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School of something
FACULTY OF OTHER
School of Civil Engineering
FACULTY OF ENGINEERING
Iron-Mediated Toluene Removal in
Subsurface Soils
Rosemary Nmavulem Orlu
Dr Douglas Stewart
Professor Simon Bottrell
cn09ro@leeds.ac.uk
Background
Oxidative
Iron
Bacteria
Reductive
Iron
Bacteria
Fe2+ Fe3+
Oxidation
Reduction
 Iron is ubiquitous in the
environment as the 5th most
abundant metal in the biosphere.
 The recent discovery of
microorganisms that are capable
of conserving energy for growth
from iron reduction has led to a
growing interest in the effect of
iron (iii) reduction in the
bioremediation of aquifer systems
contaminated with metals or
hydrocarbons.
 In many environments, Fe (III)
is the most abundant terminal
electron acceptor (TEA) for the
oxidation of organic matter.
 An interesting feature of Fe-
reducing conditions is the
ability to couple oxidation
and reduction of organic
contaminants.
 The process is referred to as
dissimilatory iron reduction
(DIR).
 DIR involves the transfer of
electrons from
microorganisms to external
Fe (III).
 External Fe (III) is reduced to
Fe (II), acting as an aid to the
assimilation of iron into the
organism.
Five common iron mineral (hydr)oxides
 Most abundant iron
oxide in nature.
 Thermodynamically
stable in
comparison to other
iron minerals.
 Common
weathering product
of siderite and
magnetite.
 Blood red in
colour.
Hematite
(α-Fe2O3)
 Most common
ingredient of iron
rust.
 Second most
abundant iron
oxide after
hematite.
 Thermodynamical
ly stable.
 Yellow in colour.
Goethite
(α-FeOOH)
 Ferro-magnetic
mixed phase
(Fe (II)/Fe(III))
iron mineral
oxide.
 Chief member
of one of the
series of the
spinel group.
 Black in
colour.
Magnetite
(Fe3O4 (FeIIFe2
IIIO4))
 Generally
poorly ordered
crystal structure.
 Commonly
termed
‘amorphous iron
oxide’ or
‘hydrous ferric
oxide’.
 Reddish-brown
in colour.
 Product of the
oxidation of
Fe2+.
 Similar
composition to
goethite but
with a different
crystal
structure.
 Orange in
colour.
Ferrihydrite
(Fe5H)8.4H2O)
Lepidocrocite
(γ-FeOOH)
Experimental hypotheses
Overall aim of this
study:
To assess the influence
of extraneous sources of
Fe3+ on contaminant
attenuation in subsurface
soil environments.
Hypothesis 1:
Indigenous soil
microorganisms in a
previously-
contaminated soil may
be able to respire
anaerobically and
couple the reduction of
Fe (III) to the oxidation
of a hydrocarbon
contaminant (toluene).
Hypothesis 2:
The addition of
extraneous iron
sources as terminal
electron acceptors can
increase the extent /
amount of contaminant
removal as well as the
rate of the reaction.
 The iron minerals used in this study are
commonly-occurring iron (hydr)oxides
with varying degrees of crystallinity.
 Hematite, goethite, magnetite and
lepidocrocite have a more compact
crystal structure in comparison to
ferrihydrite which is known to be an
amorphous iron mineral hydroxide.
 It is well known that amorphous sources
of iron are easily accessible to
microbes/iron reducers for biotic
reductive processes.
Experimental method
 Laboratory preparation of hematite, goethite and
magnetite rock samples:
Cutting with the aid of a rotating saw followed by crushing
in an automated pestle and mortar.
 Synthesis of 2-line ferrihydrite:and lepidocrocite:
-Synthesis of 2-line ferrihydrite: By titrating Fe
(NO3)3.9H2O solutions with 1N NaOH following the method
in (Parkman et al., 1999);
-Synthesis of lepidocrocite: Prepared with fresh, unoxidised
FeCl2.4H2O filtered and adjusted to pH 6.7 with freshly
prepared 1M NaOH solution as in (Yu et al., 2002).
 Mesocosm content: Live soil, iron mineral
amendment, and river water successively spiked
with toluene
 Serial sampling to monitor changes in
toluene, aqueous iron, pH
 Desired soil conditions induced by
successively spiking experimental analogues of
subsurface environments to a point at which
toluene removal occurred at suppressed levels.
 Anaerobic conditions maintained during
sampling with the use of nitrogen-filled ‘ballast
volumes’ attached to the vessels
Live
soil
Mineral
amendment
River
water
.
• Laboratory-
synthesised
2-line
ferrihydrite
.
• Laboratory-
synthesised
lepidocrocite
.
• Freeze-dried
sample

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Orlu R N_2

  • 1. School of something FACULTY OF OTHER School of Civil Engineering FACULTY OF ENGINEERING Iron-Mediated Toluene Removal in Subsurface Soils Rosemary Nmavulem Orlu Dr Douglas Stewart Professor Simon Bottrell cn09ro@leeds.ac.uk
  • 2. Background Oxidative Iron Bacteria Reductive Iron Bacteria Fe2+ Fe3+ Oxidation Reduction  Iron is ubiquitous in the environment as the 5th most abundant metal in the biosphere.  The recent discovery of microorganisms that are capable of conserving energy for growth from iron reduction has led to a growing interest in the effect of iron (iii) reduction in the bioremediation of aquifer systems contaminated with metals or hydrocarbons.  In many environments, Fe (III) is the most abundant terminal electron acceptor (TEA) for the oxidation of organic matter.  An interesting feature of Fe- reducing conditions is the ability to couple oxidation and reduction of organic contaminants.  The process is referred to as dissimilatory iron reduction (DIR).  DIR involves the transfer of electrons from microorganisms to external Fe (III).  External Fe (III) is reduced to Fe (II), acting as an aid to the assimilation of iron into the organism.
  • 3. Five common iron mineral (hydr)oxides  Most abundant iron oxide in nature.  Thermodynamically stable in comparison to other iron minerals.  Common weathering product of siderite and magnetite.  Blood red in colour. Hematite (α-Fe2O3)  Most common ingredient of iron rust.  Second most abundant iron oxide after hematite.  Thermodynamical ly stable.  Yellow in colour. Goethite (α-FeOOH)  Ferro-magnetic mixed phase (Fe (II)/Fe(III)) iron mineral oxide.  Chief member of one of the series of the spinel group.  Black in colour. Magnetite (Fe3O4 (FeIIFe2 IIIO4))  Generally poorly ordered crystal structure.  Commonly termed ‘amorphous iron oxide’ or ‘hydrous ferric oxide’.  Reddish-brown in colour.  Product of the oxidation of Fe2+.  Similar composition to goethite but with a different crystal structure.  Orange in colour. Ferrihydrite (Fe5H)8.4H2O) Lepidocrocite (γ-FeOOH)
  • 4. Experimental hypotheses Overall aim of this study: To assess the influence of extraneous sources of Fe3+ on contaminant attenuation in subsurface soil environments. Hypothesis 1: Indigenous soil microorganisms in a previously- contaminated soil may be able to respire anaerobically and couple the reduction of Fe (III) to the oxidation of a hydrocarbon contaminant (toluene). Hypothesis 2: The addition of extraneous iron sources as terminal electron acceptors can increase the extent / amount of contaminant removal as well as the rate of the reaction.  The iron minerals used in this study are commonly-occurring iron (hydr)oxides with varying degrees of crystallinity.  Hematite, goethite, magnetite and lepidocrocite have a more compact crystal structure in comparison to ferrihydrite which is known to be an amorphous iron mineral hydroxide.  It is well known that amorphous sources of iron are easily accessible to microbes/iron reducers for biotic reductive processes.
  • 5. Experimental method  Laboratory preparation of hematite, goethite and magnetite rock samples: Cutting with the aid of a rotating saw followed by crushing in an automated pestle and mortar.  Synthesis of 2-line ferrihydrite:and lepidocrocite: -Synthesis of 2-line ferrihydrite: By titrating Fe (NO3)3.9H2O solutions with 1N NaOH following the method in (Parkman et al., 1999); -Synthesis of lepidocrocite: Prepared with fresh, unoxidised FeCl2.4H2O filtered and adjusted to pH 6.7 with freshly prepared 1M NaOH solution as in (Yu et al., 2002).  Mesocosm content: Live soil, iron mineral amendment, and river water successively spiked with toluene  Serial sampling to monitor changes in toluene, aqueous iron, pH  Desired soil conditions induced by successively spiking experimental analogues of subsurface environments to a point at which toluene removal occurred at suppressed levels.  Anaerobic conditions maintained during sampling with the use of nitrogen-filled ‘ballast volumes’ attached to the vessels Live soil Mineral amendment River water . • Laboratory- synthesised 2-line ferrihydrite . • Laboratory- synthesised lepidocrocite . • Freeze-dried sample