Sampling and Testing Sites
All sample collection was done at the
Ketchum/Sun Valley Water and Sewer District Treatment Facility, located near
Elkhorn in Ketchum, Idaho. In the plant are a series of UV lights above a
“tray” that the raw effluent flows through. The effluent is exposed to UV light
sterilizing the effluent. Typical
pre-UV effluent has E-Coli ranging from 105-1300 MPN/100mL and Total Coliform
ranging from 1380-3970 MPN/100mL. After UV treatment the E-Coli count typically
is <1 MPN/100mL. This is the effluent that would be used for snow making at
the Sun Valley Ski Resort. Each sample was first collected in a sterile
container provided by the Treatment Facility. Control samples of effluent were
taken directly from the outflow trays in the sterilization building at the same
location within the trays that the submersible pump pulled effluent for the
snow gun. The samples were of two types. The first samples were the effluent
taken directly from the outflow trays in the effluent treatment building. The
second set of samples was from the “snow” produce during the experiment. Once
all samples were collected they were then shipped to Magic Valley Labs located
in Twin Falls, Idaho to be tested for Escherichia coli, Fecal Coliform and
Total Coliform matter in the effluent.
Snow/Effluent Production
In
order for the “effluent snow” to be collected as it would at a ski resort, in a
frozen, snow-like form, a variation of a snow gun had to be designed. The model
used was a modification of one used by Alan Pennay, a local bed and breakfast
owner in the Wood River Valley who produces his own man-made snow. Figure 1 shows the snow gun used in this
experiment. A Y-shaped nose fitting was used to in order to allow both the
effluent and air, under high pressure, to combine in a mixing chamber before
being released through the nozzle of the apparatus. In addition there was a
separate branch of the piping allowing for an effluent return system which was
used between sample collections. A submersible pump was placed within the
outflow trays to pump effluent to the snow gun. A high-pressure compressor was
used to produce pressurized air at a range of 80 psi to 100 psi, which is
consistent with those pressures used in commercial portable snow guns. Effluent
was circulated through the system prior to each test. All hoses and fittings
were flushed with a chlorine solution then clean water at the end of each
testing session. The collection curtain was sterilized with a sprayed chlorine
solution and clean water after each session as well.
Figure 1
Collecting and Testing Procedures
High-pressure air and effluent was mixed
before being ejected out of the nozzle into the freezing outside temperatures.
The snow effluent sample was captured by spraying it onto a device consisting
of a sheet of Visqueen (thin sheet of polypropylene) stapled between two pieces
of wood with a collecting basin located at the bottom of the Visqueen (Figure 2).
Figure 2
Each
sample was taken from the Visqueen collecting basin and placed into a sterile
container provided by the Treatment Facility. All of the samples were then
shipped to the lab where all of the appropriate microorganism tests were done.
Results
Table 1
Test #1 (12/21/2010)
(7 F or -14 C)
|
|||||
Sample
Type
|
Time
|
E.
Coli (MPN/100mL)
|
|||
Pre-UV
Effluent
|
8:00 AM
|
1300
|
|||
1
Pre-UV Effluent
|
9:30 AM
|
186
|
|||
1
Pre-UV Effluent Snow Sample
|
9:30 AM
|
275
|
|||
2
Post-UV Effluent
|
8:50 AM
|
<1
|
|||
2
Post-UV Effluent Snow Sample
|
8:50 AM
|
<1
|
|||
Test #2 (12/28/2010)
(17 F or -8 C)
|
|||||
Sample
Type
|
Time
|
E.
Coli (MPN/100mL)
|
Total
Coliform (MPN/100mL)
|
Fecal
Coliform (CFU/100mL)
|
|
1
Pre-UV Effluent
|
8:45 AM
|
105
|
1380
|
471
|
|
1
Pre-UV Effluent Snow Sample
|
8:50 AM
|
409
|
3970
|
498
|
|
2
Pre-UV Effluent
|
9:03 AM
|
209
|
1840
|
415
|
|
2
Pre-UV Effluent Snow Sample
|
9:04 AM
|
333
|
2590
|
6089
|
This experiment is to evaluate if the
snow making process could/would decrease the <1 MPN/100mL to an even smaller
amount. After test #1 it was determined that the lab could not test E-coli
levels below the stated value of <1 MPN/100mL and I determined that I needed
to test the bacterial levels prior to UV disinfection. Test #2 was done with
effluent prior to UV disinfection because the higher levels of E-Coli present
allowed the snow making bacterial counts to be tested. The larger number of
bacteria present prior to snowmaking would allow for a more accurate
quantitative analysis.
After all of the tests were concluded and
the data was collected a trend was seen. Unlike our hypothesis that the
combination of forcing the effluent through a high pressure and cold
temperature device would decrease the number of microbes, the opposite in fact seemed
to have occurred. In every one of the samples taken either the E. coli, total
Coliform, fecal Coliform or all of the quantities increased after going through
the snow gun. The one exception was Test #1 the Post-UV Effluent samples where
the difference in results was negligible due to it being less than 1 MPN/100mL
in both cases.
The first issue that needs to be
discussed is the large differences seen in the pre-snow gun effluent values. In
Test #2 the pre-snow gun E. coli values basically double in less than 20
minutes whereas the Total Coliform values increase almost 30% in the same
amount of time. The most likely reason for these seemingly random jumps in
values are the extreme fluctuations in microbe density going through the
treatment plant at one time. The effluent flow at the Sun Valley Sewage
Treatment Facility is usually ~1187 gallons/min. This very fast flow rate means
that the bacterial count in the water can greatly fluctuate in just a matter of
minutes.
The second issue that needs to be discussed
is why the increase in microbe activity occurred after going through the snow
gun. A study entitled “Repair of Injury Induced by Freezing Escherichia coli as Influenced by
Recovery Medium” tested the results of E. coli survival due to freezing at different
temperatures. Three of their freezing methods included Liquid nitrogen (-196
C), Dry ice-acetone (-78 C) and Ethylene glycol (-20 C). As the temperatures
they used to freeze the E. coli got colder so did the percentage of death,
~49%, ~56% and ~38% respectively, among the bacteria. This study proved that
extremely cold temperatures were able to kill/disable the E. coli bacterium,
but the temperatures that caused significant E. coli death were much colder
than are feasibly possible in normal snowmaking guns used in ski resorts.
Therefore according to this research the E. coli in our study should have had a
slight death rate due to freezing temperatures (-14 C and -8 C) when data was
collected.
An increase in not only E. coli levels
but also in Fecal Coliform and Total Coliform levels after going through the
snow gun was not expected. By vaporizing the effluent, thereby increasing the
exposure of the E-Coli to the freezing temperature and subjecting the bacteria
to high pressure, I expected some to be killed/disabled. I do not know from
this test if any bacteria were permanently “disabled”.
The process of making artificial snow
using sewer effluent did not decrease the number of E-Coli, Total Coliform or
Fecal Coliform. The results of this basic experiment validate the idea that
freezing alone doesn't kill E. Coli, cooking them is the only proper way to
decrease E. Coli density. This experiment also concluded that the extreme
fluctuation in microbe density at the testing site hindered the overall experiment.
Vaporization and high pressure didn’t seem to have any affect of the microbial
density of any of the samples.
6)
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