Water Conditioning & Purification Magazine

It’s Not Getting Any Cleaner

By Greg Reyneke, MWS

Over two decades ago, I started compiling a database of water test data from various locations where I or my associates have had the opportunity to clean water. Reviewing the data this week shows thousands of locations, many visited multiple times over the years, where clients have become dear friends. A common thread throughout the data is that by and large, water hardness and TDS are increasing, even on surface water supplies. This makes sense, since the hydrodynamics of our planet are changing. Weather patterns have shifted, aquifers are depleted and new developments continue to demand greater amounts of clean, safe, usable water for families, farms, business and industry.

In the water quality improvement industry, membranes are defined as physical barriers that separate solutions and allow passage of waterborne contaminants within a certain range of size, molecular mass or even charge polarity and strength. When driving pressure is applied and depending on the material, pore size and electrical charge of the membrane, certain contaminants will be selectively rejected or concentrated by the membrane, while water and unrejected contaminants will pass through as a purified permeate stream. This is the essence of membrane separation. Membrane separation technology is an invaluable resource for residential, commercial and industrial water treatment applications.

On a recent consulting project, the people of a small community were facing a groundwater supply that was no longer being naturally replenished and instead being refilled through seawater ingress. Their water that typically hovered around 10 gpg with a TDS of 280 had now morphed into water with 30 gpg of hardness, an average TDS of 2,800 and a persistent presence of halophilic (salt-loving) bacteria. This posed a significant problem, since the water was now unsuitable for drinking. Instead of hydrating the drinker, it actually acted to dehydrate them and contribute to a dangerous condition known as hypernatremia, an increased concentration of sodium in the blood. Early symptoms may include a strong feeling of thirst, weakness, nausea and loss of appetite. Severe symptoms include confusion, muscle twitching and even bleeding in or around the brain.

Apart from the human issues, this type of water also wreaks havoc on piping, valves, faucets, appliances, water heaters, boilers and fixtures. High-conductivity water that is high in hardness creates a double-whammy where it is both scaling and galvanically corrosive. The high conductivity of the water along with the excess chlorides leads to a ticking time bomb of corrosivity. Improving the water quality here would require not only removing the excess minerals, metals and bacteria, but also reducing the net conductivity and chlorides. Membrane separation was the most sensible choice to protect this community.

Flow configuration
Separation membranes are typically operated in dead-end or crossflow configuration. In dead-end configuration, the rejected contaminants concentrate into the influent stream and eventually accumulate against the surface and pores of the membrane. Naturally, the concentrated contaminants will inevitably clog the membrane pores entirely, so this process is reserved for applications where the cost/inconvenience of replacing fouled membrane sheets is less important than losing any of the raw fluid, or where the engineered process flow design specifically calls for it. A growing segment of dead-end configuration is backwashable tubular or hollow-fiber construction, which is significantly less sensitive to fouling than membrane sheets. Look for increasing market penetration of this technology as the manufacture of these tubes becomes more reliable and cost-effective. In crossflow filtration, the membrane geometry is designed for contaminants to be scrubbed away from the membrane surface when the concentrated discharge stream is passed to drain or a secondary process. Leveraging the principles of Fick’s laws of diffusion, designers can manipulate macromolecule concentration molecules at the membrane surface as a function of the velocity of fluid that is flowing parallel to it.

Membrane materials and element construction
Crossflow technology is cost-effective and practical due to durable organic polymeric materials also known as composites. Composite membranes can be made from a number of materials, such as polyethersulfone (PES), polysulfone (PSU), polyphenylsulfone (PPSU), polytetrafluoroethylene (PTFE), polyvinyldene fluoride (PVDF) and even polypropylene (PP). The vast majority of installations these days utilize composite membranes, while other materials such as ceramics made from silica, aluminum, titanium and other materials are only used where pH, temperature, abrasiveness, cleaning chemistry or other operational parameters prohibit the use of polymers.

Today’s mainstream membrane separation technologies can be separated into four categories of separation by relative contaminant exclusion size:

Reverse osmosis (RO). Sometimes called hyperfiltration, this is the finest form of filtration used today. The membrane pores are small enough to enable the reversal of osmotic pressure through ionic diffusion when sufficient external energy (pumping pressure) is applied. This reversal of osmotic pressure actually drives pure water away from molecular contaminants and enables processes like brackish and seawater desalination where sodium chloride ions are physically removed from water, bringing clean, safe drinking water to places where it was previously impractical. RO is also used industrially in many ways, such as concentrating fruit juice, concentrating whey protein and sludge dewatering. Most dealers and end users know about RO separation technology, but there are other membrane separation technologies that are worth knowing more about.

Nanofiltration (NF). Developed as an extension of RO, NF functions according to the same principles of ionic diffusion as RO, but with a pore-size configuration and slight surface charge that allows passage of all contaminants except divalent and larger ions. Monovalent ions such as sodium and potassium pass right through an NF membrane, allowing it to be used as a highly effective, salt-free softening technology without the complications of RO. NF is also highly effective at addressing semi-volatile organics, such as pesticides and removing color from water. (For this community project, NF and RO membranes were staged together to deliver different levels of water quality without complicated blending valves or injection systems.)

Ultrafiltration (UF). Ultrafiltration is a true physical exclusion process and doesn’t rely on osmotic principles. UF membranes are categorized by their molecular weight cut-off rating (MWCO). The typical range of MWCOs for UF is from 1,000 to 1,000,000 Dalton, which correlates to approximately 0.005 – 0.1 micron (µm). UF is extremely effective in removing suspended solids, colloids, bacteria, virus, cysts and high molecular-weight organics like tannins. UF membranes are operated in dead-end configuration, occasional flush (forward flush and/or backflush), or crossflow configuration. Membrane configuration can vary between manufacturers, but the hollow-fiber type is the most commonly used. Membranes in this type are cast into small diameter tubes or straws. Thousands of these straws are bundled together and the ends are bonded/potted into an epoxy bulkhead. The bundles are then sealed into a housing, which is usually PVC or stainless steel. The sealed potting creates a separate, sealed space that isolates access to the inside of the fibers from the outside. This membrane and housing combination is called a module. A number of UF membrane assemblies on the market are BioVir-certified for log reduction of pathogens in drinking water, such as bacteria and virus, enabling dealers to provide safe drinking water more cost-effectively and efficiently than ever before. (In this project, UF was deployed to ensure bacterial control and reduction of turbidity before the RO and NF membranes.)

Microfiltration (MF). Microfiltration technology is deployed in both cross-filtration, spiral-wound, occasional flush hollow-fiber (forward flush and/or backflush) and dead-end, plate-and-frame configurations to great success, depending on the nature of the application. This membrane technology typically has an exclusion size of 0.2µm – 1 µm and is very well suited for the removal of particulates, turbidity, suspended solids, as well as certain pathogens such as Cryptosporidium and Giardia. MF has an established industrial track record for sterile clarification of wine and beer, whey concentration and fruit-juice sterilization. In the wastewater treatment field, microfiltration is invaluable for dewatering flocculant sludge and economically lowering BOD and COD in discharge streams. Microfiltration is also extremely effective in protecting other downstream membrane separators.

It is very important to select the appropriate pretreatment for any membrane separation process being used. Composite polymeric membranes are sensitive to oxidative damage, so special care should be taken to ensure that chlorine, ozone and other oxidative disinfectants are not present in the water being processed. Careful consideration should also be given to macro particles and organic/inorganic contaminants in the water stream that could affect proper membrane function. As a good general rule, the smaller the pore size, the greater amount of physical pretreatment required to ensure long run times and economic operation.

Regardless of the membrane pore size, operational fouling is almost inevitable, even with pretreatment. The types and amounts of fouling are dependent on many different factors, such as feed-water chemistry, membrane type, membrane materials and operational process. The most common types of membrane fouling are scale precipitation and biofouling. Fouling causes a decrease in flux, which in turn requires greater pressure against the membrane to produce a satisfactory permeate flowrate. As fouling worsens, the increased pressure (energy) requirement will cause the operating cost to increase significantly and possibly even blind the membrane completely, leading to significant damage and operational failure. (For this project, we employed antiscalant polymers along with periodic clean-in-place [CIP] procedures to lower the total operating cost.)

When designing membrane configurations, one wants to reduce energy consumption, maximize production efficiency and of course find a reasonable bounce between price and performance. It is critically important that one either secures the education needed to ensure proper system selection, design and deployment, or works with vendors/consultants who can be relied upon before getting into trouble by making uninformed decisions. The WQA’s Modular Education Program (MEP) offers a great starting point for learning more about RO and other membrane separation technologies.

Some well-meaning but misinformed people accuse membrane-separation systems of being wasteful, since water is used to clean the membrane/s during operation. I disagree with the negative description of drain concentrate water as wasted water, since it really is not. Saying that a membrane separator wastes water is akin to saying that a tree dropping its unpicked fruit is wasteful. The fruit returns nutrients to the earth and feeds the tree, which then grows more fruit. Discharge water from a membrane separation system is also not lost forever, it will return through the building’s drainage system to a municipal plant or back to the earth in an off-grid application or can be repurposed in-process by design.

We can’t ignore the opportunity cost of the water though, since it has to be cleaned, stored, treated, pressurized and distributed before it enters the membrane separator. We use energy-recovery devices and variable frequency drives (VFD) to minimize electrical consumption, as well as harvesting some of the energy from the drain discharge and returning it to the pump. The opportunity cost of the discharge can often be recovered through innovative reuse techniques, such as graywater recovery, blending with harvested rainwater, repurposing in secondary process or used as landscape irrigation. The people of this community are now able to enjoy clean, safe water every day; a luxury that many of us take for granted. The world’s water will continue to get worse, so we have to get better at choosing simple solutions to complex water problems.

About the author
Greg Reyneke, Managing Director at Red Fox Advisors, has two decades of experience in the management and growth of water treatment dealerships. His expertise spans the full gamut of residential, commercial and industrial applications, including wastewater treatment. In addition, Reyneke also consults on water conservation and reuse methods, including rainwater harvesting, aquatic ecosystems, greywater reuse and water-efficient design. He is a member of the WC&P Technical Review Committee and currently serves on the PWQA Board of Directors, chairing the Technical and Education Committee. You can follow him on his blog at www.gregknowswater.com

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