IEG Multi-Functional Well™ System
Patented design - proven engineering
Quicker, Smaller, Smarter, Greener
The IEG Multi-Functional Well™ (IEG MFW™)
has been implemented for the remediation of subsurface contamination caused by
hydrocarbon spills. Four different remediation processes can be operated within
the same well. At optimal efficiency of each remediation process,
successive treatment of the capillary fringes, the vadose zone, and the aquifer
can be accomplished. Each treatment process requires only simple modifications
of the well configuration. Removal of the contaminants is done primarily through
in situ air stripping. The oxygen supplied through the stripping process and
additional air injection wells further enhances biodegradation of the
contaminants.
The IEG MFW™ is an in situ system for the remediation of
hydrocarbon contamination in the unsaturated and saturated zones (Figures 1 - 4)
using a combination of chemical, physical and biological processes. The system
consists of a specially configured inner well (e.g. diameter = 400 mm) with
screened sections which are separated by unscreened casings and packers.
Additionally, pumps, a stripping reactor under vacuum, and a free product
recovery system, operated under vacuum, are required. An outer well casing which
forms the treatment chamber (e.g. diameter = 1,000 mm) is arranged coaxially
around the inner well and extends from the ground surface down to a depth of
approximately 1.0 m. A blower, an off-gas treatment system (e.g. activated
carbon filters), a contaminant storage tank, and a vacuum pump are located above
ground. Several air injection wells are arranged within the sphere of influence
of the IEG MFW™.
The well screens are located within the unsaturated zone, near the
groundwater table or the capillary fringe, and at the bottom of the contaminated
aquifer. Contaminated soil vapour can be removed from both upper screen
sections, or from each section separately. Reinjection of the air after its
decontamination above ground is also possible, thereby creating a vertical air
circulation flow. Alternatively, treated soil vapour can be reinjected through
additional air injection wells, thereby creating a horizontally directed air
flow. Contaminated groundwater is pumped from one section, and after treatment
in the stripping reactor, located in the well head, reinjected into one of the
upper screens, thereby inducing a vertical groundwater flow.
The circulating flow creates a vertical pressure gradient and forces a
vertical movement of the groundwater instead of a simple horizontal flow through
highly permeable layers. The flow direction can be reversed depending on the
vertical distribution of the contaminants.
Possible Modes of Operation
1. Free Product Recovery (FPR)
Free product floating on the groundwater is removed by applying a vacuum
without having to pump groundwater. Free product moves in the direction of
the negative pressure gradient (5 - 8 kPa) towards the well in which it
accumulates (Figure 1).
In order to control the applied vacuum and thus the amount of oil flowing, an
adjustable inner tube is arranged inside the well in such a way that the middle
screening section is nearly covered by groundwater and the free product floating
on top. Because the free product is flowing towards the well continuously, no
high air velocities are required for its transport.
A vacuum pump produces a vacuum inside a receiver tank and the attached
piping which is connected to a double-cased screen containing hydrophobic
material. The free product is thus transported to the surface. Because no cone
of depression is created a downward movement of free product is prevented.
2. Soil Vapour Extraction/Bioventing
In this treatment step the volatile hydrocarbons can be removed from the
unsaturated zone by soil vapour extraction. Additional air injection wells
arranged in the zone of influence are operated to provide a continuous supply of
oxygen enriched air to the subsurface to create the effect of
"Bioventing".
At the beginning, soil vapour is extracted from both upper screening sections
(Figure 2). Using an adjustable inner tube, the length of the screen can be
varied to regulate the airflow depending on the vertical contaminant
distribution in the unsaturated zone. Oxygen enriched air flows from the
injection wells through the contaminated unsaturated zone in the direction of
the negative pressure gradient towards the Multi-Functional Well™.

When the concentration of the volatile hydrocarbons in the off-gas has
levelled off, the remediation progress can be improved by inducing a vertical
soil circulation flow. In this case, the uppermost screen is completely closed
off by the adjustable inner tube. Now soil vapour can be extracted from the
lower screen section and can be re-infiltrated into the outer casing.
Due to the heat from the blower the re-infiltrated off-gas aids in the
desorption of the contaminants from the soil matrix.The distance of the air
injection wells from the MFW™ depends on the soil characteristics and the
lateral contaminant distribution.
3. Soil Circular Flushing Well (SZB)
The saturation of the soil above the groundwater table is increased by a
vertical flow of flushing water. The hydrocarbons remaining in the soil are
either removed by in situ stripping in the well, adsorbed to an optional
activated carbon bed above ground, or biodegraded in the well and the
unsaturated zone. The water flushing the contaminated soil removes the
contaminants and enters the well through the middle screen section (Figure
3). A first pump controls the water quantity circulating through the
unsaturated zone.
The flow rate of an optional second pump located just below the stripping
reactor is higher than that of the first pump (e.g. the pumping rate of the
second pump can be five times that of the first pump). This pump regulates
the circulation within the well casing and makes sure that a sufficient
stripping rate can be achieved.

The water leaving the well through the outer casing is enriched with
dissolved oxygen and small air bubbles (100 microns and less) which enhances the
growth of the micro-organisms in the area of soil flushing. Biodegradation can
be further enhanced by adding nutrients and/or surfactants. The dissolved oxygen
concentration in the water decreases with distance from the Multi-Functional
Well™. It is at a minimum when it re-enters the well. Air injection wells
surrounding the MFW™ allow to maintain aerobic conditions also at the periphery
of the circulation cell.
After flowing radially out through the upper screen of the inner well, water
accumulates up to a controlled level in the outer well (Figure 3). A water level
sensor located in the outer well regulates the operation of the first
pump.
The outer casing contains a gravel layer placed on top of the natural soil
for better drainage. This filter can easily be exchanged should it clog due to
chemical precipitation or excessive biomass growth. In the outer casing the
negative pressure due to the vacuum and the hydrostatic head from the water
column are in an approximate equilibrium.
Nevertheless water discharges from the negative pressure well due to a
continuous supply in a downward direction. Because there is a simultaneous two
phase flow of air and water, both phases interact with each other in such a way
that a slow but continuous flow develops. The water saturation in the soil
controls the flow rate. At a designed water saturation of approx. 40 - 60% the
percolation rate of the flushing water is more reduced than that of the air.
As an option a horizontal drainage system can be placed radially just below
the ground between the Multi-Functional Well™ and the air injection wells.
Clean water draining into the subsurface is thus cohesive interconnected with
the well. This provides a more uniform remediation progress within that drainage
area.
4. Vacuum Vaporiser Well (VVW)
The IEG UVB™ technology is a
well known method for groundwater remediation. To operate in the
UVB™ mode the stripping reactor and both pumps simply have to
be arranged lower in the well. Similar to the SZB™ mode
the remediation progress depends both on in-situ stripping and
biodegradation.
Contaminants dissolved in the groundwater are continuously transported to the
well head where they are stripped under vacuum. Treated oxygen enriched
groundwater and air bubbles leave the well, are re-injected into the groundwater
and thus enhance biodegradation in the aquifer (Figure 4). A significantly
higher pumping rate can be achieved than with the SZB™.
The IEG MFW™ method is a process patented by
IEG.