Defoding on demand a new strategy for potable wafer production New approaches
to the application
water are constantly impact of fouling researchers
for the production
application
on the economic
viability of membrane
enzymes for defouling
of dynamic
immobilised
layer fdtration
on demand.
processes.
University
Now,
of
immobilised
immobilised
“activatable”
“activatable”
refers during
activated. factor
explains.
or
the drive towards of
enzymes
membranes due
to
has the
conditions
for
greener the
found
cechnoiogy,
cleaning
of
widespread
efficiency
and
application
mild
of these bioiogic‘al catalysts.
the cost of enzymes
the
fouled
that the fouling
layer is degraded
of attachment,
obviating
on demand.
whole
layer. The disadvantage
foulanr
However,
means such processes
to this problem
onto the active filtration
membrane,
so they
periods.
The added
be used
advantage
depicted
of using
in Fig.
term
are
not
operation
of the
are dormant
until
occurs when a chemical 1s Introduced For example
to
when
the ultrafiltration baxd
on
as follows
and
cothe
fouling process.
this
technology
is schematically
1
lmmobilisation of the inactive enzyme
‘the fouling
layer is degradedfiom the point of attachment”
are not
these
layer of the
IMMOBILISED
INACTIVE
IMMOBILISED
LAYER
the
retained
: PROCESS
ENZYMES
2. FOULANT
immobilised
degrade
for extended
of such a system is
I. ENZYMES
very
enzymes
is that
macromolecules
that
The enzyme
may are
by filtration.
3. INDUCER
ADDED
: ENZYMES
CATALYSE
is a manganese
by
white
the
1: ‘; -
: FLUX
MEMBRANE
DECLINES
ACTWE
CHEMICAL
LAYER
ACTIVATOR
DEGRADATION
OF FOULANT
LA YER : FLLX
DEVELOPS
SOLUTION
ENZYME
4. ENZYMES
chosen for application
treatment
BEGINS
-
DEVELOPS
they
I FOULANT
ADDED
ACTIVATED
RESTORED
DISRUPTION
OF FOULANT
LAYER
Membrane Technology No. 102
process
proceed
The
that
is to immobilise
the enzymes
can
would
the
use of
operating
yet cost effective. A solution
affxting
water
rhe
enzymes. enzymes
They
to the
cleaning
during involves
the normal
process.
A typical
from the point
the need to digest
to
co-substrate
is adversely
use
system
Activation
at Rhodes
for
membranes
ultrafiltration
when fouling occurs.
enzymes
This
functional
in the presence of
scientists
a new approach
purification.
enzyme With
this problem,
have developed
ultrafiltration
to this problem
with the use of
only functioning
that can be added to the feed solution
Leukes of Rhodes
use
process for river water clarification.
the enzymes remain dormant,
a co-substrate
To combat University
This process involves the
in conjunction
enzymes in an ultrafiltration
Interestingly,
of potable
This is especially true with regard to the
in South Africa may have come up with a solution
using “activatable”
Winston
of membranes
being sought.
rot
to river water
peroxidase filamentous
produced fungus,
/%itnerochn~t~chrysosporirrnr. I-his enzyme chosen
because
polyphenolic
tannins
to the fouling
in ultrafiltration
requires
Without
rhese
research
carried
found
this
for
out
African
enzyme
can
immobilisation
he
However,
could
and
activity.
is inactive.
in steady
batch
ultrafiltration
after
enzyme
So far,
and significant
major
component
river warer ultrafiltration.
acids,
of
African
context.
colour in upland
The water purification
the Southern
UF membrane
substances
originate
vegetation
such
problem
or cross-flow retains
make
microbes humic
filtration
substances
aromatic
forms
over the layer of immobilised
enzymes,
aiding
the filtration
and
macromolecules A cake layer
entrapment the
increases
by adsorption
molecules.
resistance
to
decline,
process
of smaller
hydraulic
(mostly
an
of
extent
resulting
where
cake
layer
it causes
in unacceptably
flux
Activation of the defouling enzymes (Defouling on demand) a state
of low be
trans-membrane activated
enzymes
can
demand)
by addition
containing
the
achieved
by addition
as
amount
Only
of this
restoration
was shown
to the catalytic ‘The
solution
flux
transformation
occurs
of the tannins
and
returns
and
of other
and
the
for
foulanr
rhe
has several ccrrain
act on the upstream
layer is obviated. efficiency
Also, enzymes
chemical
cleaning
washing
is required
methods,
filtration
and chemical
system
could
required
occasionally
cell. Flat sheet membranes
minimisation
of backflushing
the product
wafer is needed
0
with a
were used. that
the defouling
and that an approximately
to
layer.
action
permeate
is
20 %
adsorbent quality
1~0 systems,
rhereby
chemical
improving
rhe process.
cleaning that
for
srill be
productivity relevance
rcquiremcnts
the rhar of
arc much
applicarions
include
of
this
portable/compact of
potable
communities.
Ar
purification
water
number
South
Africa.
This
benefit
here because
energy
[requirement,
rhc rural
municipal
wareI available
ofsuch communities rechnology
would
of irs good arc
requiring
(no
~scrl)
a low
in
be
efficiency,
safeery
chemicals
operarion,
for small.
are not currently
to a significant
cleaning
to
present,
faciliries
rechnology
units
aggrcssivc
and
lcvrl
ot low
c.tse
of
of technical
proficiency. In addition,
wirh
rhe drive
rechnologies,
rhis “dcfouling
on demand”
suitable
dn
for
rowardb strategy
inct-easing
In hct,
in rhe tood industl-y.
be applied
to any form of filtration
on
rhe
fouling -
the
by
future on
die
of
fouling
01‘
applicarion arc
would
activatable
major
be
I[ c:,n
complexes
applicarions
provision
a
depend enzymes
componen’
in the system. major
limitations
through
to dlc .~pplication
are the cost
used. However,
production
already
organic
that
might
numbcl
apphcatlons where
greener
it ih anticipated
and
and
concurrent stabilisation
immobilisarion
in place to address
arability
of
of the.
programs
on
of rhc Mnl’ techniques
arc
this p~mblcm.
For Further information contact: Winston Leukes, Department of Biochemistry & Microbiology, Rhodes
for this procedure,
the inherent
to match
The
means that less of
This is of particular
Alrhough
is nor expected
the energy
Anticipated
enzyme
extended
in some applicarions.
prop&es.
Conclusion
enzyme
back-
it will
rhc hrlmic
l0wc.r using this approach.
The
Although
without
laycl
acids have
very good
problem
sufficient
less frequent
cleaning.
operate
ultrafiltration
the
from
quite easily. dynamic
by enzyme
and aa mentioned,
this technology
results
and toxic heavy mcrals
action.
Efficient
operation
of
small unwanted
since the cake layer is easily detached
occurring
ultrafiltration
showed
where
al-c
rctcnrion
this procesh
Clean, effective operation
and
Results
solution
as opposed
ro remove the foulant
it is anticipated
instantaneous
have a
Ease of operation fouling,
However.
wafer
wirh
on their
One only has m add a slug of acrivaror
and
can be encouraged
production
flushing
NMWCO
side of
rhe whole
and act rapidly
periods,
30,000
ic are
substrate.
rhis in
making ‘I‘hcsc
layer, the need to digest
backflushing proven
by
criteria.
batch
was
solure rejecrion strengths
of raw river water feed with batch stirred in a laboratory
concept
rhis than
applications.
removal
like pesticides
formation
effective
Pilot results ultrafiltration
.l‘hus, quality
enzyme
process can begin again.
This
impurities
rourincly
of brown
can find their way in Co rhe permeate
provision
Co the system to alleviate
at its
l&red off. Once
state
system
membranes
be RO
alone.
high catalytic
action,
the
through
can
pressure
due
(and certain
is exhausted,
to irs inactive
of flux
because
layer to be removed
metals
sorbents.
the foulant
the foulant
to
also make
warer of a higher
in
enzyme
srrongly
properties
Because the enzymes
allowing
solution
river
be
by
of attachment
m pollute
can
polymers)
poinr
and
Speed of action
organic
activator
the
as pcsticidcs
solution
(on
of the enzyme.
restoration
layer
bind
additional
cleaning membranes
IJnhkc several other IJF proceshcs,
of metal ions. ‘l‘his could
based on rhe following
to be instantaneous
efficiency
substances
the
(micromolar)
is required
or
produces
This
from the outside
a minuscule
In
unwanted
attractive
of a slug of this solution
the feed or by back flushing rhe membrane.
This
Capt.
other
rhe membrane
required
co-substrare.
and viruses.
a
such
heavy
uhrafiltrarion
microbes
the use of high
aggressive
Co damage
to rhe clarification
constitutes
in rhar ir could bind (:a’*. On the
without
costs.
rhereforc
Benefits of the dynamic layer filtration ar colour
be deleterious hand,
chemical would
their pl-opertics.
efficient
dynamic
found
and change
with soil and
humic
overall
since
making
~nvironmenraily
life expectancy
are known
applied
they
ion exchange
what can be achieved
flux,
of the activator
since
reducing
extended
Ar present,
humic
is in rhe range
for
rypically
water. Their
process
At
candidates
water
These
This
as Pr. The
aids
systems
productivity.
is
Colour
for potable
and Western
compounds
retained
low process
surface waters.
from conract
them strong adsorbents
Eventually
the
ro
as Fynbos.
mg/ml
phycoroxins,
and
in
Cape water colour
ideal
of humic
large
substances).
present
in the Southern
of 1000
in the South
consumption.
more
humic
give rise Co a yellow
requirement
for human
layer
cleaning
of- rhesc chemicals
into the envirc,nment, safer,
and
be
chemical
large quantities
process
als
ot water- arc to bc
frequent
The membrane
are
cake
substances
waters
quality
the
interest
Humic
soil and surface
Operation of the UF process can be operated
of
is of considerable
brown
The
improvemenrs
the
friendly
however,
during
supply
filtration.
is,
‘l’hc
by
by dead-end
thar
chemicals
a primary
either
in
immediately
This
formed
immobilised
here.
as required
of river water
acrivation.
unoptimised
has
also be used, but are not
process
state flux is atrained
expected.
University other methods
small batches Less
are nor released improvement
used
peroxide
at Rhodes
adsorption.
disclosed
means
significant
its catalytic
the enzyme
clarified.
which
of membranes
hydrogen
as co-factors
compararively
‘2efouZing action is instantaneous”
of this water.
‘This enzyme
physical
are
was
degrade
of some South
?‘hese
contriburors
or
such as tannins,
componenr
waters.
Mn(Il)
rransform
complexes,
are a major river
ir can
of when
University, Grahamstown 6140, South Africa. Tel: +27 461 318 262 441;Fax: +27 461 24377.
Membrane Technology No. 102