Versions Compared

Key

  • This line was added.
  • This line was removed.
  • Formatting was changed.
Comment: Migration of unmigrated content due to installation of a new plugin

Dissolved Air Flotation of Flocs

Overview

Wiki Markup
h1. Floating Flocs


h2. Overview

{float:rightleft|border=2px solid black|width=200px}
[!floating -floc-edit.jpg|width=200px!|Dissolved Air Flotation of Flocs]
{float}
Rising flocs in the sedimentation tanks have been a problem from the very beginning at the plant in Tamara. The plant in Ojojona is also having this issue but to a lesser degree. Initially the rising of the floc was thought to be caused by alum overdosing but the problem persisted even after the dosage was changed. The speed with which the floc particles rise in the tank suggests that air bubbles are lifting them to the surface. Some water treatment facilities purposely make the flocs rise to the surface as a way to remove particles in the water but since the Tamara and Ojojona plants are designed to have the flocs settle out at the bottom of the sedimentation tanks the layer of particles at the surface of the tank pollutes the effluent.

\\
{float:left|border=2px solid black|width=250px}
[!sludgeTop.jpg|width=250px!|Dissolved Air Flotation of Flocs]
{float}
Gas bubbles can form in a solution of water when the total dissolved gas pressure is greater than the local solution pressure. Very high rates of mixing can cause the pressure to drop below that of the atmosphere, creating a negative local gauge pressure. This decrease in pressure causes more gas to enter as the total dissolved gas pressure is again greater than the local water pressure. There is a lot of water turbulence at the entrance of the Tamara water treatment plant because of influent's high velocity. The churning in the grit chamber could behave like a very high rate rapid mixer and thus significantly increase the amount of gas in the water. Another possible reason for the high oxygen content of the water is the transmission line leading from the mountain stream in Tamara to the treatment plant. There are some breaks in the line that allow air into the transmission line; this air-water combination then goes through regions of high pressure causing the air to be infused into the water.  Different methods of reducing this influx of gas into the water or to take it out at the plant are being researched. The hope is that decreasing the amount of gas in the water at the beginning of the water treatment process will solve the problem of rising floc in the sedimentation tanks.

A procedure is needed that will either prevent supersaturation of air in the transmission line or a method to remove dissolved oxygen prior to sedimentation to increase the effectiveness of the water treatment plant.

h2. Objectives

Floating Floc Team [Detailed Task List|Floating Floc Goals]
Floating Floc Team [Meeting Minutes|Floating Floc Meeting Minutes]

h2. Research Areas

One method used in the lab to get gases out of water is to aerate the water before it enters the system. This process requires a large amount of air to be pumped into the system, causing many little bubbles. The addition of more small bubbles to the system increases the rate of gas transfer. The gas in the water will then rise to the surface more rapidly. The contact time between the air and the water required to allow all or most of the gas to rise out of the water would thus be decreased.

The method of aeration for gas removal would require a high flow rate of air to be injected into the water. Pumps for getting air into the water are impractical to use in the Honduras towns that have AguaClara designed water treatment are not sustainable. Instead, the properties of gases and liquids can be used to create a sustainable method for infusing the water with small bubbles.

Henry's Law states:
At a constant temperature, the amount of a given gas dissolved in a given type and volume of liquid is directly proportional to the partial pressure of that gas in equilibrium with that liquid.

Henry's Law can be utilized to pump air into the beginning of the system. A small hole in the pipe headed to the grit chamber at a point where the water is in free fall would create a pressure difference between the inside of the pipe and the atmosphere thus causing an influx of air. Henry's Law can then be applied to calculate the flow rate of air into the water. The density and velocity of the water after passing this hole can then be calculated. A time estimate for the amount of contact time between the atmosphere and water that is needed for all or most of the gas to leave the water can be calculated from those values.

A model of this process is being derived for the AguaClara systems.

h2. Experimental Methods and Results

[Floating Floc Phenomenon Research|Floating Floc Research]
This page discusses the research into the floating floc phenomenon that is being conducted.

[Quiz|Floating Floc Quiz]
This quiz checks that you have a basic understanding of the principles behind this research.

h2. Additional Information

Floating Floc Team [Annotated Bibliography|Floating Floc Annotated Bibliography]=400px, height="300"!{float}

Floating flocs in the sedimentation tanks of AguaClara plants in Tamara, Ojojona, and Marcala result in polluted effluent water. While some treatment plants use floating floc to treat water, AguaClara plants rely on flocs settling out at the bottom. The floating flocs problem is thought to stem from supersaturation of influent water, which occurs when the dissolved gas pressure is greater than the local solution pressure. Because the water is supersaturated, gas bubbles naturally tend to form in order to bring the dissolved gas concentration in the water to equilibrium with the surrounding pressure. The cause floating flocs problem is thought to be bubbles forming on or attaching to flocs, lifting them to the surface.

The Dissolved Air Flotation of Flocs Team (DAFF or Floating Flocs) has been focusing on lowering the bubble forming potential of the water entering the sedimentation tank. The team was working with a backwashed sand filter using this experimental setup. We believed that providing sand as an alternative surface on which bubbles can form and rise out of the water would stop the floating flocs problem; however, research has shown that the sand used did not aid but rather inhibited gas removal. Literature regarding bubble formation, which can be found in the Floating Floc Annotated Bibliography, indicate that rough, hydrophobic surfaces are most conducive to bubble formation. The shortcoming of the fluidized sand bed method is believed to be due to the sand particles' lack of hydrophobicity.

The team's future plans include studying the effects of hydrophobic surfaces and surfactants on surface tension and bubble formation, while trying to develop a new solution to the floating floc problem. The team has been focusing on gas removal mechanisms; however, in light of the recent failure of the sand filter method, the team will also focus on possibly developing a method to stop flocs themselves from reaching the surface. Any approach developed for stopping flocs would be constrained by preventing floc break up. The team's tentative plan for future research can be found on the Floating Flocs Team's Future Challenges page.

Objective

The main objective of Dissolved Air Floating Flocs Team is to develop a physically feasible and cost-effective solution to the problem of floating flocs at AguaClara plants. The team was previously working with a backwash sand filter. However, research has shown that sand does not facilitate, but rather inhibits, bubble formation. The team plans to focus on developing a method to either remove gas from supersaturated water or stop flocs from floating to the surface even in the presence of bubbles.

Floating Flocs Team Semester Goals and Meeting Minutes
Floating Flocs Team Research Proposal
Floating Flocs Team Future Challenges

Previous Research

Previous Fluidized Bed Method Research: Links are separated by adaptations made to the system

  • Final Results from the Fluidized Bed Method
    This page contains experimental results from the final stage of the sand filter set up. It was concluded that the sand filter would not provide a suitable mechanism for gas removal, because experimental results suggest that sand seems to inhibit rather than facilitate gas removal. The main modification made to the set up from last semester was the installment of a taller pressurized aerator to increase the residence time of the bubbles in an attempt to achieve more consistent supersaturation of the influent water into the sand filter. A more detailed description of changes made to the system along with a diagram of the current setup can be viewed here.
  • Fluidized Bed after Super Saturator
    This page contains experimental results for gas removal as a function of grain size and preliminary results for gas removal as a function of sand bed depth. These are the results obtained using a pressurized aerator to super saturate the incoming water. The performance of the fluidized bed was monitored with a bubble collector. Although this technique shows great promise, the extent of supersaturation of the raw water was not necessarily held constant for the various experiments especially since the flow rates through the aerator varied.
  • Bubble Volume Measurement Method Development.
    These are the results gained from the second stage of our experimental setup, which included no DO probes and instead collected the volume of the bubbles formed in the filter in order to monitor oxygen removal rates.
  • Fluidized Bed and Dissolved Oxygen Measurements.
    These are the results gained from our initial experimental setup, which consisted of the flow accumulator with a DO probe, the glass filter column, and a collection beaker containing another DO probe.

Previous Aeration Method Research:

  • Floating Flocs Aeration Method
    This page discusses past research on the aeration approach to dissolved oxygen removal. The aeration approach attempted to use bubbles as a catalyst to increase the rate of dissolved oxygen transfer out of solution by allowing dissolved oxygen to diffuse into the bubbles. This would increase the bubble size and cause the bubble to rise faster.
  • Theoretical Modeling of Aeration Method
    This page discusses the theory behind the Aeration method and contains mathematical models predicting air flow through orifices of different sizes and variable length pipes.

Additional Information

Floating Flocs Team Annotated Bibliography

Aeration Method Quiz
This quiz checks that you have a basic understanding of the principles behind the aeration method.