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| Potsdam WWTW -
Upgrade & Extension |
| Newsletter No
3 - November 2008 |
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Introduction |
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The Potsdam Wastewater Treatment Works (WWTW) has
been undergoing an upgrade from 32 mega litres per
day (Mℓ/d) to 47 Mℓ/d. Currently the Plant is
receiving an annual average of approximately 37 Mℓ
of wastewater daily. Construction began towards the
end of 2004 and is scheduled to be completed towards
the middle of 2009. |
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In light of the keen
public interest attached
to this project, both
during the Environmental
Impact Assessment (EIA)
process and since the
initiation of
construction, the first
two Potsdam Newsletters
were circulated in March
2006 and November 2007
to update the I&APs of
the project’s progress.
This third publication
aims to build on its
predecessors and serves
as a further update on
the remaining
development of the
project. |
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General |
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The upgrading and extension of the Potsdam WWTW
comprises decommissioning the biofilter plant of
15Mℓ and extending the plant capacity to 47 Mℓ/d.
The upgrade of the WWTW will result in a much
improved effluent quality to meet the standard
requirements set by the Department of Water Affairs
and Forestry (DWAF). |
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The 8 Mℓ interim capacity plant which was
commissioned in August 2007, to alleviated
dependency on the existing biofilter plant and allow
developments to continue, is no longer in use as the
30 Mℓ extension has been in operation since April
2008. Phase II of the main extension, which includes
the bioreactor, various pumpstations, primary and
secondary settling tanks, odour control and
dewatering facilities, is now nearing completion. |
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30 Mℓ Plant Extension and
Upgrade to Treatment Works |
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The raw sewage is split between the old (1997) 17
Mℓ/d plant and the new 30 Mℓ,/d plant. The new raw
sewage pumpstation pumps the raw sewage to the 3
newly constructed primary settling tanks. The
settled primary sludge from the settling tanks is
pumped via the primary sludge pumpstation to the
sludge holding tanks before it is dewatered and sent
for composting or disposed of to a landfill site.
The overflow from the primary settling tanks is
discharge to the bioreactor. The newly constructed
bioreactor consists of two identical streams each
with a capacity of 15 Mℓ/d. The outflow from the
bioreactor is settled in secondary settling tanks to
separate the treated wastewater from the biomass
solids. The underflow is returned to the beginning
of the bioreactor as it contains organisms which are
responsible for removing impurities from the
wastewater. The treated overflow is discharged
through a series of maturation ponds before it
undergoes UV disinfection and either re-used or
discharged to the Diep River. |
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The tanks, which were used for
the interim 8Mℓ/d capacity, as
discussed above, have now been
modified to operate as aerobic
digester tanks. A certain
quantity of sludge which is
periodically removed from the
bioreactor is thickened and with
the use of oxygen further
biologically degraded. This
procedure is to ensure that the
dewatered sludge meets
beneficial re-use requirements.
The commissioning of these tanks
is under way. |
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The main extension has been
operating in the manner
described in the first paragraph
since April 2008. The biofilter
plant has since been
decommissioned. However, there
is still construction work in
progress on site. The sludge
dewatering capacity of Potsdam
is currently being further
upgraded in order to accommodate
the increased requirement for
solids dewatering. |
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Figure 1: Interim capacity prior
to conversion |
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Furthermore, the construction of
the inlet works is currently
underway. The new inlet works
will provide for the increase in
treatment capacity and improve
the primary treatment of sewage
which involves screening and
grit removal. Screening is the
removal of obtrusive objects
which may damage equipment or
lead to blockages. Efficient
grit removal is necessary to
prevent mechanical equipment
downstream of the inlet works
from being damaged. |
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The extension of the odour
control units on site is also
underway (discussed in greater
detail below). New odour control
units will be provided at the
new raw sewage pumpstation and
the new and old primary settling
tanks which are in general the
main sources of odour at
wastewater treatment works. |
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Odour Control |
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The importance of mitigating odours at Wastewater
Treatment Works has increased over the past few
years due to the City’s commitment to good
environmental practice. Historically odours from
wastewater treatment were relatively unnoticed but
due to the rapid increase in urbanisation the buffer
zone (500m) surrounding the treatment site has
virtually vanished. |
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The Potsdam Works was the first
WWTW in the City to install the
Biocube technology at its
Tableview East pump station for
the treatment of odours.
Specialist advice was sought
from America before the
technology was installed at a
cost of approximately R1.6
million. The unit has
demonstrated that it can
consistently remove hydrogen
sulphide (H2S) up to 99.5%. The
odour is treated biologically
instead of with strong oxidising
chemicals, making it more
environmentally friendly. The
unit requires very little
operator attention and
maintenance is minimal. This
form of treatment will be rolled
out to treat odours from various
locations on the site for odour
minimisation. |
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UV Disinfection |
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The Potsdam WWTW was essentially
the pioneer for this technology
in the Western Cape as it is
only the second such
installation in the country. The
only other such installation is
at the Daspoort WWTW in Tswane.
The choice of the technology was
based primarily on the fact that
it is the more environmentally
friendly in that it is not a
major hazardous installation and
it does not produce potentially
harmful by-products. |
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Although the UV disinfection
unit at Potsdam was commissioned
in 2006, it could not meet the
required disinfection rate until
the Biofilters were taken out of
commission in June 2008 (when
the new activated sludge plant
capacity was in operation). This
was because the Biofilter
effluent could not meet the
transmissivity specification.
June 2008 marked the first time
since in the history of the
operation of the Potsdam WWTW
that all the effluent discharged
from it complied with the DWAF
legislation. |
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Single Discharge Point |
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The two sets of maturation ponds both discharged
upstream of the Diep River / Rietvlei confluence. To
minimise the negative impact that the effluent may
have on the wetland, the maturation flow pattern was
re-arranged so that the two separate process streams
are combined before the UV disinfection unit and
discharged into a final holding pond before
overflowing to the Diep River by-pass channel. |
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Increase Re-use of Effluent |
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Before the extension, the Works supplied
institutions and industries such as Century City,
Caltex, SAPPI, golf courses and several schools with
treated effluent for industrial and irrigation
purposes. This accounted for 30% of the summer flow
that would otherwise be discharged to the Diep
River. Most of the re-use water was abstracted from
the Biofilter plant’s maturation ponds which meant
that some of the customers were not always happy
with the water quality and had to treat it further
on their premises. |
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The construction of the De
Grendel reservoir and the 800mm
supply pipeline built by the
Reticulation Branch has extended
the re-use capacity to supply
several more customers,
including farmers in the
Durbanville area. Recent (2008)
figures indicate that a weekly
average of up to 76% of the
effluent can be re-used in dry
weather. With the new activated
sludge reactors now on-line, an
improved water quality will be
supplied to the City’s
customers. |
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Standby Generation |
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The national electricity crisis has emphasised the
need to have contingency plans in place to minimise
and prevent environmental pollution as a result of
sewage spills or sub standard effluent quality.
Previously, the major pump station (Koeberg) feeding
the Works did not have standby generation and in the
event of a long power outage, the raw sewage will
overflow and dicharge into the Diep River as part of
the storm water system. The on-site pump station
(Tableview East) was also without any back up. Both
of these pump stations are now equipped with standby
generation so that the risk of raw sewage overflow
to the Diep River System in minimised. |
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With the Potsdam upgrade standby
generation has been installed to
operate other critical process
units including the raw sewage
pump station and the UV
disinfection unit. |
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New Activated Sludge Reactors |
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The continued operation of the Biofilters, which
treated approximately half of the influent to the
Works, was the major reason of the non-compliance of
the treated effluent. They had to be replaced with
more suitable treatment facilities. The two new
Bioreactors are designed to biologically remove
phosphorous and can each treat up to 15 Mℓ/d. This
has essentially given the Works increased treatment
capacity, up to 47 Mℓ/d. The flow diversion has now
alleviated some of the load onto the older activated
sludge plant, which has also shown some performance
improvement. |
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Effluent Quality |
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Tables 1 and 2 summarise the average performance of
the Bioftiler Plant and the Activated Sludge Plants
(ASP) respectively. |
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Table 1: Average performance of
Biofilter Plant from Jan 01 –
Apr 06 |
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Biofilter Plant |
Effluent standard
requirement |
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Average |
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COD |
mgCOD/ℓ |
91 |
<75 |
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Ammonia |
mgN/ℓ |
11 |
<10 |
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Nitrate |
mgN/ℓ |
5.0 |
<15 |
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Phosphate |
mgP/ℓ |
6.0 |
<1.0 |
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Total Suspended Solids |
mgTSS/ℓ |
23 |
<25 |
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E.coli |
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3.1x105 |
<1.0x103 |
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It is clear from Table 1 that
the effluent quality produced by
the biofilters prior to the
treatment works upgrade did not
meet the effluent standard
requirements. |
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Table 2 indicates a notable
improvement in the effluent
quality produced by the 30 Mℓ
ASP extension – which replaced
the Biofilter Plant. |
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Table 2: Average performance of
the ASP 97 and ASP 08 |
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ASP 97 |
ASP 08 |
Effluent standard
requirement |
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Sampling Period |
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Jan 07 - Nov 08 |
May 08 - Nov 08 |
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Average |
Average |
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COD |
mgCOD/ℓ |
58 |
44 |
<75 |
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Ammonia |
mgN/ℓ |
1.6 |
0.3 |
<10 |
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Nitrate |
mgN/ℓ |
3.3 |
3.7 |
<15 |
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Phosphate |
mgP/ℓ |
1.8 |
3.4 |
<1.0 |
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Total Suspended Solids |
mgTSS/ℓ |
17 |
13 |
<25 |
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The major public concern over
the past few years has been the
high E.coli levels in
Milnerton Lagoon which is used
heavily for recreational
purposes. A graph in the print
version of this newsletter shows
the 4 stages of the construction
period (2004 to present) in
relation to the E.coli
concentrations. The E.coli
levels during Stage IV (June to
November 2008) show a definite
improvement over Stage III. |
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The new acitivated sludge plant
was optimised and is performing
very well in terms of meeting
the phosphate requirement.
However, there is a slight
increase in Phosphate during the
effluent passage through the
maturation ponds which sometimes
causes the combined final
effluent to just tip over the 1
mgP/ℓ mark. |
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On going forward, we have to pay
close attention to the Stage IV
monitoring of the E.coli
and phosphate concentrations in
particular. |
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Budget |
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The project is now in its 6th financial year with a
total of R235.77million of the budget having been
spent thus far. This represents 82.65% of the total
budget available for the project. |
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There are a number of contracts currently in
preparation that will further upgrade the Works as
follows: |
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The construction of a new
dewatering plant to increase the
sludge handling capacity of the
plant. |
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The construction of a new inlet
works to increase and improve
the screening process. |
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The installation of odour
control measures as part of the
current main extension contract. |
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Environmental Considerations |
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The Record of Decision issued by the Department of
Environmental Affairs and Development Planning
(DEA&DP) attached various conditions to the
authorisation. Most importantly, the City of Cape
Town was required to keep Interested and Affected
Parties (I&APs) informed by constituting an
Environmental Monitoring Committee (EMC) and to
develop and implement an Environmental Management
Plan (EMP) for the construction phase. |
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The Potsdam EMC was constituted
in July 2004, and comprises the
following: |
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City of Cape Town; |
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Ward Councillors; |
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Friends of Rietvlei; |
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Table View Residents
Association; |
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Milnerton Residents Association; |
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Milnerton Ridge Residents
Association; |
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Parklands Homeowners
Association; |
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Wildlife and Environment Society
of South Africa; |
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Representative for developers; |
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Representative for effluent
re-users; |
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DEA&DP; |
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The Department of Water Affairs
and Forestry (DWAF); and |
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The Environmental Control
Officer (ECO), who also acts as
Chair and fulfils the
secretarial functions of the
EMC. |
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The role of the EMC is to
monitor and report to the City
of Cape Town, DEA&DP, DWAF and
their organisational
constituents on the construction
activities associated with the
upgrading and extension of the
Potsdam WWTW, in terms of the
environmental requirements set
in the Record of Decision and
the EMP. Since its constitution,
the EMC has held 18 meetings,
the frequency of which has been
dictated by the EMC members. |
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As per the requirements of the
Record of Decision, an EMP was
compiled and approved by the
DEA&DP. The EMP takes the form
of a series of environmental
specifications that are
integrated into Tender
Documentation for each contract. |
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ANA were appointed as the
Environmental Control Officer
(ECO) for the construction
phase, and are responsible for
monitoring day-to-day compliance
by the various Contractors with
the requirements of the EMP. The
ECO reports on a monthly basis
to the City of Cape Town, the
EMC and DEA&DP. As per the
requirements of the Record of
Decision and good practice, the
ECO and EMC will continue to
monitor compliance with the
environmental requirements. |
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[ANA is a joint venture
comprised of ASCH, Ninham Shand
and Africon. Tinka Shapiro and
Alec Lambert from the Ninham
Shand Environmental Discipline
Group are acting as the ECO.] |
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The Way Forward |
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The Phase II Main Extension of the Potsdam WWTW is
nearing completion (expected completion date is
mid-2009). |
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I&APs will be kept informed on a
quarterly basis by projects
newsletters issued by the City
of Cape Town. However, should
more frequent or detail
information be required, I&APs
should feel free to contact
their representatives on the EMC
or the ECO (Michael Mangnall or
Tinka Shapiro Tel: (021) 481
2400, Email:
enviro@shands.co.za). |
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Click
here to view Newsletter No 2 - November
2007 |
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