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Conference Papers | 2004 Victorian Conference Papers
MEETING
WHO GUIDELINES FOR DRINKING WATER QUALITY AFTER THE
2003 BUSHFIRES IN NORTH EAST VICTORIA
Bruce
Tyler, Treatment
Plant Operator,
North East Water
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ABSTRACT
January
2003 saw some of the worst bushfires ever experienced
in the North East of the State. The fires burnt for
more than a month and burnt out an area of 1.1 million
hectares. These fires caused major concerns for Authority
staff in our Alpine region when the demand for water
rose by up to five times normal consumption in some
towns as people went about trying to protect their properties.
On top of this our staff also had to protect our pump
stations and treatment facilities so water would continue
to flow into the reticulation system.
Staff
members from other regions in the Authority were called
in to assist in running a 24-hour roster, which was
maintained for a few days until the threat had past.
Once the flames were gone and we were left with a smoky
haze and a charred landscape, our troubles were not
all gone.
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1: Charred bushland near Beechworth |
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Figure
2: Smoke haze over Wodonga's Huons Hill WTP |
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KEY
WORDS
2003
Bushfires, World Health Organisation (WHO) Guidelines,
turbidity, Wangaratta, Ovens River, Buckland River,
NTU.
1.0
BACKGROUND
Once
the main threat of fire had passed, we had a meeting
to debrief on events to date. The aim of the meeting
was to discuss how we would approach the problems that
we were likely to experience after rainfall caused run-off
consisting of silt, saps and eucalyptus oils into the
rivers that we draw from. Our discussions covered all
the towns in the Alpine area, and also Wangaratta as
it draws from the Ovens River approximately 100 km downstream
from the Buckland River junction. The main concern was
whether we would have enough storage to see the dirty
water flow past our offtakes. Some towns such as Corryong
have significant storage capacity and were not considered
to be an immediate concern. Wangaratta, however has
only eight hours' supply capacity during summer.
We
discussed the option of carting water to the smaller
towns, but this was not practical for Wangaratta, which
uses around 35ML per day at that time of the year. We
made tentative plans for all towns and it was expected
that by the time the dirty water travelled 100 km downstream
it would have settled out to a reasonable quality so
it could be treated at Wangaratta. Operators at the
Wangaratta plant doubted the slug would settle out totally
as they had experienced some runoff water from a controlled
burnoff in Morgans Creek catchment just above Bright
back in November 2002 after a localised storm. On that
occasion the water that ran into the Ovens River was
quite dirty and had a turbidity of 100 NTU when it got
to Wangaratta.
2.0 THE PROCESS OF WATER TREATMENT AT WANGARATTA
Fortunately
the Wangaratta Treatment Plant consists of two plants,
a conventional Upflow Clarifier Plant that has pressure
sand filters. In 1983, to keep up with demand in the
summer, a Direct Filtration Plant was built. When the
dirty water from the controlled burnoff arrived, two
of the pressure filters were offline and the Direct
Filtration Plant was in use. However as it can only
handle water up to 30 NTU, it was decided to investigate
running through the clarifiers and then into the Direct
Filtration Plant to filter the water. Operator Brian
Scobie believed this was possible, so he set about opening
and closing valves that were rarely used. After some
time he had achieved this and then had to adjust the
valves to control the flow. The plant was run like this
for several days
3.0 A ONE-IN-FIVE-HUNDRED-YEAR
STORM
3.1
Wednesday
I
don't think anyone could have predicted what happened
when it did rain.
It
is well documented that on 26 February 2003 a microstorm
dumped 150mm of rain over a 10 to 15sq km area in 20
minutes. Sadly one firefighter lost her life as she
was washed away by a wall of water about 2m high flowing
down Dingo Creek at an estimated speed of 25km/h. The
runoff carried everything on the ground with it and
devastated the river banks and any structure in its
path. Early reports had readings that the wall of water
in the Buckland River was as high as 3m.
3.2
Thursday
On
27 February, we received a call to inform us that the
storm had raised the turbidity to 129,000 NTU and that
the river looked more like syrup than water. We quickly
headed up the river to find the front of dirty water
and collect samples so we could conduct some early jar
tests to see if or how we could treat it. The turbidity
of the samples ranged from 40,000 NTU to 70,000 NTU.
Preliminary tests proved that if we used Megapac 23
instead of Aluminium Sulphate that we could treat up
to 16,000 NTU. The next important questions were when
the front would arrive in Wangaratta and how long it
would take to pass.
We
had discussions with North East Catchment Management
Authority and Goulburn Murray Water. Their predictions
were that the dirty water front would arrive either
late on the evening of Thursday 27 February or early
on Friday the 28 February.
After
travelling up and down the river collecting samples
our prediction was that, with no large flows in the
Ovens River to push the front on, we wouldn't see this
slug of dirty water for a few days. Nevertheless we
staffed the plant all night to monitor the river in
case our prediction was wrong.
3.3
Friday
Friday
morning came and the water quality was still OK in Wangaratta.
The main front had reached Whorouly, about 75 km up
river. This meant we needed to get a tank and a delivery
of Megapac 23 on site so that when the dirty water arrived
we would be able to treat it, as long as it wasn't more
than 16,000 NTU. We contacted our chemical supplier,
Omega Chemicals, and they were able to arrange a tank
container with 10,000 litres of Megapac 23 for first
thing on Saturday 29 February.
3.4
A Working Weekend
Over
the weekend we continued monitoring the river and testing
with different polymers to see if we could find one
that worked better. We found that the poly we use on
our DF plant was the best. We also began testing for
manganese and alkalinity, and found that these were
very hard to determine as we couldn't pick a colour
change, and diluting with deionised water on the alkalinity
test affects the test significantly. We set about putting
an injection point into our clarifier plant as it didn't
currently use poly, and we also had to connect our Megapac
tank into our dosing pump lines.
These
works were done, and then our electrical department
set the plant up to run our dosing pumps and flow pacing
up off the one flow meter. This took some time and they
tried several combinations before it worked correctly.
As is usually the case with electronics, when you make
a change it causes a problem somewhere else.
Figure
3: River Turbidity Levels in the Ovens & Buckland
Rivers Following the Microstorm

3.5
Wednesday
It
was now decided that the main front of dirty water would
arrive on about Thursday 6 or Friday 7 March. Over the
next few days we continued jar testing and monitoring
the river and the steady decline in the turbidity as
the slug travelled downstream towards Wangaratta. By
Wednesday the front was down to 1,000 NTU and just a
bit further up the river was 5,000 NTU. Conversely,
the turbidity at Wangaratta was steady and likely to
increase in the next 24 hours; our best prediction was
that the dirtiest water we would get was in the range
of 2,000 to 4,000 NTU. We concentrated our jar tests
on this range and were quite pleased with the results
- we believed we would be able to produce water at a
quality similar to normal operation.
Figure
4: Decrease in Peak Turbidity as Dirty Water Passed
Down Ovens River 26.2.03 - 11.3.03

3.6
Thursday
On
Thursday 6 March we drained the alum dosing lines and
flushed them out before changing to Megapac 23 and beginning
with the poly dosing. At this point the raw water quality
was:

We
found that the only way we could calculate the dosage
of Megapac was to use a ppm volume / volume formula
as opposed to a mg/lweight per volume formula.
3.7
Friday 7 March 2003 - The Big Day
On
Friday 7 March, the dirty water finally arrived. At
7.30am the turbidity was 437 NTU and rising rapidly.
Previously we had decided to run the plant at 210 L/s.
We soon noticed our storage levels were decreasing rapidly,
so after some discussion we decided to increase the
flow through the plant to 260 L/s to try to keep up
with the demand. This went well and everything appeared
to be going to plan. We were conducting regular jar
tests, and were taking a treated water sample out of
the inlet pipe and seeing how well it would floc and
settle.
Figure
5: Treatment Team Contemplates Pptions with the Turbid
Ovens River in the Background

At
12 noon, a routine inspection of the clarifier showed
it looked terrible; the sludge blanket had lifted up
almost into the launder troughs. By the time I got back
into the lab the settled turbidity had jumped from 0.7
NTU to 25 NTU and we had no choice but to shut the plant
off until we could work out what caused the problem.
Turbidity tests from the top of the clarifier were around
100 NTU and there were many tiny dead fish floating
around. There was also a white frothy substance floating
on the top of the cells in the Direct Filtration Plant.
Immediately
we contacted our Treatment Technologist, Mark Samblebe
and he arrived at 1.30pm to assist us to find a solution.
During the afternoon we contacted the Operations Manager,
Bruce Gardiner, Technical Services Manager, Don Jackson,
and Chief Executive, Jim Martin, who set about implementing
our emergency response procedure upon their arrival
at the plant. This involved contacting the council,
police and media, all of whom responded positively and
assisted where possible. TV and radio stations were
asked to arrange broadcasts to advise of emergency stage
four restrictions effective immediately to lower consumption.
We believed that if consumption continued at the existing
rate, Wangaratta would have run out of water by midnight.
To alleviate community concerns, we tankered water from
Benalla to the Wangaratta storages, and set up a tanker
to supply drinking water to the public at Bachelors
Green.
Goulburn
Valley Water provided their water quality specialist
who has experience with a similar upflow clarifier plant.
By Friday evening the turbidity was 1400 NTU and we
had worked out the right dose rates and believed that
the plant could produce water of acceptable quality.
However we believed we would have to run the plant and
dump the water back into the river until the turbidity
at the top of the clarifiers was at an acceptable level
to put it through the Direct Filtration Plant.
We
restarted the plant at 11pm, and it was 5am before water
was running into our very low storages.

Figure
6: Turbidity and Dose Rates at Wangaratta

3.8
The Labor Day Long Weekend to Remember
The
following Saturday morning dawned and the nightshift
operator was happy to be relieved. The dayshift continued
with the regular jar tests and half-hourly treated water
tests as the turbidity was continuing to rise and we
didn't want a repeat of the previous day's incident.
Things were going well. Then the media invaded: three
metropolitan TV stations and two local newspapers who
wanted to take shots and footage in the lab and outside
on top of the clarifiers. Jim Martin and Bruce Gardiner
handled most of their questions and the operators only
had to deal with a few technical questions.
The
Department of Human Services requested that we notify
them if our treated turbidity went over 1 NTU and also
to test for E.coli in a few locations around the reticulation
system. With only three operators in Wangaratta, we
only had enough staff for one per shift, so we had to
get additional staff from Benalla and our central region
to fulfil all our testing and operational requirements.
We continued to staff the plant around the clock for
the next 10 days, and then went to a split shift with
overlap from 7am to 11pm for another seven days. During
that time our turbidity peaked at 2,780 NTU and then
dropped back to a much more manageable 50 NTU about
17 days later.
We
found that even though we could treat the dirty water,
it caused a few problems along the way. We were producing
11 ML per day, and as a result we produced just over
1 ML of sludge and the plant was unable to discharge
this in the normal way.
We
tried unsuccessfully to leave the sludge cones open
manually, so we opened the disused sludge weirs. This
still didn't alleviate the excess, so we decided to
dump each clarifier out of the manual valve in the base
each morning for 10 minutes. This worked well as the
plant had usually been off for two or three hours and
we could manage the rest of the sludge through the cones.
On
Sunday evening our jar tests showed that the higher
the pH at the start of the process, the better the process
worked, so we installed another pre-dosing pump and
increased our soda ash dose by 10 mg/L to 20 mg/L and
then adjusted our post-dosing accordingly. We also were
experiencing a continual decline in our chlorine residual,
and were constantly having to raise our dose rate to
compensate for manganese consuming the chlorine. One
of the major industries in town uses about 4 ML/day
and they experienced problems with their process that
they believe was caused by high manganese levels. As
a result they had to use different chemicals in their
bleaching process.
4.0
PUBLIC PERCEPTION
This
is an interesting area. We found that the public responded
well to the forced restrictions. They did, however,
feel that our notification process when we lifted restrictions
wasn't handled as well as it could have been. We experienced
problems with the logistics involved in mailing out
the information. Our contractor acted professionally
in meeting our deadlines, but because restriction levels
were changing so rapidly, there were often unavoidable
conflicts between the written information residents
received, and what was being broadcast in the electronic
media. The confusion was caused partly by operators
notifying management that we could increase the flow
through the plant as the turbidity levels decreased,
and unavoidable delays in passing this quickly changing
information to the public.
The
other area of public concern was the water's taste and
odour. Unfortunately we were unable to do anything about
this. Most of the feedback we received was positive
as people could see what was flowing down the river
and appreciated having clean disinfected water to use
throughout the house, even if it had a smoky taste to
it.
5.0
CONCLUSION
There
is no doubt that all levels throughout the Authority
gained a considerable amount of knowledge from the fires
and the events that followed. We found that our emergency
response procedure worked well, although it needs to
be addressed in some areas. One of the main areas of
concern was the 24-hour rostering and communication
between staff over the first few days. However all involved
believed they benefited greatly from the experience,
which was highlighted by the teamwork and cooperation
between operators and other areas of the Authority.
Communication with the public needs to be handled better
and this has been looked at by management.
The
Wangaratta operators used the experience gained from
this event six weeks later when, on the Easter weekend
after more rain, the river turbidity peaked at 2,870
NTU. On Good Friday at around 1,000 NTU the plant experienced
the same process problems.
The demand at this time wasn't as high, but the storages
dropped to a similar level as in March. As we knew what
to do, we didn't have the same panic and fuss as previously.
The
incident was managed well and the processes followed
have been documented for future reference, although
we hope we never have to use them again.
6.0
ACKNOWLEDGEMENTS
The
author would like to thank authority staff from the
following areas: Wodonga and Benalla treatment staff;
Wangaratta treatment and distribution staff; Western
Treatment Coordinator, Rex Humphreys; Treatment Technologist,
Mark Samblebe; university placement staff Brooke Anderson
and Elise Ring; senior management; and Goulburn Valley
Water for their help with staff. Without the assistance
of all these people we would not have been able to get
through a very difficult few weeks.
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