streaming current and streaming potential induced by water flow t.pdf
TRANSCRIPT
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
1/142
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
2/142
ABSTRACT
\
\
Return
To
UTAH
Wi\TER R E ~ : t R C H L ~ B O R i \ T O R Y
U T ~ · ; } :
ST \TE
t;i :lV J1SITY
LOG \H UT?H ~ ~ 1 3 2 2
----------------
Abaza, Mohamed M.
10;
1936; Streaming
Current and Streaming Potential
Induced by
Water Flow Through Porous
Media;
Department
of
Civil
Engineering; Dr. Calvin
G. Clyde, major professor.
This
study was conducted to inves t igate analyt ica l ly and experi-
mentally the re la t ionship between the rate of flow of water through
porous materia l
and the streaming current and streaming potential
in-
duced by
this
flow.
The effect
of dissolved
s l t s
in
the
permeating
solution and the size
of the
so i l
p r t ic les
was also investigated.
Results and conclusions
of
th is
study are
summarized as
follows:
1.
A modified procedure using
the
appropriate delay to
.insure
stead
s t te
conditions
was used for the measurements of both stream-
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
3/142
waters
and NaCl and KCl solut ions provided
that
the conductance
of
the solution was taken
as
a parameter.
5 decrease
in
current and potential was observed with in-
crease of
soi l
par t ic le diameter.
6.
a
Relationships
~ the form o l bN and ~
Clog
N da re
suggested to express the effec ts
of
part ic le s ize and sa l t concen-
t ra t ion on the
streaming
current and the
streaming
potential
induced
by the flow.
7. Induced
streaming potential
was
found to
increase
with
the
decrease in temperature.
8. The analyt ical relationships
developed
together with the
experimental work
could probably be used as the basis of a
method
for
measuring
the rate of
flow
through
porous material .
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
4/142
ACKNOWLEDGMENTS
am indebted to Dr.
Calvin
G. Clyde
major p rofessor
and
thesis di rec to r for his continuous encouragement deep in teres t
valuable advice guidance throughout this work and finally for his
active in teres t
in providing
an environment conducive
to
research by
acquir ing nece s sa
ry
equipment
in shor t t ime.
Special
thanks
are
due
to
Dr.
S.
A.
Taylor
m e m be r
of
the
doctoral
commit tee who introduced m e to i r rever s ible
thermodynamic s
for
his painstaking
review
of
that
part
of
the dis
sertat ion.
am
also grateful
to
Dr. V. E. Hansen Dr. G. Z.
Watters
and
Dr.
D.
V. Sisson for serv ing as memb ers
of
m y
doctoral comm it tee .
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
5/142
TABLE OF CONTENTS
Chapter
I
INTRODUCTION
Objectives
I I
ELECTROKINETIC PHENOMENA
Historical
Recent Theories
and
Modifications
to
He1moho1tz •
Factors Affecting Streaming Potential in
Porous
Media
Utilization
of Streaming Potential for the
Determination of Flow
Parameters
I I I DERIVATION OF THE
ANALYTICAL EQUATIONS
Streaming Current
Streaming Potential •
Limitations
and
Assumptions
•
Page
5
6
6
8
10
14
14
19
21
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
6/142
Table
1
2.
3.
4.
5.
6.
7 •
LIST
OF TABLES
Conversion factors •
Phenomenological
coefficients and electrokinet ic
couplings equation
20
Phenomenological coefficients and electrokinet ic
couplings
equation
21
Calculated , values
for
different concentra-
t ions of
KC
for Sl
and
S2 •
Cell
constant
measurements,
Sample
1
Cell
constant measurements,
Sample
2
Chemical
analysis of
simulated
natural waters
Page
80
81
8
83
8
85
86
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
7/142
LIST OF FIGURES
Figure
1.
2.
4.
5.
6.
The
structure
of the
double
layer
and
the
cor
responding
potent ia ls .
is
a t
the
wall,
is
a t
the beginning
of the
diffuse double
layer ,
a t the hydrodynamic plane of shear
o
In
the
diffuse
double
layer the potential decays by a
factor of
l o v e r a
distance
of 6
= }
for
low
p o t e n t i a l s ~ a f t e r Mysels, 1959
•
Experimental apparatus--general view
A general view
of
the
instrumentation
set
Schematic sketch for
the
apparatus showing the
flow system
.
Block diagram of the electrodes and
associated
electronic instrumentation
Details
of
the
cel l
•
Page
87
88
89
90
91
92
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
8/142
Figure
13. Discharge q
in
cm
3
/sec versus
streaming
potent ia l
E
x
10
3
in volts with NaC permeating through
S2
confined in
ce l l s
f i t ted with
Ag-AgCl
and p1atinized
p l
electrodes
0
14
D
o
h . 3/ °
. SC
arge
1n cm sec versus stream1ng
current
I
x 10
9
in ampers
with 5 x 10-
4
NaCl permeating
through
S2
confined
in
ce l l s
f i t ted
with
Ag-AgC1
and
plat inized p l electrodes
15. Slope of discharge versus
streaming
potent ial
in mill ivol ts
x
sec versus normality of KCl
2
solutions
~ ~ r m e a t i n g through
~
confined in cel ls
f i t ted with
Ag-AgCl
and
platin1zed plo electrodes
16.
Normality
of
permeating
solution
versus the
resistance
for 8
1
and
8
2
17.
The
slope
versus NaCl
normality for 8
1
and S2
18. Slope S versus
NaCl
normality for Sl
and
8
2
19.
The slope versus KCl normality for Sl and 8
2
.
Page
99
100
101
102
103
104
105
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
9/142
Figure
27.
Discharge in cm
3
/ sec
vs. applied
di f feren t ia l
pressure H in
cms
of
water for potassium
chlor ide
so lu t ion with different sa l t concen
t ra t ions
permeating through 8
1
and 8
2
28.
Discharge
q versus
streaming potential E
for
conductance water
permeating through
8
1
and 8
2
29.
Discharge
q
versus streaming potent ia l
E
for
NaGl
permeating through
8
1
a t different
sa l t concentra-
t i o n s • • • • • • •
30. Discharge q versus streaming potent ia l E for NaGl
permeating through
8
2
a t different
sa l t concentra-
t
ions
•
31.
Discharge q
versus streaming potent ia l
E for
KGl
permeating through
8
1
at d i f ferent
sa l t concentra-
t ions
• •
32. Discharge
q versus streaming
potent ia l
E for
KGl
permeating through
8
2
a t
di f ferent sa l t concentra-
t ions •
33.
Discharge
q
versus
streaming
potent ia l
E
for
WI
Page
113
114
115
116
117
118
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
10/142
Figure
Page
40
Discharge q versus
streaming
current
I
for
WI
W
2
and
W
permeating through
8
1
126
41 Discharge q versus
streaming
current I for
W
permeating through
8
2
127
42
art ic le size
dis t r ibut ion
for
both
sand samples
128
43
Cell
constant
for
8
1
and
8
2
•
129
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
11/142
Symbol
A
0
a
mp
C
C
s
C
l
,
C
2
D
d
E .
s
t r
i
s t r
E
Notations
Cross sectional area perpendicular to the
direct ion
of the flow
Average
radius of
pore
Ampers
Cell constant
Specific
conductance
Proportionali ty
constants
Dielectric
constant
Effective sample
diameter
d
lO
Streaming potent ia l
elect r ical potential
difference
across the system
Charge carr ied per
second
per l iquid per unit
surface
length
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
12/142
Symbol
L
11
L
P
L12
L21
L
22
L
e
m
moa.
moVe
N
p
P
s
q
qp
Notations
Represent hydrodynamic
conductance
Represent elec t ro
osmosis
Represent streaming
potential
Represent elect r ic l conductance
Effective area of pores;
superf ic ia l
porosi ty
Mi11iampers
Mill ivolts
Normality of s l t solution
Pressure difference
across the
system
Total perimeter of l iquid sol id interface in a
cross section area
of the
sample
Discharge; volume r te
of flow
Rate
of
flow that would
exist
in absence
of
coupling
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
13/142
Symbol
}
rt
Notations
Kozeny
coeff ic ient
Laplacian
operator
Elect rosta t ic potent ia l
Potential t the surface of the wall
Potential
a t the two layer
interface
Dynamic viscosi ty
Electronic charge
Porosity
Elect r ica l charge density
Zeta potential potential at the hydrodynamic
plane
of
shear
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
14/142
CH PTER
INTRODUCTION
The problem of developing suff ic ient water
suppl ies
for in-
dustry,
agriculture
and
domestic
use
is
rapidly
growing
more
serious
and may well become of basic worldwide
concern
i f the
present
rate
of population growth
and economic
development
is maintained.
In developing ground water
supplies there
is
often
a
need for
deta i led information concerning the
ra te
and direct ion of ground
water movement
in
order to
evaluate
the
ult imate safe
yield
of ground
water reservoirs .
Measurements
of
the velocity of f luid
flow
throu.gh
porous media have been of concern to
the
hydrologis t ,
soi l
mechani-
cian, petroleum
engineer
and sanitary
engineer
for
more than
half
a
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
15/142
2
and heterogeneous
charac ter i s t ics of
the medium.
Most
equations
relat ing
head
to discharge,
time, space
and
hydrologic
propert ies have
been
derived through
applicat ion of
Darcy s law
to
the
continuity
equation. Thus, determination
of
the
hydraulic constants of an aquifer requires not only measurement
of
the
head
dis t r ibut ion
in
space
and
time
but
also
measurements
of
dis
charge from or
recharge
to
the aquifer a t
the
same locat ion
where
the
shape of the f low-field boundary
is knowno
Thus, a t
most
loca
tions
in
an
aquifer ,
i t
is not pract ical
to obtain
by direct m e s u r e ~
ments the data needed
for
applicat ion
of
the available
analytic
equations.
I f some
method
for
measuring ground water velocity
can
be found,
the
u t i l i ty of
the tes ts
to
determine the hydraulic
constants
of the
aquifer can be
greatly
extendedo
The obvious approach is
to include,
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
16/142
The simultaneous
t ransfer
of heat and
the
flow of water u n e r ~
ground
resul t
in
head
and
temperature
distr ibutions
which
can be
ex
pressed by different ia l
equations.
Some
of
these
qual i ta t ive re la-
t ions have been published. Some quant i ta t ive experiments
re la t ing
temperature and veloci ty
changes
have yet to be conducted
before
valid
conclusions
can
be
derived. Therefore,
a new
approach
is
sug
gested
in this work. That is to
ut i l ize
electrokinet ic phenomena,
known and
extensively
used in co l lo idal and biological
science,
for
the
evaluat ion
of discharge and velocity for
flow
of
f luids
through
porous materials .
When
a solid comes
in
contact
with
l iquid,
an e lec t r ic pot,ential
difference between
the two comes
into existance a t
the
interface.
Consequently, the l iquid will be
charged
opposite to
the
solid (wall).
Ions of the
l iquid
accumulate
near
the
solid
surface
and cause .an
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
17/142
4
to
flow. This
phenomena
is ow
well
understood for uniform c p i l ~
1aries
and
has
been
shown
also to
exist when
flow
occurs
through
porous
plugs and diaphragms see Abramson, 1934; Kraemer, 1942;
G1asstone, 1946; Overbeek
and
Wigga, 1946; Partington, 1949; Butler,
1951; Overbeek, 1953a
and
b;
Rutgers,
1954;
Bikerrnan, 1958; Bier,
1959;
Mysels,
1959;
Adamson
1960; Schulman and
Parriera ,
1963;
and
Davies
and
Ridea1, 1963).
Many measurements
of streaming potent ial
have been ut i l i zed
in studying
the
s t ructural
and
electrochemi.cal
properties of sol id surfaces in contact with l iquids Neale
and
Peters , 1945;
Buchanan and
Heyman 1948 and 1949a
and b;
Goring and
Mason
1950; Dulin
and Elton, 1952
and
1953; Fuerstenau,
1953; Gaudin
and Fuerstenau,
1955; Biefer
and Mason,
1959; Martinez, 1960; Par-
r i e ra
and
Schulman, 1961).
I t
is
well known
that ,
when
l iquid
flows
through porous materi-
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
18/142
5
needed experimental procedures th is study has been
undertaken.
Experimental
procedures
developed
and
equipment used
in
th is
work
have
proved
to
be r e l iab le
enough
to
investigate the approach sug-
gested.
Analyt ical
relationships developed
together
with the experi-
mental
work could probably be
used
as the basis of a rel iable method
for
measuring
the
rate
of
flow
through
porous
materials .
Objectives
The object ives
of
th is
study
are:
1. o develop
the analyt ical relationship
between
the
ra te
of
flow
of
f luid
through porous
material
and
streaming
current
I
and
streaming
potent ia l
E induced
by
th is flow.
2. o
establish
a rel iable
experimental
procedure for
the
me.a-
surement
of
E
and
I
developed by
flow of
water
through porous materi -
al .
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
19/142
CHAPTER
I I
ELECTROKINETIC
PHENOMENA
Histor ica l
Elect rok inet ic phenomena
were
observed as
far
back as
the
begin-
ning
of the
19th
century. In 1808 Reuss discovered that flow through
a capi l lary
element
can be induced by the applicat ion of an e lec t r ic
f ie ld . About hal f
a century
l a t e r in 1852,
iedmann
performed
a
number of
quanti tat ive. experiments
and
promulgated
one
of the funda-
mental theories of elec t rokine t ics .
His
theory,
which
has been ver i -
fied
many t imes,
sta tes that
the volumetric
flow t ransported through
porous material by galvanic current i s d i rec t ly proport ional to the
in tens i ty
of the applied
current.
In
1859
Quinke
discovered
the
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
20/142
7
In 879
Helmoholtz developed the double layer
theory
which re
lated
analyt ical ly
the
elect r ic l and
f luid
flow
parameters
of
elec
t rokinet ic
t ranspor t .
Although subsequently modified,
his develop
ment stood the t es t
of time and
s t i l l represents
an acceptable
formu
l t ion
of the electroosmosis phenomena in most capil lary mater ial .
Actuated
by an
in teres t
in
the nature of
s t b i l i ty
of
s u s p e n s i o n s ~
Smoluchowski (1921) reinvestigated the theory
of Helmoholtz.
F:reund
l ich (1909) published and discussed the
resul t s
of some prior compre
hensive experiments performed by other
inves t iga tors .
His d e m o n s t r a ~
t ion--based on Saxen s experimental
resul t s 1 8 9 2 ) ~ s h o w e d that i f
both
electroosmosis and
streaming potent ial
are
measured in the
same
system,
then
the proportionali ty
constant
in electroosmosis re l t ing
volumetric flow
to e lec t r ic
current was ident ical with that
rel t ing
streaming potent ial and applied pressure. From tha t
time
on thE: f ie ld
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
21/142
Recent
Theories and Modifications
to
Helmoho1tz
He1moholtz theory
The
basic premise of Helmoholtz development is that
when a
l iquid and solid come
into contact ,
there is usual ly an accumulation
of
ions of the l iquid near the surface of the solid to produce a
double layer. Helmoho1tz envisaged the double layer as
two
para l le l
planes of opposi tely
charged
ions. The fixed layer adheres to the
surface
and
a
neutra l iz ing counter ion layer tha t
exis ts
in
a
single
plane para l le l to the surface
a t
a
distance
x
into
the l iquid e
considered the
mutual
act ion
between
the
ions
to
be
negligible .
Gouy theory
In 1910 Gouy introduced a more rea l i s t i c concept of
the
poten-
t i a l and charge dist r ibut ion
in the
f luid
adjacent to
the sol id wall .
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
22/142
Stern
theory
In
1924
Stern
suggested
a
type
of
double
layer
which
is
a com-
bination of the
simple
Helmoholtz fixed layer
with
the
Gouy
diffuse
layer. Roughly
the potent ia l
is assumed
to
vary with dis tance as
shown
in
Figure
I . In Stern s picture of
the
double
layer , he
con
sidered the possibi l i ty of
specif ic
adsorption
of ions and assumed
that these ions were also located in the plane x. This
layer
of
adsorbed ions is called the Stern
layer.
The
to tal
potential drop
is accordingly divided
into
a potential
drop over
the diffuse part
of the
double layer
and
that over
the
molecular
condenser.
Present
theory
9
With
a l l these modifications the theory ow reaches acceptable
status that could be summarized
as
follows:
The charge on
the solid
wall of
the
part ic le)
at t racts
counter
ions
and
repels s imilar
ions.
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
23/142
10
equi l ibrium condi t ions a re destroyed
and a
se r ie s of e lec t r ok ine t i c
e f f ec t s
may
be
observed.
Each
may
be
dis t inguished
pr imar i ly
by
the
nature of
the
dis turb ing
force , which
may
be
mechanical or e l e c t r i c a l .
One
of
these e f f ec t s i s the s t reaming po ten t ia l . In
t h i s
case
the
dis turb ing
force is mechanical movement
which crea tes an
e l e c t r i c
cu r ren t .
When
the
l i qu id
i s
forced to
f low
through
the
charged
c a p i l l a r y ~ cur ren t
flows with the l iqu id
and i s known as
the
s t ream-
ing
cur ren t see
Chapter
IV). This cur ren t can bui ld up
a
po ten t ia l
d i f f e r ence
between
two
e lec t rodes s i tua ted a t the ends
of
the
cap
i l -
l a ry
known as s t reaming po ten t i a l .
Factors Affect ing Streaming Po ten t ia l
in
Porous
Media
As
may be
s e e n ~
the s t reaming po ten t ia l
i s
dependent upon three
majo "
fac tors :
the
composi t ion
of the
l i qu id
phase (permeant
so lu-
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
24/142
11
contact with pure water or di lu te solutions. This charge ar ises
ei ther
from
the adsorption of
hydroxyl ions
or
dissocia t ion
of
H
ions) or the
adsorption
of
negative
ions from
elec t rolyte
solutions.
For example,
with
potassium or sodium chloride solutions
tested, the
negative
potent ial
of sand could
be
as
shown
in Figure 1, Appendix.
Effect of the composition of l iquid phase
The effect
of the
composition
of
the l iquid is
detected in
the
electrokinet ic behavior of streaming potent ial
for
l iquids
contain-
ing dissolved elec t rolyte
That
effec t
wil l
be recognized
through
i t s effec t
on the
double layer thickness and the conductivity of the
system. The
nature of the elec t rolyte
is as important
as i t s
concen-
t ra t ion The
resul t s
found
for
the
influence of
ions on potent ial
consequently
on streaming potent ial) may
be
summarized
as:
1.
The
nature
of
the counter
ions
is
more
effect ive
than
tha t
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
25/142
12
streaming
potential . Investigations of
the
re la t ion between turbu-
lence and streaming potential with
an
objective being
the
use of
e1ectrokinetics as a tool for turbulence
measurements
in pipe flow
have
been conducted Cermak
and
Baldwin, 1963). The research accom-
plished
by Binder 1960) showed
that
streaming potent ial
might be
a
valuable tool
in
the study
of
turbulence
and
unsteady water
flows.
Chaung
and Duckstein 1962) ci ted by
Cermak
and Baldwin, 1963) s u ~
ceeded in adapting the electrokinet ic electrode to
the
study of ful ly
developed
pipe flow see also
Binder and
Cermak, 1963).
Some thoughts
have
been
given
also
by Bocquet 1952)
at
the
University
of
Michigan
regarding
the
measurement
of
blood flow in veins
by streaming poten-
t i a l techniques.
In
the f ie ld
of soils
porous
media), not much work has
been
done
on the
usage
of
streaming potent ial
for
fluid
flow measurements
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
26/142
3
account for the
non-Darcy
behavior of flow through
Kaolini te .
Olsen
1966) conducted an experimental investigation
to
study values of
the induced
hydraulic
and potential difference across Kaolinite sam-
ple
as affected
by the form of the externally
imposed
inducing
force.
These forces were in the
form
of
l iquid flow,
current and Na l
con
centra t ion difference
across the
sample.
The research work reported
in
here,
however, is
intended
to
develop
an
analyt ical
re la t ionship
between
streaming
potential and
streaming
current induced
through
sand
beds by
flowing solut ions and
the
r te
of
flow
of
these
solutions.
The
experimental
investigations
were conducted to tes t
this analyt ical relat ionship;
also to deter
mine
how
this
re la t ionship
wil l
be
affected
by
electro ly te concen
t r t ion in the percolat ing solut ions and the
size
of the p r t ic les
forming
those beds.
These
relationships
are
then
discussed
in order
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
27/142
CHAPTER
I I I
DERIVATION OF THE ANALYTICAL EQUATIONS
Streaming Current
Assume that Poiseul l s theory for velocity
dis t r ibut ion
(para-
bolic veloci ty
distribution)
in
a capi l lary
is valid
for
each
inf in i -
tesimal length of the flow channels. Then
in
a
length
oL of the
flow
channel
of
average
radius a, the
axial veloci ty
of flow of
l iquid
(of viscos i ty 11
at
a point any dis tance from the center under a d
i f -
ferent ia l pressure p (where Op = h as the flow channels are
horizontal with oz =
0).
= ~
V(r)
4110
L
2 2
(a
- r
1)
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
28/142
15
p
3)
I f , as
is usually the case, the ionic atmosphere
a t the
wall
the
diffuse double layer) is extremely thin in comparison with
the
pore diameter, then the gradient
of
the velocity, :; can be assumed
to
be
constant
inside
the
layer,
and
the
velocity,
v x)
at
any
dis-
tance,
x x
= a-r , from
the wall
is
given
by
x
S
dv
v x)
dx) x=o
dx 4)
0
as
dv
dx)x=o
2 T)L
5)
therefore
x
v x)
=
dv)
dx
pax
o dx x=o
2T}L
6)
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
29/142
16
r-a
i
_paD
[
(xd f)x=a
d'i'
dx
]
s t r
- 81)rrL
dx X=X
o
dx
x=xo
~
[
(xd' ')x=a
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
30/142
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
31/142
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
32/142
9
Streaming
Potential
This streaming current (convective current)
is responsible
for
the streaming potent ia l
E
t
As a
consequence
of the streaming
cur
s r
rent ,
a
potential difference will
be
set
up
between the
ends
of the
bed which in turn wil l cause an elect r ic
conduction
current I oppo
c
s i te
in
sense with the
streaming
current.
At
steady
s ta te ,
I
s t r
will
be balanced
by
I and
the potential difference, streaming
c
potent ial , wil l remain steady as
I - I
c s t r
and
the
to ta l
current
wil l
be
I + I = 0
c s t r
The conducting of the charge back wil l be through the l iquid and
solid
surface so,
16)
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
33/142
20
1940;
Jones and
Wood 1945; Gaudin
and
Feurestenau,
1955)
showed that
the
contr ibution of
surface
conductance
to
the conductance of
the
electrolyte in
the
plug
could be
appreciable. This contr ibution is
usually
compensated
by the use of a ce l l constant. In
such
case
k = where R is
the
no-flow resistance between
electrodes
and
C is
the
cel l
constant
and
So,
I
s t r
E
s t r
I
c
C
E
s t r R
R
I
s t r
x C
= TT
(l-ct).'
2
~
tr .
R
(18a)
C . q
R
under
the previously
mentioned conditions and as C is
constant ,
then
E = Constant • q = C q
(18b)
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
34/142
2
or current) increases nonlinearly
with
p While th is effect
is
not important
for aqueous solutions under pract ical conditions, i t is
signif icant for non-aqueous solutions where the ionic double layer
is
much
more
diffuse and may extend
into the region
of
turbulent
flow.
d) Darcy
Law
is
valid and
the
media
is
homogeneous
and
iso-
t ropic .
Limitations
and
Assumptions
The
previous conditions are
to be
sat i s f ied
for the val id i ty of
equations
15) and
18). The
following
is a discussion for
those
l imitat ions
in general and
degree
of
approximation in
cases where
any
of these
conditions is
no
longer sat i s f ied
Laminar flow condition. The condition
that
the flow of the
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
35/142
22
concluded no effect
in their work.
However,
Rutger,
Desmet
and
Myer
1957) established
such an effect for diffuse
double
layer
as in
the
case of
benzene
in
contact with
glass) in
capi l lar ies and were
able
to develop
a
re la t ionship between
streaming
current
and the average
veloci ty
V V =
discharge/cross
sectional area) for
turbulent
flow
as
follows:
~
s
t r
- 20
v
where I ,D , are
as
defined before, 0
is
the thickness of dif -
s t r
fuse part of
double
layer
and
a is the radius of the capi l la ry .
Similar equations were obtained
by
Davis and
Ridel 1963).
Bournans
cited by Davies
and
Rideal, 1963) developed
the
analysis for the
case where
some
of the
ions from
the ionic sphere near the wall will
extend into
the turbulent core. His terms should be
added
to ei ther
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
36/142
3
large with
respect
to the thickness of the double layer . Burgreen
and Nakache 1964)
developed
another
analyt ical
solution
for the case
of the ul t ra f ine s l i t
Rice
and
Whitehead
1965) developed a solu-
t ion
for the case of f ine cylindrical
capi l lar ies
In
both
i t was
shown that the electrokinet ic potent ial i s dependent upon electro-
kinet ic
radius
which
is
direct ly
proportional
to the
capil lary
radius.
They ~ u g g e s t e d that
their function be used
in the case
of
ul t raf ine
pores
instead of the c lass ica l Helmoholtz
equations
in which the
potent ial
is
considered
to be
independent
of the capil lary pore)
s ize
Dielectr ic constant D
and
dynamic viscosity, lJ factors. In
the previous
derivat ion,
the
dielect r ic constant,
D
and
the
dynamic
viscosity, ~ o f the
l iquid
in the double layer were taken, as usual,
the same as for bulk solutions.
Some
authors have pointed out that
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
37/142
24
influence
both
and D. However,
comparison
of theoretical results
with experiment
showed
that
both
effects
are
rather
small
under
most
conditions
Hunter, 1966).
Chattoraj and Bull 1959) and Hoydon
1960) have previously shown that .for
l iquid surface having
adsorbed
films
giving
charge densit ies less than
30,000 esu/cm
2
, a good agree-
ment
with the
true potential
may
be
obtained
by
assuming
a
bulk
value
for
D and
in the double layer.
Surface
charge
densit ies
are
calculated from , potential by
means of Gouy
theory, for uni-univalent electrolyte
a t 25
0
C i t
is
Parriera and Schulman, 1961)
c ~
I
v ::::
134
Sinh 51.5
19)
where
cr is the electrokinetic
charge,
in electron charge/angstrom,
c
is
the sa l t
concentration
in mole/ l i t re , and , is
zeta
potential
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
38/142
25
experimentally
using
resonance method and Linton and Maoss have formu-
1ated those results
as
D
= 79.80 [
-
4.28
x
10-
3
t - 25) + 2.12 x
10-
5
t
-
25)2
- 4.1 x
10-
7
t - 25)3 ]
Partington
(1954)
has developed
the
following
formula
D
=
78.54 [ - .0046 t - 25) + 88 x 10-
5
t -
25)2
J
He
also
reported measured values for water at
25
0
C
to be 80.37
and
7902. Buchman and Heymann (1949c)
reported
D =
85.5,
80.8 and 76.5
o
for
6,
18 and 30 C
respectively.
Our experiments were conducted in the constant temperature room
where the temperatures were kept a t
a fa ir ly
constant temperature of
80 .5
0
F. At such controlled temperature, the temperature of water
and
solutions
was generally
kept at
25
0
C
.2
0
C.
So,
D
values
in
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
39/142
Thermodynamics of
Irreversible
Processes
Streaming current and streaming
potent ials
6
Since
a l l electrokinet ic processes are i r revers ib le the thermo-
dynamics
of
i r revers ib le
(non-equilibrium) processes
can be applied
to
derive
general
relat ionships
between
different
electrokinet ic
processes
including
streaming potential and streaming current
(Staverman, 1952; DeGroot, Mazur
and Overbeek,
1952;
Overbeek,
1953b;
Guggenheim,
1957; Taylor, 1960, 1963
and
1964; Zaslavsky and
Ravina, 1965).
When t ransport of l iquid and t ransport of electr ic charge take
place
by
simultaneous
e lec t r ica l
and
hydrodynamic processes, the
e lec t r ica l
and
viscous flows in terfere with each other giving r i se
to i r revers ib le processes (coupling phenomena) known as
e l e t r o ~
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
40/142
27
conductance, L2l represents e lectrohydraulic conductance, and L12
represents
the
hydroelectr ic
conductance
or
in
view
of
Onsager
re la
t ions,
both
are water-electr ic in teract ion coefficients and equal
each other .
Using another
form
of phenomenological
coefficients we
can write
q
J
L
LI
I
21a)
w p
I =
J
L q L
E
:2
e q e
As we have
sa l t moving in the system, we should include another equa-
t ion and another factor in
each equation.
In
di lu te
solution,
how-
ever, such
as
we
used, i t has
been shown
that the
flow of
sal ts
may
have
negligible
influence on
water flow Michaeli and Kedem, 1961).
The
coefficients in equations 21)
are
related to those
in
equa-
t ion 20) as follows
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
41/142
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
42/142
29
because
of
thei r
part icu lar
concern
with the
system under study:
a)
Fluxes
are
l inear ly related
to
driving forces;
i f they are
not, then equations 20), 21) and 22) need to be expanded
to
the non-
l inear case.
b)
Only
hydraulic
and elect r ical
gradients
cause flows;
i f
other
forms
are
acting,
then
addit ional
terms
must
be
included in
the above derivations.
The
requirements
that the forces and fluxes
be
l inear were
checked for
each
run
and
substantiated Figures
25, 26 and
27). In
each case the re la t ion between the discharge q and pressure was
shown
to be
l inear the same as for
the discharge
and streaming poten-
t ia1.
The requirement that
only
hydraulic
and elect r ical gradients
cause the flow was
met
by the experimental conditions. The two side
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
43/142
30
one of
these
two could be used as a check on calculat ions Tables
and 3 show a summary
of
these
coefficients
with
their
calculated
values
and
their
dimensions Conversion factors between experimental
resul ts and the
quanti t ies required
for computations
of
these coef-
f ic ients
are
shown in Table 1
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
44/142
CH PTER
IV
EXPERIMENT L PP R TUS
ND PROCEDURE
Apparatus
The experimental
apparatus
is
shown
in Figures
2 and 3.
Details
of
dif ferent
parts are
shown
in Figures
4
and
5. The
paratus
consists
of
three main parts: streaming ce l l s
flow system
and pressure manometers
and
the
e lec t r ica l
ci rcui t and elec t ronic
equipment
for
measurement
and
recording
of
the streaming
potent ia l .
Streaming
cel l
Two ident ical streaming ce l l s were used, one f i t ted with s i lver -
s i lver chloride electrodes and the other with pla t in ized
platinum
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
45/142
3
Flow system
Deionized conductance)
water
and
sa l t
solut ions
were
stored
in
an elevated pyrex reservoir . The l iquid then flowed to the s ide
tank which was
kept
a t a
desired
constant posit ion on the stand by
bolting i t s support
into
the corresponding holes at equal dis tances
into
the
stand.
To
keep
the
head
constant
in
the tank, the
flow
was
approximately control led by the screw clamp and the outflow was
wasted
through an
outflow system
near the
top
of
the tank. The tanks
have provisions
so
that thermometers and
conduct ivi ty
ce l l electrodes
can be
fixed
through the top
of
the tank. The flow connections are
also
arranged
such as
to
allow
for
spot
samples
to
be
drawn during
flow into or
out
of
those
tanks. Spot samples could be
obtained
also
from the outflow
system. Solutions
from the
tank were
conveyed
to
the two side
compartments
of
ei ther
cel l through
the flow control
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
46/142
output
from
the electrometer was fed into the y
axis
of a time
base
recorder
Model HR-96
where
the
x
axis
was
an
adjustable
time
of
sweep. The
recorder has
a range
from
.05
in/sec
to 20
in/sec in
steps
with a chart
that
provides 7 x 10 inches
of
plot t ing
area.
Resistance
and
conductivity
of
the
porous plug column
were
measured
with
a
general radio
impedance
bridge
model 16S0-A)e
The
specif ic resistance and conductivity
of the
permeant solution were
measured
by dip
in
a
conductivity
ce l l
model R
16B2.
Details of Procedures
Preparation of sample
water and
solutes
Ottowa sand C109
and
C190
grain size
dis t r ibut ion
curves
shown
in Figure 42, was
leached
repeatedly in boil ing concentrated
hydro-
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
47/142
34
through the
porous
plate . Also, no t race of a i r
would
be
formed on
the
electrode
which
might cause
change
in
the
electrode
potential .
Very
few workers Goring and
Mason, 1950) concerned themselves
with
the deaerat ion of water, yet proper deaerat ion is essential in ob-
taining reproducible resul ts
and
i t s
importance
cannot be too strongly
emphasized. Chemical reagents used were
purif ied
crys ta l reagents.
Electrodes
Silver-s i lver
chloride
electrode. Silver-s i lver
chloride
elec-
trodes
were prepared from
a perforated
l ight platinum disc
two
inches
in
diameter
and one
mill imeter
thick.
The
disc
had
144
per-
forations
per
square
inch, each .032 inch
in
size. The face of the
disc was
covered with
80 mesh
platinum
gauze spot welded to
i t .
A
platinum wire
was
elect r ical ly spot
welded
to
the back
of the
per-
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
48/142
35
10 gm K Ag (CN)2) potassium s i lver cyanide per l i t re The
sa l t
was
prepared
af te r
the procedure of Basset
and
Corbette:
add
41
gm
of
s i lver cyanide to an aqueous solution of 20
gm
potassium cyanide.
When the
s i lver
plating solution was used
for
more than one time,
t
was freed from
the
free cyanide by adding di lu te s i lver ni t ra te
solu-
t ion unt i l no
discolora t ion
was
observed.
Silver deposition was
coo-
2
t inued
for
six hours a t 004 rna
cm
) 81 rna. When the pla t ing was
f inished, the electrodes were soaked in concentrated ammonium hydrox-
ide NH
4
0H)
for
three hours and washed with water
for
two days. The
same ce l l vessels were used in chlor idiz ing the electrode
with
the
electrode as
anode
in
the ci rcui t and electrodeposit ion. This process
was performed in the dark
by
turning
the
l ight off and covering the
anode
vessel
with
black.
2
The
current
densi ty was the same .4 m.a/em )
for about 30 minutes using 0.1 N
hydrochloric acid
(HCI)
as
electro-
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
49/142
36
The gauze was brief ly immersed in a di lu te aqua
regia
cleaning mix-
ture
made
of
three
volumes
of
12 N
Hel,
one
volume
of
16 N
ni t r ic
acid and four volumes of water).
The
electrode
was
then treated with
warm
concentrated
ni t r ic
acid
and
washed in conductance water.
Im-
mediately before plat in izat ion, the electrodes were cathodical ly
electrol ized
in
di lu te
0.01 N
sul fur ic
acid for
10
minutes
and 30
m.a.
The electrodes
were then
washed with double
dis t i l l ed
water
and then plat in ized in the
previously
discussed elect r ic cel l f i l led
with
a two per cent solution of commercial
platinum
chloride in 2 N
hydrochloric acid.
The
current density
was 300
m.a. ~ 1 5
ma/cm
2
for 15
minutes.
The
whole procedure
was
then
repeated while the
electrometer was positioned to the current measurement. The deposi-
t ion
was
hardly
vis ib le
grey and the
no
flow potential
was
about
2
m.v. in
conductance
water.
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
50/142
7
and
the
chart
cal ibra ted
by
adjust ing the vernier control located in
the
center of
the
attenuator control.
The
mult iple pole
multiple
throw e lec t r ic
switch was then switched
to the desired
cel l Ag-AgCI
and platinum electrode cel ls simultaneously. The
flow
switch board
was then switched to l e t the solution flow from
r ight
to l e f t through
the sample.
The
streaming potent ia l recorded
continuously
on
the
recorder chart . When the
steady s ta te
condi t ion for
both
the
poten·
t i a l
and
pressure head
was reached
the
manometer readings were r e ~
corded and
the
flow
stopped.
The
flow
was then reversed to
flow
from l e f t to r ight and the previous process repeated. This whole
procedure was then repeated at s ix to eight
dif ferent
pressures
yielding several
se ts
of data a t dif ferent values of streaming poten-
t i a l .
In
the f i r s t preliminary runs the ce l l resistance was measured
for
each
pressure
and
found
to be
fai r ly constant
over the period
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
51/142
39
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
52/142
Figure
43.
For
dis t i l l ed
water
and
di luted solut ions
of
KCl the
specif ic
conductivity
of
the plug
was
compared
to
that
of the bulk
l iquid thus
indicat ing
a large surface conductance. With
increasing
concentration
of
electrolyte surface conductance effect becomes less
and the greater part
of
the conductivity becomes due to bulk
l iquide
The ce l l
constant ,
C C
=
conductivity of the l iquid x bulk
resis tance of
the
plug) therefore
decreased
unt i l the normality
reached such a
value
that surface conductance was no longer s ign i f i -
cant; C then remained almost constant . From Figure 43 i t
is
evident
that for the
plug, the
ce l l
constant ,
C i s e f fec t ive ly
constant
-5 -2
for
the range
of
normality
= 5 x 10
through
2 x 10 • So a value
for C 0.85 was taken as a representative
constant
for
the f i r s t
sample 1 and C
= 0.510
for sample 2.
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
53/142
40
with
the
electrodes.
He
also
concluded tha t th is extraneous potent ia l
is
made
up
of
two
phenomenons, one
associated with
the
flow
and
the
other
with polar iza t ion. However, polar iza t ion could be in turn
con-
nected
to
the
flow condi t ions.
The fact tha t polar iza t ion potent ia l
may
stay constant during flow
but may
change once flow has stopped
indicates
that connection. Thus one
can conclude tha t
the
electrode
contr ibutes an arbi t rary EMF to the streaming potent ia l
which
con-
t inues for a period af te r the
flow has
stopped.
Previous methods
of obtaining
streaming
potent ia l
Although
electrode potent ia ls (flow,
polarizat ion)
had
been
noticed some
time
ago,
i t
was not unt i l recently (Zuker, 1959;
Korpi,
1960) tha t thorough
invest igat ions
have
been
made. Most of the pre-
vious
workers
t r ied to eliminate the electrode effects or
render
41
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
54/142
under
a known almost constant
pressure
and the streaming potent ial
was
read, then the
flow
was
stopped
and
readings
were
taken
af te r
sixty seconds. Next
with
the
flow in
the opposite direct ion the
streaming potent ial was
measured.
The no
flow
potent ial (reading
af te r
s ix ty seconds from the flow stoppage) was added
or
subtracted
as correction to the reading depending
on the
direct ion of the l o w ~
This
procedure produced
a
s t raight l ine re la t ionship between
E and the
pressure, P,
for
solut ions of very low concentrations.
s t r
Yet i t
produced anomalous curves for
solut ions
with concentration
-3
greater
than 10 N.
Also,
the corrected streaming potent ials in
both direc t ions do not seem to
agree
and produce two separate l ines
for E P
relat ionships
not
passing
through the origin, a
case which
is
not
supported
by
the electrokinet ic phenomena.
Korpi
used
a procedure--which was
the primary object of his
42
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
55/142
condition that the convection current , I t is
balanced
by the con
s r
duction
current
(counter
current) ,
Ie
and
then
the
to ta l
flow
of
e lec t r i c i ty
wil l
be zero; I
s t r
+
Ie
O
I t
is when this condition
prevai ls that one
should stop or s ta r t
the flow
and
record the
read-
ings
which wil l
be the
actual
streaming
potent ia l .
Secondly,
the
electrode contribution
to the
streaming potent ial
is embodied in the streaming potential readings and prevails
for
a
period
af ter
the
flow
is stopped (Zuker, 1959). That contribution
is
related
to the flow and
proved
to
be
direct ional . So when
the
flow is suddenly
stopped or s tar ted , the sudden increasing or de-
creasing
ordinate is not only the streaming
potential but will also
be the flow potential added or subtracted to the
streaming
potent ial
depending on the flow direct ion.
Modifications the
procedure
43
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
56/142
=
a. The actual
streaming potential
wi l l
then
be a ; b Korpi s
method
when
used
wil l
give
an
erroneous
value
ei ther Eb E )
or
c
E
f
- E
g
.
Those
two
values wil l algebraically
include,
rather
than
the electrode potent ia l , the effect of
the
response of the recorder.
This factor was
observed by Korpi
and suggested
as
a source of error
in his recorded values.
s
i t could be seen from Figures
10 and
-4
-3
for
10 N
KGl
and
10 N
KGl
i f
Korpi s
method
were used, then
streaming potential
in one
direct ion wil l be
25
per cent to
100
per
cent
more
than
that
in
the other direct ion (compare ordinate
1
and
2
of the f igures) . The eff iciency of our procedure is appreciated for
the cases of relat ively
high
concentration
and
low
pressure
(rate of
flow).
In these cases
the
error effec t
using
the
Korpi method
may
be
more than
the
actual
readings,
and the ordinate considered by
Korpi may
give
negative values .
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
57/142
45
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
58/142
streaming current induced due to the
same
different i l pressure head.
Most
of
the
resul ts
obtained
produced
a s t ra ight l ine relat ion-
ship
between both
E
and
I
and the effect ive different i l pressure or
discharge.
These
l ines passed
by
the origin in agreement with the
electrokinet ic
phenomena and
the analyt ical developments.
Flow and pressure
measurements
were found
to
be suff ic ient ly
consistent
for
repeated runs t steady
s t te
conditions. Errors
from
these
sources
i f
any
are within the precision of the tes t
measurements.
Experimental
Results
8unnnary of the
complete
resul
ts from
the
experimental
investi·-
gations
is given in
Figures 5 to
41. Only concluding
results
are
presented
here which i l lus t r t e the principal
features of
the stream-
46
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
59/142
Experimental resul ts are presented here under the
following
headings:
a) Plug
resistance,
b)
Rate
of
flow
and
applied
differ-
ent ia l
pressure,
c) Phenomenological coefficients and electrokinet ic
couplings,
d) Rate of
flow and developed
streaming potential and
streaming
current,
e) Salt concentration and
par t ic le
s ize effects
f)
Temperature
effects
g) Zeta potent ia l ,
h)
Pract ical
considera-
t ions.
Plug
resistance
The
plug resistance
of
the
cel l
was
measured
for
each run and
results
are
shown
in
Figure
16.
In
th is
figure
log plug
resistance
is plotted against log electro ly te concentration
normality)
in the
permeating
solution are tabulated. From the graph i t
can
be seen
that a l l resistances
are
below 10
5
ohms for concentrations greater
than 10-
4
N
47
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
60/142
Rate
of
flow and applied di f fe ren t ia l pressure
3
Flow
ra te
means
flow
ra te
per
uni t
time,
i e
ern per
second.
For
calcula t ion of seepage veloci ty in
ern/sec,
i t must be divided by
a factor equal to
the
cross-sectional area mult ipl ied by the porosi ty .
For Sl th is factor wil l be equal
to 19.06
and for S
i t
is equal to
17.20. The applied di f fe ren t ia l
pressure
here
is
the pressure be-
tween
the ends
of
the
sample in centimeters
of
water, for pressure
per uni t length i t
has
to be divided by 7.70. Each
point on
the
graphs shown is the
average
of two readings, one
with
solut ions
flow-
ing l e f t to
r ight
and the
other
with solut ions passing r ight to l e f t
through
the plug
for
a l l values
measured.
Values
for the ra te
of flow
in cm
3
/ sec
are
plot ted as
a funct ion
of applied pressure in ern
of
water on Figures 25, 6 and 7 for con-
ductance
water, sodium
chlor ide and
potassium
chlor ide solut ions
48
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
61/142
The discharge
ra te
q
will
then
be
P
A
=
K L.
ld
2
3
a
A
E
T
I-a )2
.
.
L
23)
d
0.023
centimeters,
a
=
31 and
\
= 5.50,
and
d
0.0575
centimeters,
a
=
28
and
e
=
6.12
and
(.9..)
for
Sl
p
= 0.20
for S2
From
the previous
experimental resul ts
reported
in
this
study
Fig-
ures 25, 26 and 27),
or
Sl
is on the
average
= 0.485, and
for
S2 =
2.20.
then
49
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
62/142
clear that there
was no
significant difference in the
p vs q
re la-
.
h
d
tt
. Th1 s means
that
10ns
1p
ue
0
coun
ere
ec
ro-osmOS1S.
q E=o
will
be
the same as g)
q
1=
The
effect
of
sa l t concentration
of
the pore
f luid on the
ra te of
flow showed in
general
that
there
was no
effect
on
the pressure
discharge
relat ionship due
to change
in
elect ro ly te
concentration for
both samples and
solutions
tested.
Phenomenological
coefficients and electrokinet ic
couplings
Phenomenological coefficients were determined from experimental
results
together with
equations (20)
and
(21)
and calculated
values
are
summarized
in
Tables 2 and
3. s these equations involved
both
e lec t r ica l
and
mechanical
units
i t
was
necessary to convert
the
ex-
perimental resul ts into cgs uni ts . These
required
conversion factors
are tabulated in Table 1.
After
having determined those coefficients ,
50
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
63/142
Also, as
w
have sa l t moving with the system,
then
i t
is
expected
that
the
flux of
sa l t
would
affec t
the
rate
of
flow
Taylor,
1964). The
experimental resul t ,
however, has shown
neither . This
is
due
to
the fact that ,
in
case of saturated coarse
sand,
the linkage
t ransfer coefficients
are
very
small
with
respect
to the direct ones.
Also,
in di lute
solution
such
as the ones
used,
i t has been shown
that Michaeli and
Kedem
1961)
the flow of
sal ts
has negligible
influence.
This
means that
the
flow of
solution
is
determined only
by the
effect ive
pressure, and
this is what
was actu-
al ly
observed.
Rate of flow and developed
streaming
potential
and
streaming current
The values for
streaming
potent ia l , E for different samples
-6 -3
considered
ranged
from
30 x 10 to 240 x 10 vol ts . Streaming cur-
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
64/142
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
65/142
53
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
66/142
concentration. Similar relat ionship in the form of S c l og
N d
where
d is
another constant
value
for
each
size and
c
related
also
to the
sa l t
concentrat ion.
This
could be
seen from
Figures 18
and
20.
In th is
case
the
two
l ines approach
each
other in
a
similar
man-
nero
The
conveyance
of
charges
is l imited
only
to the
diffuse
part
of the double layer , i . e . to the l iquid that can flow with
respect
to the surface.
The
potent ial within such
layer
decreases
pract ical -
ly
in
exponential manner
see
Figure 1).
This diffuse double
layer
has no sharply defined
end
point
but slowly
becomes negligible. I t
is nevertheless convenient
to
assign to i t a thickness designed
usually by 6 This thickness changes
great ly with the normality of
the solution. Hence, when the
sa l t
concentration in the permeating
solution increases i t suppresses
the
double layer , especially
i t s
54
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
67/142
by both v and then one would
expect
i t to vary l inear ly with log
sa l t concentration. The reason
for
more
rapid
decrease
of
streaming
potent ial E (than
streaming
current
I) due
to
increase in
sa l t con-
centra t ion may be
due
to the fac t tha t E
is
proportional to
both
I
and the conductivity
of
the bulk solution. Hence, rather than being
proportional only
to and the
conveyance, i t
is
also affected
by
change in the conductivity. The l a t t e r is found also to be propor-
t ional
to
log sa l t
concentration. Therefore, one would expect log
E
i Ci= - )
to be
proportional to log normality
of
the bulk solution.
q
According to class ical derivat ions He1moho1tz and Smow10wsky)
the size and shape does
not
affec t
streaming
potent ia l . The o n v e n ~
t iona1 equation
(25)
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
68/142
6
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
69/142
were multiplied
by
~
and the resul ted
values were plotted on Figure
19 together with the
experimental resul ts
a
close
agreement was
ob-
tained. The
difference
between
calculated and
observed values, how-
Rl R
thought to
be
due
to the
difference between and -1
c
l
c
2
ever,
is
This difference was
actual ly
about
10
per cent.
Temperature
effects
By temperature effects
i t
is
meant the
effects of
change
in t e m ~
perature
of the sample
and
the
percolating solutions
on the
resul t-
ing streaming potential provided that al l
other
factors are kept con-
s tant .
All the experimental
resul ts
reported
in
these
have
been
ob-
tained by keeping
the
whole apparatus in the constant
temperature
room with the l iquid solutions always l e f t
in
the room unt i l
their
temperature
was
the
same
as that of the room, i . e . at
80
lOF. How
ever, two special runs were made with
the temperature in the
room
57
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
70/142
order
of
-0.20
millivolt/oC.
Variations due
to temperature
effects
may
be related to the increasing thickness of
the double
layer with
the
increase in
temperature.
I t also could be
due
to changes in
die lec tr ic ,
D, and
viscosity with
change in
temperature.
As
. dD ,
I
hown previously Chapter I I I , dT .30 was
reported
for conduc-
tance water.
Zeta potential
Of
paramount importance
in
the quanti ta t ive study represented
here is the evaluation of
the
zeta
potential ,
As mentioned be-
fore,
C
is
the
potential
at
the
plane
of shear
(Figure
1), that
is
the potential at the
boundary between
the solvent adhering to the
particles at rest and
that
which moves with respect to i t .
Streaming current is given previously as
58
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
71/142
Calculated values for
1 and 2 for
KCl are tabulated
in Table 4
and
were
plotted
as
a
function of KCl concentrations Figure
22 _
s
shown
in this f i gu r e , decreased l inearly with the logarithm of
the sa l t concentrations wi t h values higher for
S2-
Two separate
l ines f i t ted the calculated
values for
1 and 2
These two l ines
are not paral le l but
approach
each
other as
sa l t concentration de-
creases.
Helmoholtz-Smowluchowski
class ical formula
is
usually used in
ca. lculat ing,
potential from streaming potential
measurements_
This
equation
has been amended by several
authors Briggs, 1928; Rutgers,
1940 and
there is
a general
agreement now Buchanan and
Heymann,
1949c) to
use
the equation
JTT}
= D
Ek
P
29)
59
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
72/142
considered
to
avoid
surface
conductance problems.
Buchanan and Hey-
man
suggested the function
where l l variables as defined
before.
The equation s t i l l includes
c, which would affect the precision of calculation. The Davis and
Ridea1
re la t ion
is
applicable
only
for
capil lar ies
and
needs
to
be
adjusted
to
be
used
for porous materials .
In
our procedure we
use
TT
= ))
30)
This
is believed to constitute
a
satisfactory
method
of finding
.
Besides
avoiding conduction
problems,
i t pOints out the effect of
both size
and shape
of
the media on
.
Our calculated
values
for
for
10.
4
N KC
is
190 m.v. This is in close agreement
with
the
60
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
73/142
material .
Sedimentary
rocks
are
more soluble than igneous rocks.
Because of
the ir
high
solubi l i ty
combined
with the ir
abundance in
the
ear th s crust , they furnish a major portion
of the soluble con-
st i tuents
to ground water. Out of the commonly added cations due to
sediment rocks
sodium,
Na, and calcium, K, have the highest
possibi l i -
t ies .
Bicarbonates, carbonates and sulfates are the corresponding
anions. Chloride,
CI,
also occurs to a certain amount, with sewage.
connate waters
and
intruded sea water
as i t s
major
contributing
source
Foster, 1942; Todd, 1960).
For the experimental resul ts reported in this study, two sal ts
NaCl and KGI were used as solute in
the
test solutions. For each
run,
one at a time each of the two sal ts at a specified concentra-
t ion was used. The normality of the solutions was used
to express
their sa l t
concentrations.
Therefore, i t was fel t
necessary
to test
61
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
74/142
solut ions. This
suggests
the feasibi l i ty
of the
use
of this proce-
dure
for
natural ly exist ing
ground water with dissolved combined
sal ts as
well
as solutions
with
one soluble sa l t
Considering the di f f icul t ies
connected
with
the determination
of the normality of these natural waters, an alternative method to
the
normality was
thought
to be used to express the
concentration of
solutions. This
is done
by
measuring
the electr ical conductance
of
the solutions. When the experimental resul ts for E, I and q for
these simulated
natural
ground waters
were
compared
to
those
for
NaCl
and K l
solutions
tested
before, comparable results were obtained
provided
that
conductance of the
solutions
was taken
as
a parameter
Figure 24).
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
75/142
CH PTER
VI
CONCLUSIONS ND SUGGESTIONS FOR FURTHER RESE RCH
Conclusions
Analytical derivations
and
analysis of
the
experimental
inves-
t igations, together
with
the subsequent interpretation
and
discus-
sions
of the
results from
this study,
suggest the following conclu-
sions with respect to streaming
current and
streaming
potential
in-
duced by
water
flow through porous media.
1. The flow through samples
tested
followed Darcy s law and
the ratio
of
petmeability
coefficients
of
different samples agreed
with
Kozeny Carreman equation,
2. There
was no significant
difference in flow
versus pressure
6
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
76/142
in the form
of
I = Clq and E = c
2
q are suggested
in
which C
I
and C
2
are dependent
upon
sa l t concentration and
par t ic le
size diameter.
5. Both streaming current , I and streaming potential , E, were
affected
by
sa l t concentration
normality and
less affected
by
the
type
of
ions
in
the solut ion.
An increase of
soluble
sa l t
con-
centrat ion resul ted
in a
decrease in
both E and
I .
A
sharp
decrease
was observed in case of streaming
potential whereas
a
gradual
de-
crease was
observed
in the case of streaming current .
6.
Increase in soi l particles
effective
diameter,
a t
a con-
stant sa l t concentration, caused a
decrease
in both a and S
where
I
S
= - •
q
This
decrease was more for dilute
solu-
tions.
These
relat ionships may be expressed
by
log a
= a
long
N b
and S = c
long
N a where a and c related to sa l t
concentration,
band d related to part ic le size.
6
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
77/142
easy
procedure for cases
where such
effect is of a significant amount.
11.
Analytical relat ionships
developed together with the
experi-
mental
work could probably be used as the
basis of re l iable
method
for
measuring
the rate
of flow
through
porous
materials.
Suggestion for Further Research
Experimental investigations in
this
study
were
limited only to
sand samples
of
effective diameters
of
0.230 and
0.575 millimeters.
Permeating
solutions
tested
were conductance water sodium
chloride
and potassium chloride solut ions.
Combination
of
sal ts as
solutes
in
the
permeating
solutions
were
tested in order to determine the
pract ical i ty of the proposed procedure
for naturally
exist ing waters.
In view of these experimental l imitat ions complete
information
on
the
practical aspects
of
the
flow streaming
potential and streaming
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
78/142
66
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
79/142
electrokinetic coupling
effect
was
negligible.
5. Some
studies
should
be
devoted to different problems that
will be
encountered
in
the
field
use
of the suggested
procedure,
Two
of these
problems
will be:
a)
To develop
a rel iable
procedure
for
placing
electrodes
in si tes without disturbing the media through which rate of flow
is to be
determined;
b)
To
isolate
part icular s trata f i t ted to these elec-
trodes
without disturbing the
general flow
pattern
of
the
flow.
6.
Util izat ion of the suggested
procedure
for
determining the
direction
of
the
flow
should be
experimentally evaluated. This
could
be done by placing
similar
electrodes
at
different positions in a
sample through which liquid is flowing. t is expected that the
highest induced E
or I would be recorded
between
the two electrodes
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
80/142
68
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
81/142
Buchanan,
A S.,
and E. Heyman. 1949a. The
electrokinetic potential
of barium sulphate.
Proceeding
of
the Royal
Society of
London
195A:152.
Buchanan, A S. , and E. Heyman. 1949b. Electrokinetic potential of
sparingly soluble sulfa tes . Journal
of
Colloidal Science,
Part I I I 4:137, 151.
Buchanan, A S.,
and E. Heyman. 1949c.
Determination of electro
kinetic potential
in concentrated s o l u t o n ~ by
the
streaming
current
method.
Journal of Colloidal Science
4 : l 5 7 ~
Bull, H B., and R. A Gortner. 1932. The effect of part ic le size
on
the
zeta
potential . Journal of Physical Chemistry
36:111.
Burgreen,
D.,
and F. R Nakache.
1963.
Electrokinetic flow in
capillary elements. Aeronautic System
Division
Technical
Documents Report 63-243.
Burgreen,
D.,
and
F.
R
Nakache. 1964.
Electrokinetic
flow
in
ul t raf ine capillary
s l i t s . Journal
of Physical Chemistry
68:
1084.
Butler, J . A V 1951. Electr ical phenomena at
interfaces.
The
Macmillan Company New
York, p. 30.
Cermak J.
E.,
and L. V Baldwin. 1963. Measurements of
Turbulence
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
82/142
70
-
8/18/2019 Streaming Current and Streaming Potential Induced by Water Flow T.pdf
83/142
Gurney,
R. W. 1953. Ionic processes in
solution.
McGraw-Hill,
New
York.
Haggis, H.,
J .
B.
Hasted,
and
A.
S.
Buchanan.
1952.
Dielectr ic
depression caused
in water by
addit ion of elect ro ly te . Journal
of
Chemical Physics 24:575.
Ham A. J . and E. D. M. Dean. 1940. An examination
of
elec trokinet ic
charge
as a function of the thickness of
the double layer.
Transaction
of the Faraday Society 36:53.
Harr,
M.
E.
1962.
Ground
Water
and
Seepage.
McGraw-Hill
Company,
New
York, p. 4.
Hasted, J . B., D. M. Robinson,
and
C.
H.
Collie.
1948.
Dielect r ic
propert ies of
aqueous
ionic
solut ions
pat 1 Part 11.
Journal of
Chemical Physics 16:1.
Helmoholtz,
H.
1879. Ann.
Physik
Vol. 7, Part 3,
p.
337; Gesamrnte
Abhanglungen,
Vol.