Refining NAPL distribution and occurrence using FLUTe™ liners

Refining NAPL distribution
using FLUTeTM liners
Tamie R Weaver, ERM, Melbourne
Mike Mercuri, Matrix Drilling, Melbourne
Steve McKeown, ERM, Cape Town
Joe Fiacco, ERM, Boston
Lance Robert, ERM, Barcelona
Abstract E111
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Dr Weaver is a technical director in hydrogeology at ERM in Melbourne. She has many years’ experience as a university lecturer and consultant hydrogeologist assessing the fate and transport of contaminants in groundwater from contaminated sites, waste facilities and in the natural environment. Presenting on behalf of colleagues within and outside of ERM in
Australia and overseas.
Mike Mercuri – Matrix Drilling
Steve McKeown – ERM Cape Town
Joe Fiacco – ERM Boston
Lance Robert – ERM Barcelona
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Assess Risks and Inform Remediation
■ Extent and distribution of contamination
■ Non aqueous phase liquids (Light vs Dense, mobile vs residual)
■ Type and extent of dissolved phase contamination
■ Contaminant storage vs contaminant transport
■ Preferential pathways for contaminant migration vs storage in the rock matrix
■ Maturity of the plume
■ Is the plume expanding, stable, or declining
■ Is NAPL still present
■ Transfer of contaminants to vapour / surface water (exposure pathways
and risks)
■ Address regulatory requirements (e.g. remaining NAPL in aquifers)
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CSM and Remediation
Where is contaminant
stored / transported?
Areas and methods
for remediation?
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Investigations in Fractured Rock
■ Increased uncertainty / complexity regarding contaminant
distribution
■ Exacerbated if LNAPL or DNAPL are present
■ Difficult to predict behaviour away from investigated area
■ Small features can be important
Uncertainties drive
■ “More targetted” assessment – technologies such as FLUTe, downhole logging, passive flux meters, short screened / multilevel wells,
targetted aquifer testing, bail-down testing
■ Distribution and occurrence of NAPL, dissolved phase
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FLUTeTM liners – NAPL Distribution
Apply to an open borehole before well construction
■ NAPL FLUTeTM (identify where non-aqueous phase liquid is
present in the borehole)
■ Identify zones, layers, filled fractures
or globules of NAPL
■ Assess NAPL as ongoing secondary
source zone away from primary
source
■ Identify NAPL in unsaturated zone
■ Does not address whether remaining
Hydrocarbon
NAPL is mobile or residual
stainingg
■ Potential to “smear” NAPL during drilling
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Considerations
“Standard” wells
■ Sample extended part of aquifer
■ Where did NAPL (usually LNAPL) enter well from?
■ Does same feature / unit host NAPL at different locations?
LNAPL on water
table in well
NAPL FLUTe Liners
■ FLUTe identifies specific areas where NAPL is present in
borehole
■ May / may not relate to recoverable / mobile NAPL
■ Compare occurrence across different locations.
■ Unsaturated zone assessment
LNAPL in
formation
(unsaturated
zone)
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Petroleum Release Site
Objectives:
■ Contaminant Migration
■ Risk to Aquifers
■ LNAPL Recoverability
Multiple techniques
■
■
■
■
■
■
■
Geological mapping
Surface geophysics
Coring
Downhole geophysics
Packer tests
NAPL FLUTeTM
Monitoring wells
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NAPL FLUTeTM Liner Installation and Staining
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■ NAPL distribution – discrete
zones related to fracturing
and bedding planes
■ Not a “pool”, but contained
within vertically discrete and
laterally defined transmissive
fractured zones
■ Combine with other
assessments to refine CSM
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Outcomes
Refined Conceptual Site Model
■ Identified transmissive fracture zones: 3.5 – 5 mbgl; 14 – 19 mbgl; and
46 mbgl
■ Very limited hydraulic connection between the two shallow sets (5 and 15
mbgl) and deep (46 mbgl) transmissive fracture sets
■ Lateral migration of LNAPL in 2 shallowest bedding-plane fracture zones, not
in deepest fracture set (NAPL FLUTe)
■ Delineate lateral and vertical extent of LNAPL (NAPL FLUTe)
Risks and Risk Mitigation
■ Replaced drinking water supply well – now drilled to deeper part of aquifer
■ Identified areas of potential vapour risk based on LNAPL extent.
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Example: Chlorinated hydrocarbons in groundwater
Site Conditions
■ Fractured siltstone and sandstone
■ TCA concentrations in groundwater to 30-50% solubility of TCA
■ No evidence of DNAPL in wells
Issues
■
■
■
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Is DNAPL actually present?
How extensive, how thick, where in the aquifer?
Where to focus remediation?
Type of remediation to implement?
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Example: DNAPL site
12 m
Residual DNAPL Zone
(approximately 10 m deep)
DNAPL staining on NAPL FLUTe liner
Monitoring well
NAPL FLUTe, no staining
NAPL FLUTe, staining
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Verifying FLUTe liner results
■ Comparison with downhole logging
■ Care re spread of DNAPL in the
borehole during drilling
■ Comparison with dissolved phase
TCA concentrations
■ >10% concentrations, DNAPL
identifiable in the borehole (FLUTe
and borehole imaging)
■ ~1-2% concentrations, DNAPL was
not identified in the actual borehole
■ Targetted remediation depth. DNAPL
absent in shallow aquifer
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Conclusions
Groundwater contamination in fractured rock systems is complex
■ exacerbated with presence of LNAPL and/or DNAPL
Combined tools, including FLUTe, coring +/- downhole logging with
dissolved phase clarify extent and form of NAPL occurrence
■ Move away from the concept of a “pool” of NAPL.
■ NAPL focussed along transmissive zones
■ trapped in pores / dead end fractures
■ Clearer indication of form / extent of NAPL in aquifer
■ More informed decisions regarding risk management
■ More informed decisions about effective remedial approaches
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Thank you
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