Aquafer Water Source
(Distributed by RainDance Water Systems)
Phone: 1-877-788-8387 Fax: 760-896-6999 E-mail: sales@aquaferwater.com
 
Specializing In Water Softeners, Conditioners,
And Whole House Water Filters
Built In The USA
Residential and Commercial Water Filters and Conditioners
For The Farm, Home, Business, Factory and Plant

aquafer
waterSource

Design and Testing of a Physical Water Treatment Device

Summary: Within the water treatment industry, few subjects raise more eyebrows than the discussion of physical water treatment devices, which often come in the form of "magnets" Questions and concerns about the efficacy of such a technology usually revolve around the testing methods used and how they're applied. One particular case study with the specifics is presented here.

About 10 years ago, the term physical water treatment wasn't in our vocabulary. High Langelier Saturation Index (LSI) numbers experienced in commercial reverse osmosis (RO) concentrates were giving us operational problems with large reverse osmosis systems. LSI is a determination of when calcium scale begins to form. When the calcium hardness, alkalinity (M), and pH of a particular water are known they can be applied to a simplified chart. This chart establishes the pH (pHs) at which the calcium carbonate will come out of solution and begin to form scale for the temperature selected. This pH value is then subtracted from the actual pH of the water. A positive number indicates probable scaling. 0 is a balance point and a negative number would indicate no scaling and possible corrosion. Many customers require recoveries in excess of 50% ( % Recovery = permeate / concentrate + permeate x 100) or more. As recovery increases there is a need to bring some concentrate water back thru the pump (re-circulation of concentrate) to provide adequate flushing water flow across the membrane surface. The combination then of high recovery and recirculation dramatically increases the calcium carbonate seen by the element. The classic "cure" for this situation is to exchange the calcium for sodium through a conventional water softener or by feeding a commercially available liquid scale prevention chemical. Both of these methods are extremely effective but there can be high operating costs and in some cases sewer discharge regulations that prevent their use. Thus, the need for non-chemical (physical) treatment was established.

Existing products and patents were studied, but the basic concept for the design came from an out-of-print Permutit booklet explaining the Spiractor process of dropping water pressure to release carbon dioxide, thus reducing the solubility of calcium carbonate. A controlled pressure drop independent of a flow rate occurs in chamber A. the result is the creation of sub-micron size particles of calcium. In chamber B , a stainless steel mesh constructed of a high nickel alloy is present. Because of the flexibility of the mesh during changed in flow, the scaling found in many catalytic based devices isn't encountered. Chamber C contains multiple rare earth magnets. We were hesitant to use magnets because of the controversy surrounding their use. However, early experiments with available catalytic devices were not too successful especially if the water resided in a holding tank before being fed to an R.O. unit. We theorized that perhaps the particles that had been formed were so small that they were being re-dissolved in a short period of time. We further theorized that if we could get these small particles to cling to one another to form a more substantial size, the tendency to re-dissolve would be reduced. The same small particles that we had created in the catalytic chamber would logically have the same charge so they would repel one another. This repulsion of like charged particles is usually referred to as the zeta potential. a chemical coagulant could be used to neutralize this charge but this would defeat our purpose of elimination chemicals. We then thought to try a magnetic field to see if it would cause these particles to coagulate. In the absence of instruments and electron microscopes, we could only run tests to confirm our theory. With proper water velocity, magnetic field pattern and field strength, we were able to use the water from the catalytic process without scaling taking place after days of storage where we had experienced problems after hours of storage with the catalytic process only.

Setting the parameters

1) A test water was selected. It contained:

a) Calcium hardness 220 to 260 mg/l with a 245 mg/l average.
b) pH of 8.03 to 8.3 with an 8.1 average.
c) Alkalinity (M) 130 to 160 mg/l with a 145 mg/l average.
d) Total dissolved solids (TDS) of 556 to 745 mg/l with a 651 mg/l average
e) Iron <0.1 mg/l
f) LSI averages +0.7 at 75F and +1.4 at 150F
 
Establish if calcium hardness particles are formed during flow through the combined catalytic and magnetic physical water treatment device. Water at 45 psi and 75F was run alternately through a 2" x 10" ultrafiltration (UF) element at 80 percent recovery. Calcium hardness as measured with a LaMotte PHT-CM-DR kit was reduced 60 -75 percent in the treated water line. There was no measurable change in the hardness of the water that was not treated by the physical water treatment device. UF had a 100,000 molecular weight (MW) cut-off.
 
Conduct a long term test to establish a basis for offering the device as a scale prevention device. The test protocol was as follows:
 
a) Inlet water temperature was 54 to 91F
b) Heated water temperature range was 146 to 151F
c) Water flow in each heater varied from 1.86 to 2.1 gallons per minute
d) Water -on cycle was set at 91 seconds
e) Cycles set for heat six hours and a drain/fill of 91 seconds and repeat
f) Test duration was 324 days. No interruptions measured with a duration of over 10 minutes.
g) Estimated water flow was 5,830 gallons per heater.
 
Test Results: Prior to the test, all components were weighed to the nearest one tenth gram. After the test, all items were air dried and again weighed. The most dramatic changes were seen on the galvanized pipe sections. The section of pipe (1/2" x 12" galvanized for both) gained 36.9 grains of scale on the untreated water heater and 2.8 grains on the treated unit. This was considered a successful test and field samples followed. In-field testing indicated that the process is affective on water suppliers with a LSI up to +1.6
 
Conclusion:
 
The physical water treatment device has been incorporated into a tank along with KDF in a upward service flow pattern called The aquafer waterSource. With this flow pattern there is a constant " backwash" so there is no need to have a valve or timer on the unit. (See our Frequently Asked Questions) The aquafer waterSource uses the physical water treatment device to control hard water scale while KDF is used for chlorine taste and odor filtration. A United States (US) Patent has been issued for this unit.
 
See our complete water softening website @ www.raindancewatersystems.com
RainDance Water Systems Inc: P.O. Box 2312 Ramona, Ca. 92065
U.S. Toll Free: 1-877-788-8387 / Outside The U.S. 760-788-8387
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