DNAPL
Further characterization of contamination
Results:
» Geological cross sections
Dwarsdoorsnede AA'
0,00
2,00
4,00
6,00
8,00
10,00
12,00
14,00
16,00
18,00
Puntweerstand
diep
te (m
-mvS
4)
PW S3
PW S100
PW S102
PW S103
PW S104
S100 S3 S102 S103 S104
vermoedelijke verspreiding (niet afgeperkt)
puur product in de klei van Asse
Zand van Buisputten
Klei van Zomergem
Zand van Onderdaele
Klei van Asse
zandige tussenlaag
minder doorlatende laag
Dwarsdoorsnede BB'
0,00
2,00
4,00
6,00
8,00
10,00
12,00
14,00
16,00
18,00
Puntweerstand
diep
te (m
-m
vS4)
PW S3
PW S6
PW S9
PW S11
PW S100
VUB1A
Zand van Buisputten
Klei van Zomergem
zandige tussenlaag
Zand van Onderdaele
Klei van Asse
minder doorlatende laag
minder doorlatende laag
S100 S3 S6 S9 S11 VUB1A
Further characterization of contamination
Contamination cross section
Further characterization of contamination
Pilot test : ISCO remediation
» Materials and methods:
› HMVT bvba. – Soresma nv.
› 2 stages (May and July 2007)
› Area: 10 x 15 m² - 12 injection points (screen depths of 13.0-14.0 m-gl.)
› Injection of Fentons reagens (conc. of 5 to 10 %)+ catalyst (Fe2+-sulphate)
› Vapor extraction wells (14)
Site remediation
ISCO in action
Site remediation
Pilot test : ISCO remediation
» First results: Reduction of the contamination load with 80-95%
M1
M2
M3
M4
M5
M6
M7
INJ
1
INJ
6
INJ
9
INJ
12
2-8-2007
0
5000
10000
15000
20000
25000
30000
punt e n
ug/ l
minerale olie
2-8-200723-5-200723-4-2007
Site remediation
M1
M2
M3
M4
M5
M6
M7
INJ
1
INJ
6
INJ
9
INJ
12
2-8-2007
0
5000
10000
15000
20000
25000
punt e n
ug/ l
PAK 16
2-8-200723-5-200723-4-2007
Reduction MO first step: 73%Reduction MO second step: 83%
Reduction PAH first step: 82%Reduction PAH second step: 94%
Pilot test : ISCO remediation
» Conclusions :
› At first: reasonable reduction was obtained
› After 1 year: DNAPL contamination was restored
› DNAPL levelled out from upper layers (non-treated)
Site remediation
Before start After 4 months After 1 year
Future perspectives
» Prior to ISCO a selective removal of the mobile DNAPL will be performed by specially designed pure product pumps => pilot test
» Final characterization of DNAPL by ROST probing
» Determination of risk based remediation values