h1. Secondary Experiments
h2. Procedure
{float:right|border=2px solid black}[!SandFilterSetup2.png|hspace=5,width=600px!|First Sand Filter Setup with Bubble Collector]
h5. First version of the experimental setup that included a bubble collector
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Since there were problems with the DO probes we used in the initial experimental setup, we switched to measuring the total volume of the bubbles that form inside the filter column. Using _MathCad_, we used the bubble volume collected to calculate the equivalent DO concentration removed from the water.
The only changes in the setup were to remove the DO probes and instead feed the water leaving the filter column into an inverted graduated cylinder. This cylinder was filled with water at the start of each run and had its mouth submerged in water. As bubbles formed in the filter media, they flowed out into this cylinder and floated to the top, displacing some water and causing the water level inside the cylinder to fall. The air volume was measured every 10 minutes during each run, using the calibrations on the side of the cylinder.
We also tried a new method of testing the quality of the effluent water, using sugar. The sugar test involved collecting the outflowing water in a clear beaker or cylinder and adding some sugar. As the sugar dissolved in the water, if tiny gas bubbles were seen floating to the surface, the water is still super-saturated with gas and our filter method did not work. If no bubbles were seen, then the water was no longer super-saturated, and it could be assumed that the gases were removed.
h2. Results
The first experiment run using this bubble collection method used glass beads as the filter media, with a flow rate of 200 ml/min and an unsuspended filter depth of 32 cm. We observed that the performance of the system increased for about 20 minutes, after which the rate of the increase in air volume became relatively constant. These results are illustrated in [#Figure 1]. After 20 minutes, the line becomes nearly linear. We concluded that the experiment needs run for at least 20 minutes in order for the data to become steady and reliable, and that we would start recording data after at least 20 minutes of runtime. For the data file for [#Figure 1], click [here|First Results using a Bubble Collector^Data file for Figure 1.xls]
Next, we experimented with the glass bead depth. At a flow rate of 200 mL/min, obtaining the results shown in [#Figure 2]. [#Figure 2] illustrates that a glass bead depth of 10cm would work better than the larger glass bead depth of 32cm. For the data file for [#Figure 2], click [here|First Results using a Bubble Collector^Data file for Figure 2.xls]
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!BubbleVol vs. Time, 200mLmin.png|width=500px!
h5. Figure 1: total bubble volume collected over time with a flow rate of 200 ml/min and a sand depth of 32 cm.|{anchor:Figure 2}
!BubbleVol, varied depth.png|width=500px!
h5. Figure 2: the effect of varying glass bead depth at a flow rate of 200 ml/min.|
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Logically, this did not make sense, so we repeated the experiment at a later date. [#Figures 3 and 4], below, illustrate these results, showing that a larger filter depth does in fact extract more dissolved oxygen.
As shown in [#Figure 3], DO stripped from the water flowing at 150 mL/min through the 33 cm filter was much greater than at the other flow rates and depths. This was probably because the 150mL/min run was at a greater filter depth, which meant we needed to add glass beads to the column. A lot of air came in with the dry beads, and we most likely did not allow sufficient run time afterward in order to allow all the trapped air to escape before we began recording the data. By the time we ran that depth at the lower flow rate, the extra air had left and we were gathering only the air being stripped from the water.
[#Figure 4] shows the same results as [#Figure 3] but omits the 150 mL/min at 33 cm data, making the results from this run easier to see. Clearly, the greater filter depth resulted in the removal of more dissolved oxygen than the lower depth. The flow rate was not varied enough to have much impact on the effectiveness of this method. For the data file for [#Figures 3 and 4], click [here|First Results using a Bubble Collector^Data file for Figure 3 and 4.xls]
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!DO removed vs. time, fig 3.png|width=500px!
h5. Figure 3: DO concentration versus time at varying depths and flow rates.|{anchor:Figure 4}
!DO removed vs. time, fig 4.png|width=500px!
h5. Figure 4: DO concentration versus time at varying depths and flow rates. This graph is the same as Figure 3, but the results from the flow rate of 150 ml/min at 33 cm filter depth are excluded.|
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[#Figures 5 and 6], below, compare the DO removal as measured by the DO probes to our calculations using the total collected bubble volume. [#Figure 5] reveals a large discrepancy between the DO probes' data and the actual volume of water collected. [#Figure 6] shows that the DO probes were in fact recording that oxygen was _added_ to the water during the process, although the volume of air collected from the water was definitely increasing. We concluded that our DO probes were definitely not reliable.
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!DO removed, measured and calculated, 10cm.png|width=500px!
h5. Figure 5: DO removed, measured by the DO probes as well as by calculating equivalent DO using the collected bubble volume. Sand depth of 10 cm, flow rate of 200 mL/min.|{anchor:Figure 6}
!DO removed, measured and calculated, 32cm.png|width=500px!
h5. Figure 6: DO concentration removed, measured by the DO probes as well as by calculating equivalent DO using the collected bubble volume. Sand depth of 32 cm, flow rate of 200 mL/min.|
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h2. Conclusion
We have not yet drawn any final conclusions. The data collected was not reliable or stable, due to many problems, such as the DO probes not reading the concentration correctly. WeThe sugar test was performed after several runs, but the results varied greatly, even when performed on multiple effluent samples for the same run, or on tap water. Overall, the sugar test results were inconclusive.
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h2. Conclusion
From these results, we may tentatively conclude that greater filter depth removes more dissolved oxygen, but further research is necessary. However, the method of measuring and recording the volume of gas removed from the water was not precise, and it allowed for a large amount of error and inconsistency. We also cannot be sure that water entering the system was in fact supersaturated, as the temperature outside was growing warmer and varying greatly by the day. As such, we will be able to draw firmer conclusions when the problemssetup ofincludes thea setupmethod areof fixedsupersaturating andthe wewater haveand a more accurate and precise method of measuring the collected air volume.
The sugar test proved to be very inconsistent, but it may perform better if a finer sugar is used. This method requires further testing.
After this round of experiments, we altered our setup to include a new bubble collector and a chamber to make sure the water is super-saturated when entering our filter. [See the method and results here.|Current Experiments] |
