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Foam Filtration
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Excerpt

Numerous techniques of water filtration are in use today, most of which involve the use of sand as the porous media.

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Foam filtration, however, goes beyond traditional water treatment methods and utilizes the filtering capacity of reticulated polyurethane foam. A foam filter requires less surface area,

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treats higher turbidity water (lab results have shown pC* values of 1.5 for 100 NTU influent), wastes less water during backwash, and is less expensive to build than a traditional rapid sand filter.

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Foam filtration has been ruled out for an AguaClara plant because the foam would be too difficult for an operator to clean. However, previous research has proven that foam is an effective method of filtration, therefore this team decided to focus on designing a point of use foam filtration unit. Due to chemical dosing and usability concerns, the point-of-use application was ruled out as a possibility for foam filtration. The team then focused on the design of an emergency filtration system that can be transported on the back of a pickup truck. After speaking with communities in Honduras, it was decided that foam filtration would be more useful in small communities. Research has been done to optimize the design such that it is as efficient as possible and provides the desired standard of 1 NTU effluent water turbidity. 

Read more.

Note: Turbidity is defined as the cloudiness of a fluid caused by suspended particles. Higher turbidities correlate to more opaque fluids.

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Current & Future Research

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Excerpt

After visiting Honduras, the apparatus designed in fall 2013 was implemented with mild success. The design met the desired constraint of 1 NTU however the filter was difficult to use, especially in cleaning. The Fall 2013 team designed the foam filtration unit to fit all into one 55 gallon drum. The apparatus consisted of two 23” disks: a roughing filter that used 30 ppi* foam and a finishing filter with 90 ppi foam. The filter unit was designed on the premise of providing water for a community of 100 families at approximately 1 L/s. The Spring 2014 team updated the apparatus for easy use and transport. In order to clean this unit, a user-friendly simple pulley design with a hoist supporting approximately 500 pounds of concrete was implemented to compress the foam with a hard plastic plunging disk. A side drain was spin-welded to the drum to drain the dirty water that pooled on the surface. This was the beginning model for summer 2014.

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The primary goal of foam filtration is to design a low cost, locally sourced, easy to operate water filtration system for communities of less than 1,000 inhabitants and for disaster-relief scenarios where the community's main water supply has been compromised.

 


 

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Figure 1: Full scale filter deployed in El Carpintero, Honduras during January 2015

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Figure 2: Sketch of the current implementation of the Small 4” Pipe Filter in the AguaClara Lab


 

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Figure 3: Example of reticulated foam used in the foam filtration technology

 

Flow through the Filter: Turbid raw water is dosed with coagulant before moving through an inverted linear flow orifice meter and pouring into the top of the foam filter body. As the water passes through all the foam layers, large particles created during flocculation stick to the pores of the foam, removing them from the water and generating a clean, drinkable effluent. When the filter becomes clogged with large flocs, it must be cleaned by initiating the backwash cycle. The backwash system employs a wooden lever-arm to lift the foam and plunge it through water accumulated in the 24" PVC pipe. This "plunge" creates a high velocity in the pores of the foam, dislodging the captured particles from the pore spaces. The backwash water, which comes out the top of the foam layers, is then drained away, and the filtering cycle may resume.

Spring 2015

Throughout the semester, backwash cleaning efficiency experiments were performed on the small-scale filter, designed in Fall 2014 to hydraulically model the full scale filter implemented in El Carpintero. The objective of these experiments was to determine an empirical relationship between backwash pore velocity and the percent mass removal of the particles from the foam during the cleaning cycle. Experimentation with different pore sizes revealed a new mechanism for filtration: the foam acts as a sedimentation tank, providing a large surface area for the flocs to settle. This is contrary to the initial hypothesis that coagulant-covered flocs stuck to the inside of the pore walls, and that a large shear force would be required to remove the flocs during backwash. Evidently, there is still much to be understood with regards to the mechanisms behind filtration and backwash.

Apart from work in the laboratory, the team continues to analyze data collected from experiments performed on the full-scale filter in El Carpintero by AguaClara engineer, Walker Grimshaw, to understand the discrepancies between performance in the laboratory and in the field.  

Much of the semester was spent preparing for the EPA P3 Conference held on April 10th and 11th in Washington, DC. The team fabricated a small scale model of the technology, prepared a technical report, and created a poster display for the competition, and received an Honorable Mention for its efforts in creating an “Off-Grid Solution to Drinking Water Treatment.”

Fall 2014

The Fall 2014 Foam Filtration team has focused its efforts in exploring the new backwashing method with the design and construction of a new apparatus: the 4” Pipe Small Scale Filter. Experiments performed on this filter, designed to hydraulically model the full scale filter, will be used to determine an empirical relationship between backwash pore velocity and the percent mass removal of the particles from the foam during the cleaning cycle.

The Chemical Dose Controller was redesigned with (1) an altered constant head tank constructed from Nalgene bottles or a 3” pipe, (2) the float situated inside the LFOM, eliminating the need for an entrance tank, and (3) major headloss elements that run vertically to reduce overall size.

Tests through mass spectrometry have confirmed that chemicals are leaching from the foam, however more testing must be done to determine the composition of the leachate. Designs for the on-the-ground implementation of the foam filter pilot project have been drawn up by AguaClara Engineer, Walker Grimshaw in Honduras. This design includes the set-up for the chemical stock tanks, designs for managing backwash and finished water, and the possible addition of a grit chamber.

The lever arm used for plunging the foam was redesigned with a rigid connection to the base of the filter support. This rigid connection eliminates large movement in the z-direction and the need for guidance by the barrel lid on the 55-gallon drum. The open-top design allows for integration of the new CDC/LFOM design: influent raw water pours out of the LFOM and directly into the filter body.

Read more about what the foam filtration team hopes to accomplish through Future Research.

 

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Team Members

Marlana Hinkley

Alena Hutchinson

Ethan Keller

Alicia Peters

Email Team

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*PPI stands for pores per inch, which is a linear measurement of foam pore size. A larger pore size number (i.e.60 ppi) corresponds to a smaller pore size.

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Team Members

Abigail Brown
Ethan Keller
Ji Young Kim
Michael Erickson

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Documents

 

Challenges

Tasks

Symposium

Final Presentation

Final Report

Additional Materials

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Summer '14

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Spring '14

 

 

Fall '13

 

 

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Fall '12

 

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Fall '11

 

Spring '11

 

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Past Research

Spring 2011
Fall 2010
Summer 2010
Spring 2010
Reflection Reports
General Filtration Page