Sg Selangor Phase 2 Water
Supply Scheme (SSP2) was implemented on
a Build-Operate-Transfer (BOT) basis. The
construction Cum Operation Agreement (CCOA)
to design, finance, construct, operate,
maintain and manage a new Water Treatment
Plant (WTP) was signed between the Selangor
State Government and Puncak Niaga (M) Sdn
Bhd on 22 March 1995 and the concession
period is up to 31 December 2020.
The construction of the SSP2 was carried
out in two stages, with a full design capacity
of 950 million litres per day (mld). Construction
of Stage 1 with design capacity of 450 mld
commenced in March 1996 and was originally
scheduled for completion in December 1998.
However, the construction of the WTP was
accelerated for partial commissioning on
14 July 1998 as one of the measures taken
to alleviate the water crisis experienced
in the Klang Valley during the month of
March to July 1998. Construction of the
Stage 2 WTP Works commenced in 1998 and
completed in December 2000. With this completion,
the SSP2 WTP is officially completed and
capable of producing 950 mld commencing
on January 2001.
In meeting its obligation to successfully
complete the project, Puncak Niaga has raised
the single largest water supply infrastructure
project financing totaling RM1.28 billion
on a non-resources basis by domestic financial
institutions.
The Sungai Selangor Phase 2 WTPabstracts
water from the Sungai Selangor. The raw
water Intake is located near the town of
Batang Berjuntai.
On the whole the raw water are treatable
and this is despite occasional high turbidity
spikes experienced after heavy downpour.
The Sungai Selangor at the point of intake
near Batang Berjuntai has a big open catchment
upstream, and inevitably there are industrial
and development activities within the vast
catchment upstream of intake point.
Raw Water Monitoring System (RWMS) has
been installed upstream of the Intake to
continuously monitor raw water quality.
The RWMS works by transmitting selected
raw water quality parameters to the WTP.
Any severe violation of raw water quality
will be detected and early preventive measures
can be taken.
Once the water leave the Raw Water Pumping
Station (RWPS), it travels over 4 Km through
a 2100mm dia pipes where it enters the plant
at the aerator. The aerator provided at
the plant is the horizontal cascaded typed
and it’s function is to :
i. Remove Taste and Odor
Tastes and odors in raw water evaporate
readily and are released into the atmosphere
by exposing as much water surface to the
atmosphere as possible and introducing turbulence
via the cascaded aerator.
ii. Oxidise Iron and Manganese
Completely dissolved iron and manganese,
when exposed to air will be oxidised and
become particles which can easily be removed
via coagulation / flocculation / settling.
By gravity, water leaves the aerator and
travels to the flow splitter through two
separate pipes. In the splitter, water is
divided equally into five (5) separate flows
by means of simple weirs.
At each overflow weir, lime is added for
pH control and alum as coagulant. Polymer
is also added as a coagulant aid to bind
the floc. Apart from making it larger and
heavier, it makes the floc more durable
and less likely to break during the flocculation
process. Microsand is added in the coagulation/
flocculation process to hasten the settling
of flocs which requires a small sedimentation
basin.
Chlorine is dosed at the filtered water
as a disinfectant to control any pathogenic
organisms in the water before it is supplied
to consumers. Fluoride is also dosed at
the treated water to prevent tooth decay.
Finaly the treated water pH is adjusted
at the outlet of contact tank by adding
lime.
The water clarification process is by
means of Actiflo-Settler, a compact unit
with a high degree of operating flexibility.
It uses microsand as the catalyst to expedite
the clarification process with facilities
to recover the sand used. This system enables
the clarification process to be reduced
to 21 minutes from point of coagulation
to outlet of the settling tank.
The purpose of coagulation/flocculation/settling
is to remove particulate impurities, especially
non-settleable solids (colloids). This process
is carried out in 4 steps.
i. Flash Mixing/Coagulation Tank
Raw water with added lime and alum coagulant
enters the coagulation tanks and rapid mixing
is introduced to ensure that the chemicals
are evenly dispersed in the water as quickly
as possible. Chemical reaction takes place
and flocs are formed. However, the flocs
formed are relatively light and small.
ii. Injection Tank
Microsand with an average particle size
of 85 µm and a specific gravity of
2.3, is continuously injected along with
polymer and becomes entrapped in the floc
making the floc substantially heavier as
well as more resistant to breaking up in
the flocculation process.
iii. Flocculation Tank
Gentle mixing is introduced in this tank
to increase the frequency of collision between
floc particles, making them attach to one
another thereby becoming larger and heavier.
This will allow them to settle out at a
much faster rate thereby requiring a much
smaller settling tank. The water then leaves
the flocculation basin and enters the sedimentation
basin to undergo further treatment
iv. Sedimentation
After the floc has been developed to an
acceptable level, it is allowed to settle
out. To improve the efficiency of the sedimentation
process, lamella settlers are incorporated.
As the water leaves the flocculation basin,
it is directed to the sedimentation basin
and underneath the lamella settlers which
are placed at an inclination of 60 degrees.
The heavier floc settles to the bottom while
the lighter floc is carried with the upward
flow of the water through the lamellas.
The rising floc becomes attached to the
walls of the lamellas and this build up
eventually becomes heavy enough to slide
down the lamellas and settles to the bottom
of the sedimentation tank.
Sand filtration is the last stage of clarification.The
filter media is composed of 100 mm gravel
with an effective size of 2 - 4 mm at the
bottom layer whilst the upper layer is 900
mm of sand with an effective size of 0.8
- 0.95 mm.
From the settling basin, settled water
is fed to the rapid gravity filters. The
water flows downward through the sand and
gravel, removing much of the remaining turbidity
in the process and it eventually ends up
in the filter underdrain and subsequently
flows into the clear water tank.
Filters are back washed by reversing the
flow of air and water. A computer automatically
regulates the order in which filters are
washed based on a head loss of 2.4m or per
set runtime.
Filtered water is then transferred to
the holding tank before being pumped to
Balancing Reservoirs through 2.1 m diameter
pipeline for distribution to consumers. |