successful long-term operation results of seawater ro plant by using hollow fiber...
TRANSCRIPT
SUCCESSFUL LONG-TERM OPERATION RESULTS OF
SEAWATER RO PLANT BY USING HOLLOW FIBER TYPE
CTA-RO MEMBRANE MODULES
Toshitaka TANAKA
Desalination Membrane Dept.,
TOYOBO CO., LTD., Japan
October 18, 2017
Water Arabia
Background
Serious water-shortage
Membrane
Deterioration
18% Element
Deterioration
4%
Fouling 77% Biofouling
43% Organic
15%
Colloids
22%
Scale
13%
Khedr, Desalination & Water Reuse, 10/3 (2000) 8-17
(2/17)
Demand for desalinated water is increasing.
Seawater RO membrane desalination plants
Advantage: Saving energy
Problem: Fouling
(biological fouling)
Skin layer : 5 mm
Support layer : 45 mm
Pressure Vessel
RO Element
RO Module HU10255MI
Features of CTA Hollow-Fiber RO Module
Hollow Fiber RO Membrane
Outer dia. : 140 mm, Inner dia. : 55 mm
(3/17)
(4/17)
Features of CTA Hollow-Fiber RO Module
Structural Advantage
Cross winding
arrangement
Cross winding arrangement of hollow fiber
bundles can minimize pressure loss and
uniform water flow.
Space between hollow fibers is remarkably
large, so fouling matter can pass through
very easily
Large membrane
surface area
Millions of hollow-fibers are wound
into element configuration.
Compared to spiral wound
membrane element, hollow-fiber
membrane element has about
10 times larger surface area.
Much larger surface area
allows much less surface fouling.
(5/17)
Features of CTA Hollow-Fiber RO Module
Material Advantage
“Control biological fouling with chlorine disinfectant”
Hollow-fiber RO membrane made from CTA has a superior chlorine
tolerance compared to Polyamide membranes, and it enables direct
injection of chlorine disinfectant to RO modules.
The disinfection operation mode can also be optimized by continuous
chlorine injection (CCI) or intermittent chlorine injection (ICI).
Chlorine Injection to RO Membrane
1. Dechlorination before RO inlet to prevent deterioration of the membranes
from happening due to oxidation.
2. AOC (Assimilable Organic Carbon) problem has been reported.
ICI (Intermittent Chlorine Injection)
1. Intermittent chlorine injection directly injects chlorine disinfectant to RO
modules in order to prevent biological fouling on the membrane.
2. Membranes have to be resistant to chlorine.
Seawater Pretreatment
Sodium Meta
Bisulphite (SBS) ;
Continuous
Chlorine
HPP RO module
Seawater Pretreatment
Chlorine SBS;
Intermittent
injection
HPP RO module
Dechlorination Operation
(6/17)
Investigation on the Optimization of ICI Condition
(7/17)
Lag phase is for at least 6
hours from the incubation
start
0 3 6 9 12 15 18 21 24
Growth Time in Seawater [hr]
To
tal B
acte
ria C
ou
nts
[C
FU
/ml]
Lag Phase Logarithmic Phase
Initial counts: 104 CFU/mil level
Initial counts: 103 CFU/mil level101
102
103
104
105
106
Bacteria counts of 105
CFU/ml level became
below the detection limit
in 30 minutes after
chlorine injection.
0 10 20 30 40 50 60
Time after Injection of Chlorine [min]
To
tal B
acte
ria C
ou
nts
[C
FU
/ml]
101
102
103
104
105
106
Residual Chlorine: 0.5 mg/L
Residual Chlorine: 0.2 mg/L
Initial counts: 105 CFU/mil level
Initial counts: 103 CFU/mil level
Detection limit : 20 CFU/mL
Result of growth rate of bacteria in the seawater from the Red Sea
Result of sterilization of bacteria by chlorine
Summary of Bacteria Count Test
1. 104 to105 level of total bacteria counts became under the detection level
when the bacteria were exposed to 0.2 to 0.5 mg/l of residual chlorine for
30 minutes or more.
2. The number of bacteria stayed the same during “Lag phase” for at least 6
hours, after that, the number of bacteria increased exponentially. Even if
bacteria increased during “Logarithmic Phase" , 1-hour chlorine injection
every 24 hour could constrict the biofouling.
Seawater Pretreatment
Sodium Meta
Bisulphite (SBS) Chlorine Intermittent
injection
HPP RO module
Dosing (example);
0.2~0.5 mg/L
for 1hr/24hr ~
Intermittent Chlorine Injection (ICI)
(8/17)
Chlorine Consumption during ICI
Result at actual SWRO plantICI condition : about 0.5 mg/L (target value) for 1hr/24hr
(9/17)
Chlorine consumption*1
during ICI was high
Fouling potential
became high
*1 Chlorine consumption
means the difference between
R-Cl conc.*2 of RO inlet and
R-Cl conc. of RO outlet
*2 R-Cl conc. means “Residual
chlorine concentration”.
-0.6
-0.4
-0.2
0.0
0.2
0.4
0.6
0.8
0 5 10 15 20 25Time [Month]
Re
sid
ua
l c
hlo
rin
e c
on
ce
ntr
ati
on
[mg
/L]
-0.02
0.00
0.02
0.04
0.06
0.08
0.10
0.12
Inc
rea
se
of
dif
fere
nti
al p
res
su
re
[ba
r/d
ay
]
R-Cl conc. in RO inlet <Feed>R-Cl conc. in RO outlet <Brine>Increase of DP (moving average)
0
100
200
300
400
500
600
0.0
0.2
0.4
0.6
0.8
1.0
1.2
0 1 2 3 4 5 6 7 8 9 10 11 12 13 14
Actu
al
perm
eate
qu
ality
[ m
S/c
m]
Dif
fere
nti
al
pre
ssu
re [
bar]
Time [Month]
Differential pressure
Actual permeate qualityCriteria for chemical cleaning
Operation Result of ICI
Result of Site Test at Addur SWRO Plant in Bahrain (Arabian Gulf)
Stable Permeate quality
・ICI condition: from 1hr/24hr to 1.5hr/24hr, 0.3 mg/l as R-Cl conc.
・Addition of periodic continuous 24-hour chlorine injection
Maintaining of differential pressure at low level
ICI can effectively prevent biological fouling
(10/17)
Initial ICI condition: about 0.3 mg/L (target value) for 1hr/24hr
0
100
200
300
400
500
600
0.0
0.2
0.4
0.6
0.8
1.0
1.2
0 1 2 3 4 5 6 7 8 9
Ac
tua
l P
erm
ea
ter
qu
ality
[m
S/c
m]
Dif
fere
nti
al p
res
su
re [b
ar]
Time [Month]
Differential Pressure
Actual permeate qualityCriteria for chemical cleaning
Operation Result of ICI
Results of site test at Al-Jubail SWRO plant in Saudi Arabia (Arabian Gulf)
ICI is effective against biological fouling
(11/17)
Initial ICI condition: about 0.3 mg/L (target value) for 1hr/24hr
Differential pressure
was maintained at
low pressure level
ICI condition: 1hr per 24 hrs,
R-Cl conc. Fluctuated between 0.2 to 0.5 mg/L
Actual permeate quality was at the low level
Optimization of ICI
Condition during ICI Assumption Countermeasure
A small amount of
chlorine-consuming
matters was in RO
module
No need to
change the ICI
condition
A great amount of
chlorine-consuming
matters was present in
RO module or RO inlet.
Required
Change of chlorine injection frequency
Addition of periodic continuous 24-hour chlorine injection
*2 During ICI, it is desirable R-Cl conc. of RO brine/permeate is more than 0.05 mg/L (less than 0.10 mg/L).
Improvement method
(12/17)
*1 R-Cl conc. means “Residual Chlorine concentration”.
Feed Pressure
Brine Pressure
R-C
l co
nc.
R-C
l co
nc.
R-C
l co
nc.
RO membrane
Feed Pressure
Brine Pressure
R-C
l co
nc.
R-C
l co
nc.
R-C
l c
on
c.
RO membrane Chlorine-
consumption
Differential Pressure (Stable)
Differential Pressure (Increase)
Operation Result of ICI(13/17)
0
200
400
600
800
1,000
0.0
0.5
1.0
1.5
2.0
Pe
rme
ate
TD
S [
mg
/L]
Dif
fere
nti
al
pre
ss
ure
[ba
r]
Differential Pressure Permeate TDS
0
50
100
150
200
250
300
0 1 2 3 4 5 6 7 8 9 10Co
lon
y c
ou
nts
fo
r R
O
bri
ne
wa
ter
[CF
U/m
L]
Time [Month]
During SBS Injection During R-Cl Injection
Results of Site Test at Jeddah SWRO Plant (Red Sea)
Conductivity was stable during test period.
Colony counts of brine under ICI was at low-enough level.
ICI is a very effective disinfection method
ICI condition: 0.2~0.4 mg/L for 1hr/8hr
0.0
1.0
2.0
3.0
4.0
5.0
Diffe
ren
tia
l P
ressu
re
[bar]
0
500
1,000
1,500
2,000
0 10 20 30 40 50 60
Perm
eate
TD
S [
mg
/L]
Time [Month]
Operation Result of ICI
Jeddah Phase-2 SWRO Plant for 5-Year Operation (Red Sea)
ICI is applied as a basic disinfection method to all SWRO plants using
hollow fiber CTA based RO membranes.
ICI condition: 0.2~0.4 mg/L for 1hr/8hr
(14/17)
Product TDS satisfied the plant specification during 5-year guarantee
operation without membrane replacement.
Differential Pressure was maintained at a low level. Once a year citric
acid cleaning was enough.
0.0
0.5
1.0
1.5
2.0
2.5
3.0
1-Jan 2-Mar 2-May 2-Jul 1-Sep 1-Nov 1-Jan 2-Mar 2-May 2-Jul 1-Sep 1-Nov 1-Jan
Dif
fere
nti
al
Pre
ss
ure
[b
ar]
Date
Operation Result of optimization of ICI condition
(15/17)
ICI condition:
0.3 mg/L for 1hr/8hrICI condition:
0.5 mg/L for 1hr/24hr
Chemical cleaning :
4 times/year
Chemical cleaning:
2 times/year
The stable RO operation has been achieved by appropriately adjusting
the ICI condition depending on the quality of RO feed water.
Result at an actual SWRO plant in Saudi Arabia (Arabian Gulf)
Haql (SWCC)- 4,400m3/d (1989)
Duba (SWCC)- 4,400m3/d (1989)
Yanbu (SWCC)- 128,000m3/d (1998)
Yanbu (MARAFIQ)- 50,400m3/d (2006) Bahrain (MEW)
- 45,500m3/d (2005)
Al Jubail (SWCC)- 85,000m3/day (2007)(90,000m3/day)
Ras Al Khair (SWCC)- 345,000m3/d (2013)
Manifa (Aramco)- 27,000m3/d (2012)
Shuqaiq (SqWEC)- 240,000m3/d (2010)
Rabigh (RAWEC)- 218,000m3/d (2008)- 109,000m3/d (2015)
Al Birk (SWCC)- 2,200m3/d (2001)
Jeddah (SWCC) (RO1) 56,800m3/d (1989)(RO2) 56,800m3/d (1994)(RO3) 260,000m3/d (2012)
TOYOBO RO Membrane for Seawater Desalination
(16/17)
SWRO plant that applies ICI
Conclusions
1. It was demonstrated that ICI (Intermittent chlorine
Injection) was an effective method for preventing
biological fouling and it has already been proved
practically in the regions of both Red Sea and Arabian
Gulf.
2. CTA based RO membranes and ICI is a good
combination for a long-term operation of SWRO
desalination plant.
3. Even with the seawater of the Middle East, ICI can
ensure the stable operation of RO modules by
adjusting its condition to the followings.
- Concentration: 0.2 to 0.4 mg/l as residual chlorine
- Injection time: 1 to 3 hour per 24 hours
(17/17)
Thank you for your kind attention.