BIOREMEDIATION
AND
CONTAMINATES
Classification
of Bacteria
Bacteria
are
classified
in several
different
ways,
all
of which
are
based
on different
aspects
of the
metabolic
process.
In terms
of carbon
sources,
bacteria
are
divided
into
autotrophs,
which
use
carbon
dioxide
as their
carbon
source,
and
heterotrophs,
which
derive
carbon
from
organic
compounds.
Additionally,
bacteria
are
grouped
according
to their
source
of external
energy:
phototrophs,
which
derive
energy
from
photosynthesis,
and
chemotrophs,
which
obtain
energy
from
the
oxidation
of chemical
substances.
Based
on these
two
classifications,
there
can
be four
basic
types
of bacteria
based
on their
external
sources
of energy
and
carbon.
Bacteria
that
play
a key
role
in bioremediation
derive
their
carbon
and
energy
from
organic
compounds.
In
the
wastewater
industry,
bacteria
have
traditionally
been
classified
based
on their
oxygen
requirements:
aerobic
bacteria,
which
convert
their
food
source
(organic
compounds)
to energy
by transferring
electrons
from
the
compounds
to oxygen
(electron
acceptor):
anaerobic
bacteria,
which
metabolize
their
food
in the
absence
of oxygen
and
instead
utilize
inorganic
chemicals
such
as nitrates,
sulfates,
carbon
dioxide,
or metals
such
as iron
as substitute
electron
acceptors;
and
facultative
bacteria,
which
can
function
in both
aerobic
and
anaerobic
environments.
Bio-Form LLC
formulas
use
facultative
bacteria
that
are
heterotrophs.
In
a report
published
by the
National
Research
Council
(NRC),
three
metabolic
processes
were
identified
as playing
the
most
significant
roles
in bioremediation:
aerobic,
anaerobic,
and
cometabolism
(National
Research
Council,
1993).
In cometabolism
reactions,
transformation
of a
specific
contaminant
occurs
indirectly,
i.e.,
as the
result
of the
metabolism
of another
substance,
which
otherwise
could
not
be metabolized
by the
bacteria
themselves.
Factors
and
Conditions
Affecting
Bioremediation
In-situ
bioremediation
is highly
dependent
on site
conditions
and
soil
properties,
more
so than
Soil
Vapor
Extraction/Air
Sparging.
Factors
that
play
a significant
role
in the
design
and
successful
operation
of a
bioremediation
system
include
contaminant
characteristics,
natural
supplies
of macronutrients
and
micronutrients,
availability
of electron
acceptors,
and
subsurface
characteristics.
Contaminant
Characteristics
The
biodegradability
of petroleum
products
is dependent
on the
chemical
structure
of its
various
components.
In general,
the
lighter,
more
soluble
petroleum
hydrocarbons
are
more
biodegradable
than
the
heavier,
less
soluble
members
of the
group.
A compound's
resistance
to biodegradation
increases
with
increasing
molecular
weight.
Additionally,
highly
viscous
hydrocarbons
are
less
successfully
biodegraded
because
of the
inherent
physical
difficulty
in establishing
contact
among
the
contaminate
and
the
microorganisms,
nutrients,
and
electron
acceptors.
For
example,
gasoline,
which
is considered
more
easily
biodegradable
than
diesel
fuel,
has
a solubility
of 50
to 100
ppm
and
a viscosity
of 0.5
to 0.6
centistokes
as compared
to a
solubility
of less
than
1 ppm
and
a viscosity
of 2
to 4
centistokes
for
diesel
(Table,
Cole,
1994).
Similarly,
diesel
is more
biodegradable
than
used
oil,
which
has
a solubility
of less
than
1 ppb
and
a viscosity
of 40
to 600
centistokes.
Solubility
and
Viscosity
of Data
of
Representative
Petroleum
Products
|
Product
|
Solubility
in
Cold
Water
(at
20
C
in
ppm)
|
Viscosity
(in
Centistokes)
|
|
Gasoline
|
50-100
|
0.5-0.6
|
|
1-Pentene
|
150
|
n/a
|
|
Benzene
|
1,791
|
0.5
|
|
toluene
|
515
|
0.5
|
|
Ethylbenzene
|
775
|
0.6
|
|
Xylenes
|
150
|
0.6
|
|
n-Hexene
|
12
|
0.4
|
|
Cyclohexane
|
210
|
n/a
|
|
i-Octane
|
0.008
|
n/a
|
|
JP-4
Jet
Fuel
|
<
1
|
0.8-1.2
|
|
Kerosene
|
<
1
|
1.5-2
|
|
Diesel
|
<
1
|
2-4
|
|
Light
Fuel
Oil
#1
and
#2
|
<
1
|
1.4-3.6
|
|
Heavy
Fuel
Oil
#4,
#5
&
#6
|
<
1
|
5.8-194
|
|
Lubricating
Oil
|
<
0.001
|
400-600
|
|
Used
Oil
|
<
0.001
|
40-60
|
|
Methanol
|
>
100,000
|
<
0.1
|
|
From
Cole,
M.G.,
Assessment
and
Remediation
of
Petroleum
Contaminated
Sites,
CRC
Press,
Boca
Raton,
FL,
1994,
63.
With
permission.
Simpler
chemical
structures
are
also
easier
to degrade.
Branched
structures
degrade
at a
slower
rate
than
the
corresponding
straight-chain
hydrocarbons.
Alkanes
are
degraded
more
rapidly
than
aromatic
compounds.
Monoaromatic
compounds
such
as BTEX
are
broken
down
faster
than
the
two-ring
compounds
such
as naphthalene.
Some
chemicals
may
be toxic
to the
microbes.
In some
cases,
compounds
that
are
readily
biodegradable
in low
concentrations
may
exhibit
toxicity
characteristics
to the
microorganisms
at high
levels.
Bio-Form LLC's
all
natural
bacteria
and
enzyme
formulas
perform
in the
broadest
possible
physical
and
chemical
treatment
parameters
to achieve
the
fastest
breakdown
of contaminates.
Bio-Form LLC's
formulas
have
proven
in the
field
to not
only
breakdown
the
complete
BTEX
DRO-GRO
ranges
but
a large
number
of toxic
organic
chemicals
in the
unheard
of time
of just
three
to five
weeks
or less.
|