The Refrigerant Revolution: Cooling Buildings ... But Warming the Earth?

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The Refrigerant Revolution: Cooling Buildings ... But Warming the Earth?

The internationally sanctioned phaseout of chlorofluorocarbons (CFCs) is causing an unprecedented pace of change and innovation in the refrigeration industry. The old standby refrigerants no longer make the grade. These ozone-depleting chemicals are now well on their way to being contained—1995 global production of CFCs was down 76% from its 1988 peak, according to the Worldwatch Institute. Yet a problem that is potentially even more troublesome—global warming—looms ever larger on the horizon. Most refrigerants are themselves greenhouse gases, and they are used in refrigeration and cooling systems that are huge electricity consumers—associated with a whopping 23% of all electrical generation capacity in U.S., according to Lawrence Berkeley National Laboratory’s Center for Building Science.

Refrigerants escaping from older air conditioners and chillers are still harming the ozone layer. Replacing older equipment will not only eliminate a use of the most damaging chemicals, but it will also greatly reduce refrigerant leakage and improve operating efficiency. With the leaks under control, energy efficiency emerges as a key environmental benefit of replacing equipment—and it may be enough to finance the upgrade.

How Refrigerants Work

Mechanical cooling—the technology used in the vast majority of refrigeration and air conditioning equipment—is based on two principles:

1. A refrigerant can be changed from liquid to gas or gas to liquid (phase change) by altering either its temperature or its pressure.

2. Vaporizing a refrigerant (phase change from liquid to gas) absorbs far more energy than marginally raising the temperature within one phase. Condensing the refrigerant from gas to liquid

releases the same amount of energy.

These two principles are the basis for the vapor compression cycle on which mechanical cooling is based. In a residential air conditioner, for example, a refrigerant is used that vaporizes at slightly below room temperature. This refrigerant arrives in liquid form, under pressure, at the space or air chamber that is to be cooled. The pressure is reduced, and the liquid vaporizes inside a heat exchanger, absorbing heat from the surrounding air in the process. The refrigerant, now in gas form, moves on to a condenser, where it is compressed using electrical power. As its pressure increases, it condenses back into a liquid, releasing the heat it had previously absorbed. This heat is vented to the outside, and liquid refrigerant is now available to repeat the cycle.

A refrigerant must have a boiling point that is within the proper range for the application, though this point can be varied somewhat by changing the pressure in the evaporator. All common refrigerants are gases at atmospheric pressure and room temperature. In early vapor-compression refrigeration systems, naturally occurring gases such as sulfur dioxide or ammonia were used. Sulfur dioxide is highly toxic and was not used for long, while ammonia, though it is also somewhat toxic, continues to be used in some applications. Hydrocarbons such as propane and butane also began to be used, in spite of their flammability.

To address these concerns, in 1930 a team led by Thomas Midgely, Jr. at the DuPont Company combined chlorine, fluorine, and carbon to produce a new generation of nontoxic synthetic refrigerants that were sold under the tradename Freon. These chlorofluorocarbons (CFCs) were very stable, performed nearly as well as the natural refrigerants they replaced, and were inexpensive to mass-produce. They quickly became ubiquitous, not only as refrigerants, but anywhere it was useful to have a liquid under pressure change quickly to a gas when released. Thus, they were widely used in aerosol sprays, cleaning of electronic circuits, and as blowing agents for plastic foam insulation.

Relying on CFCs, the air conditioning industry expanded rapidly after World War II. CFCs were so safe and inexpensive that there was little effort to prevent their release into the atmosphere. Small leaks in refrigeration systems were not considered a problem—the system was simply “topped off” periodically with more refrigerant. The refrigerant charge was typically vented during maintenance, then replaced with new stock. No one thought twice about the gradual accumulation of these synthetic gases in the atmosphere.

Ozone Depletion and Global Warming

Estimated ozone-depletion potential and global warming potential of several common refrigerants and blends

Global warming figures assume a 100-year time horizon. Data from “Heat Pump Working Fluids: An International Overview” by Bert Stuij, published in the IEA Heat Pump Centre Newsletter,

Vol. 12, No. 1, 1994, and from New Refrigerants for Air Conditioning and Refrigeration Systems.

All that began to change in 1974, when scientists realized that if chlorine atoms were reaching the stratosphere, 12 to 15 miles (20–25 km) above the earth’s surface, they could wreak havoc on the sparse layer of ozone molecules that filters out much of the sun’s harmful ultraviolet (UV) rays. Chlorine atoms didn’t have a way to reach the stratosphere until the creation of CFCs, because other chlorine-containing molecules are not stable enough to survive the journey. Once CFCs reach the stratosphere, UV rays are strong enough to break even them apart, releasing destructive chlorine ions, and the highly water-soluble chlorine washes out of the atmosphere in rainfall.

All this was an interesting scientific theory, but it failed to get much attention until 1985, when scientists discovered an alarming “hole” in the ozone layer over Antarctica. All of a sudden, these arcane theories became a worldwide environmental concern leading, in 1987, to an unprecedented international treaty that called for a freeze and gradual phase-out of the production and use of CFCs and other ozone-depleting substances. The Montreal Protocol on Substances that Deplete the Ozone Layer required a radical and uncharacteristically rapid shift for the refrigeration industry, and for other industries that relied on CFCs.

As scientific evidence of the extent of the problem continued to mount, and as manufacturers demonstrated that alternatives were feasible, the Montreal Protocol was amended several times, mandating even quicker phase-out of ozone-depleting chemicals.

By January 1, 1996, the production of CFCs and most other “Class I” ozone-depleting substances was banned in the U.S. and other industrialized countries. Refrigeration systems using these chemicals must rely on existing stockpiles and on fluids reclaimed from other machines.

Global warming

A second and potentially more significant atmospheric problem, that of global warming, also affects most refrigerants. According to most researchers, by slowing the escape of heat from the earth’s surface into space, the accumulation of

greenhouse gases is gradually increasing surface temperatures. Refrigerants contribute to global warming in two ways. First, most refrigerants are greenhouse gases that will contribute directly to global warming if they escape into the atmosphere. On a per-pound basis, both CFCs and some of the new refrigerants being developed to replace them are hundreds or even thousands of times more powerful greenhouse gases than carbon dioxide (CO2). Second, because they are one component of refrigeration systems that consume electricity, refrigerants contribute indirectly to global warming. Much of that elec-tricity is generated by burning coal, oil, and natural gas—a process that produces vast quantities of CO2, the most significant single greenhouse gas.

This combination of direct and indirect contributions to global warming has led scientists at Oak Ridge

National Laboratory to develop the concept of Total Equivalent Warming Impact (TEWI). A refrigerant’s TEWI is calculated by combining its potency as a greenhouse gas with its theoretical efficiency (its ability to transfer heat under standard conditions). It is important to note, however, that many other factors also affect efficiency of refrigeration systems.

HCFCs

In the scramble to come up with replacements for CFCs, the initial focus was on

hydrochlorofluorocarbons, or HCFCs, some of which were already in use. By adding one or more hydrogen atoms, the molecules are made less stable, so most break down before they can reach the stratosphere. HCFCs still cause some ozone depletion, however (4% to 11% of the damage caused by CFC-11 and CFC-12), so they, too, are slated to be phased out eventually. The current phase-out schedule of these “Class II ozone-depleting substances” ranges from 2003 to 2030 depending on the compound, with an acceleration of that schedule possible, based on the outcome of a September 1997 meeting in Montreal. Some HCFCs are significant greenhouse gases, so their accumulation in the atmosphere is also problematic from that perspective.

HFCs

The other major category of CFC-replacements being used and developed is a group of compounds known as hydrofluorocarbons (HFCs). Because HFCs contain no chlorine, they pose no threat to the ozone layer. Some HFCs are still significant greenhouse gases, however. The U.S. air conditioning and refrigeration industries are looking to HFCs as the next generation of refrigerants, to replace the HCFCs now in widespread use. They are already used in most new household refrigerators, and some companies, most notably Carrier, have begun introducing HFC-based air conditioning equipment.

In addition to their contribution to global warming, HFCs in the atmosphere break down into trifluoro-acetic acid (TFA), among other compounds. There is some concern that TFA could accumulate through the hydrologic cycle to the point of toxicity to wildlife in wetlands. Research is just beginning on this potential problem. These environmental concerns have led some Northern European governments to consider HFCs as only an interim solution, like HCFCs. For a longer-term solution, many are going back to some of the natural refrigerants that were used in the past.

The “naturals”: ammonia and hydrocarbons

Ammonia is a respiratory irritant at low concentrations and could explode at high concentrations. Nevertheless, this longtime refrigerant has advantages, especially in industrial settings. Hydrocarbons such as propane and isobutane are inherently flammable and therefore potentially dangerous.

Both ammonia and hydrocarbons perform very well as refrigerants, however.

The theoretical efficiency of ammonia exceeds that of all synthesized compounds, including CFCs. While propane has a slightly lower theoretical efficiency than the best synthesized refrigerants, equipment using propane can be up to 10% more efficient than comparable conventional systems. Due to this high efficiency, and the fact that ammonia and hydrocarbons pose no ozone-depletion or global warming threat, they have generated significant interest in some countries. In Germany and Scandinavia, where refrigerators are smaller and have fewer electrical gadgets than in the U.S., hydrocarbons are commonly used in refrigerators. They are also gaining acceptance in residential air conditioners and smaller commercial systems, while ammonia is used in larger systems. In the U.S., both the Clean Air Act and most building codes prohibit hydrocarbon refrigerants in homes, according to Len Swatkowski, an engineer with the Association of Home Appliance Manufacturers. The electrical resistance heating used for automatic surface defrost in nearly all American refrigerators is particularly hazardous with hydrocarbon refrigerants.

Use of hydrocarbons is expanding in the U.K. where the British company Calor Gas has had some success promoting propane, isobutane, and various combinations of the two in small air conditioning systems. Appropriate mixes of these hydrocarbons can be used as direct drop-in replacements for CFC-11 or CFC-12 in existing equipment. Another advantage of hydrocarbon refrigerants is that 60% less fluid is required by weight, compared with HCFC or HFC systems. Safety features, such as automatic shut-off in case of a leak and shielding of electrical controls, may need to be added.

In the U.S., in addition to industrial uses, ammonia is also used occasionally as the primary refrigerant in public settings such as supermarkets, but in such cases it never circulates into the retail space. Instead, a secondary heat transfer fluid, such as propylene glycol, is used. This additional system of heat exchangers reduces the energy efficiency of the system, however, negating much of the benefit of using ammonia. Propane is also used in some settings with a secondary heat exchanger and is gaining popularity in direct use as well.

Eliminating leaks solves much of the problem

Along with implementing the internationally mandated phase-out, the U.S. EPA has taken measures to prevent the release of CFCs and other refrigerants into the atmosphere. Intentional release of refrigerants during servicing or replacement of equipment is strictly forbidden, and measures must be taken to prevent accidental releases.

Industry has responded with equipment that helps prevent releases. For example, air must periodically be purged from most centrifugal chillers, and some refrigerant typically escapes during this process. In the past, it was not uncommon for a 500- ton (1750 kW) chiller to lose 100 lbs. (45 kg) of refrigerant per year in purging, according to Eugene Smithart, Director of Environmental Affairs for The Trane Company. Current equipment has reduced that loss to less than 34 ounce per year (21 g/yr).

In relation to global warming, as the frequency of leakage and other releases to the atmosphere decreases, the operating efficiency of refrigeration and air conditioning systems becomes relatively more significant. The theoretical efficiency of CFC refrigerants is somewhat higher than their replacements, leading to an ironic situation. Engineer William Rittelmann of Burt Hill Kosar Rit-telmann Associates suggests that, in terms of large commercial systems, leaks are now so rare that the elimination of CFCs may have been unwise. “If we had tightened those systems down across the board,” Rittelmann told

EBN, “we could have stayed with CFCs and gotten better performance.” Rittelmann also points out, however, that in the changeover from CFCs a great number of older, inefficient chillers are being replaced with new systems that are much better, in spite of their use of refrigerants with slightly lower theoretical efficiencies.

Real-World Choices

In the wake of the CFC phase-out, there is a broad range of refrigerant options to choose from. Refrigerant producers and equipment manufacturers have to balance many issues when developing and selecting refrigerants, including long-term availability, heat-transfer efficiency, possible toxicity, operating pressure, and lubricant requirements.

Interim and long-term replacements

Although HCFCs are slated for phase-out between 2010 and 2030 (only the blowing agent HCFC-141b is to be phased out in 2003), they are currently the most common refrigerants. The HCFC R-22 is the most popular option for new chillers. At ambient and higher temperatures R-22 operates at significantly higher pressures than R-11 and R-12 (the CFCs that are no longer produced), so it cannot be used to replace those refrigerants in existing equipment, except in cold applications such as industrial refrigeration. Another HCFC, R-123, is the most widely used replacement for R-11 because it operates at similar (low) pressure. In addition to its status as an interim option, R-123 is plagued by toxicity concerns, which are accelerating the search for alternatives.

HFCs have the advantage of not containing chlorine, so they have zero ozone-depleting potential and thus are not slated for phase-out.

The most common HFC currently in use is R-134a, which has replaced CFCs in automobile air conditioning and home refrigerators, and is gaining acceptance for use in residential air conditioner and some commercial chiller applications. The main drawback of R-134a is that is has a lower heat-transfer capacity, so more fluid and larger compressors are required to deliver the same cooling capacity. This drives up the equipment cost.

Refrigerant blends

To improve performance and/or reduce potential hazards, most equipment manufacturers are now looking to refrigerant blends consisting of various combinations of HCFC or HFC compounds. Although some blends were in use even before the CFC phase-out, the search for better replacements has led to a proliferation of blended options. Blends of HCFCs, including various versions of R-401 and R-402, are interim alternatives. HFC-blends are considered longer-term solutions.

Use of many blended refrigerants is complicated by the fact that they are

zeotropic, meaning that the different components have different boiling points. Thus, if a system were to develop a leak while one of the components is a gas and others are liquid, more of the gas would escape, changing the composition of the fluid. A technician replacing the leaked fluid would need sophisticated testing equipment to know if the composition had changed. In addition, recharging a system with a zeotropic blend must happen under pressure, so the blend is in its liquid state.

The R-410a used in Carrier’s new Weathermaker 38TXA residential air conditioner operates at significantly higher pressure than previous refrigerants, so it requires heavier pipes and stronger fittings.

Engineer and refrigerant expert David Wylie reports that for commercial chillers as well, “410a is becoming one of the more interesting refrigerants.” “It had been considered too high-pressure,” he adds, “but now it looks like manufacturers are developing equipment that can use it.” Wylie reports that there was a similar concern with the transition from R-12 to R-22. R-22 was originally considered too high-pressure a refrigerant, but now it is widely used.

Although R-410a is a zeotropic blend, the difference in the boiling points of its components is quite small, so it is only marginally affected by the complications of using such blends. Fred Keller, director of residential engineering at Carrier, points to the fact that R-410a has a higher heat-transfer capacity than most refrigerants, allowing for smaller compressors and heat-exchangers. From an overall material consumption perspective, Keller suggests that “R-410a will enable manufacturers to build products with less material in them.” The operating efficiency of R-410a is comparable to most alternatives. Carrier’s new unit has a seasonal energy efficiency ratio (SEER) of 13, which is well above the industry average of 10.5, but far lower than the most efficient units available. Even though R-410a is much more expensive than R-22, the new unit is priced “to be competitive with other 13-SEER offerings using R-22,” according to Keller.

Riding the glide

In the future, zeotropic blends may offer higher efficiencies than are currently available using any pure fluid. This potential exists because the different components boil under different conditions, so there is a temperature range when the fluid is part liquid and part gas. This range is called the

glide of a refrigerant, and by designing the heat exchanger to take advantage of the glide, higher efficiencies are possible than with fluids that change all at once. This potential has been demonstrated in laboratories, but exploiting it is considered too complicated to be practical in the U.S. market. In Europe, where energy costs are higher, systems designed to take advantage of the glide in R-407a and in some hydrocarbon blends are currently being developed.

Lubricants

In addition to refrigerants, chillers have special, high-quality oils to provide lubrication for the compressor. Compatibility between refrigerants and these lubricants is yet another complication. Initially, it was considered a liability if a refrigerant would not work with existing mineral-oil lubricants, but that perspective may be changing. “Some of the properties of the synthetic oils actually help us,” reports Jim Parsnow, Carrier’s director of environmental systems marketing. In particular, synthetic oils have better viscosities, he says.

Options for Existing Cooling Systems

Owners and operators of buildings with existing cooling systems using CFCs have a number of options:

1. The entire system can be replaced with a new system, using either HCFCs (which will require replacement in the future), or other, non-ozone-depleting refrigerants;

2. The system can be retained and an appropriate drop-in replacement used instead of the CFC refrigerant.

3. The existing system can continue to be supported, as long as any leaks are within legal limits (15% of the charge annually), and the appropriate CFCs can be affordably procured to keep it running.

Replacing equipment

Due to gradual improvements in chiller and air conditioner efficiencies over the past few decades, any system more than 20 years old should generally be considered ripe for replacement. For large chillers, even if the entire replacement cost must be financed at market rates, the dollar savings from the increased operating efficiency will more than offset that cost, according to engineer William Rittelmann.

What to replace it with is a more complicated decision. Given the low leakage rates of new chillers, HCFC-based systems should not necessarily be ruled out if they offer improved operating efficiency.

Trane’s Eugene Smithart claims that their EarthWise™ CenTraVac system loses less than 0.5% of its charge annually. This low leakage rate is possible in part due to the very low pressure at which this R-123-based chiller operates.

If, on the other hand, the safety concerns surrounding the use of natural refrigerants such as ammonia and propane can be addressed adequately for these to be used directly, they may well be preferred choices, first because they are highly efficient, and second because they pose little or no threat to the atmosphere if they escape. Using such refrigerants with secondary cooling loops, however, will generally compromise their efficiency far beyond the point where any advantage in terms of atmospheric pollution can be justified.

The most popular option is likely to increasingly become the use of an HFC blend, because they don’t have the safety concerns of ammonia and hydrocarbons, nor the impending phase-out of HCFCs. HFCs do still have high-global warming potential, however, so they are not entirely benign if they should escape. Restrictions or taxes on the production and use of greenhouse gases, including HFCs, are possible down-the-road if evidence for global warming increases. Although they have been thoroughly studied, HFCs are still newly developed compounds, and problems may yet emerge. When compared with such hypothetical risks, however, the known hazard of CO2 emissions from energy use is most important, and operating efficiency remains the top priority.

Replacing the refrigerant

Systems that are less than 20 years old may be operating efficiently enough that it is hard to justify their replacement, yet current and future shortages of CFCs are looming. In such cases the first priority should be to do any maintenance and repairs that are necessary to minimize leakage. If even such measures cannot significantly reduce leakage, both environmental and economic concerns would suggest replacing the refrigerant with a less harmful and cheaper alternative. (This is one instance where the combination of the production ban and high excise taxes is working to bring environmental and financial incentives into alignment.) HCFCs are the most likely replacements in such systems. All feasible measures should still be taken to prevent their release into the atmosphere and to optimize operating efficiency.

Holding on tight

For newer systems that are operating efficiently and have negligible leakage, continued operation using CFCs may be feasible. Operators of such systems should be aware, however, that in spite of unprecedented international cooperation and quick action, CFC levels in the atmosphere are still on the increase, and the ozone layer continues to decline. These conditions are expected to begin reversing in the next few years, but it is imperative that all measures be taken to prevent unnecessary releases of CFCs. Although they may be expensive, CFCs should continue to be available from existing stockpiles and from reclaimed or recycled (purified) sources. Some CFCs are also being smuggled illegally into the country, so care should be taken to deal only with reputable sources.

Choices for New Systems

Given the small amounts of refrigerant that are likely to escape from new cooling systems, reducing energy use for cooling should be far and away the top environmental priority. The actual refrigerant used is only a minor factor in this effort. First, all reasonable measures should be taken to reduce the cooling load. These include selecting glazing and exterior surfaces to reduce unwanted solar gain, providing shading, using efficient lighting and mechanical systems, and much more (see “Keeping the Heat Out” in

EBN

Vol. 3, No. 3 for details). In dry climates such measures may eliminate the demand for mechanical cooling entirely—the preferred solution, both environmentally and economically.

When the entire cooling load cannot be avoided, all available options for meeting that load should be considered. Top priority should be given to passive and low-energy solutions such as night-flushing and evaporative coolers. Only when these solutions have been exhausted should conventional mechanical cooling systems be considered.

Within the realm of mechanical cooling, non-electrical systems, such as gas absorption chillers, may offer financial advantages due to the low cost of natural gas, but they tend to be much less efficient than electrical compressor-based systems. With conventional mechanical systems, many factors contribute to the overall system efficiency, including fan and pump efficiencies, optimal distribution, moisture removal capacity, and advanced controls. Chillers rarely operate at their peak capacity, so their operating efficiency under part-load conditions is an important factor to evaluate as well.

Within the matrix of all these factors, the primary consideration in selecting a refrigerant should be its compatibility with the optimal cooling system. As described above, natural refrigerants may be an attractive option if they can be used in direct systems. Otherwise, if HCFC blends offer significant performance advantages, they may be worth using in spite of their eventual phase-out. Meanwhile, the performance of HFC-blends, especially in new, high-pressure systems, is making them look increasing feasible.

Conclusion

When the ozone scare was just upon us, avoiding refrigerants containing chlorine was generally considered a top priority in environmental circles. The significant advances of recent years in containing refrigerants, especially in new cooling equipment, has changed the equation somewhat. The balance is further altered by the unprecedented international cooperation in eliminating CFCs, and the emergence of the possibly more troublesome accumulation of CO2 and other greenhouse gases as a global threat. Thus, ozone-depleting HCFCs that would be highly undesirable in applications where they can readily escape into the atmosphere may be an acceptable option if their use is necessary to optimize energy efficiency.

Similarly, the direct contribution of HFCs to global warming is mitigated by their containment within refrigeration systems. Making these systems as efficient as possible will reduce fossil-fuel-related greenhouse gas emissions, and the whole refrigerant changeover has become a valuable opportunity to upgrade chillers and air conditioners across-the- board. By far the most desirable option, however, is to design buildings from the start to eliminate or minimize the need for mechanical cooling.

Resources for more information:

New Refrigerants for Air Conditioning and Refrigeration Systems by David Wylie, P.E. and James W. Davenport offers a good introduction to the field and a comprehensive overview of the options. It was published in 1996 by The Fair-mont Press and is distributed by Prentice Hall, Inc.

Commercial Space Cooling and Air Handling Technology Atlas from E Source, Inc. is an excellent overview of strate-gies for optimizing cooling systems in commercial buildings. This atlas is available as part of a (quite pricey) membership in the E Source information service:

E Source, Inc.

1033 Walnut Street

Boulder, CO 80302-5114

303/440-8500, 303/440-8502 (fax)

esource@esource.com (e-mail)

www.esource.com

Published February 1, 1997

(1997, February 1). The Refrigerant Revolution: Cooling Buildings ... But Warming the Earth?. Retrieved from https://www.buildinggreen.com/departments/feature

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Ecological Wastewater Treatment

Feature

Ecological Wastewater Treatment

Since the late 1980s about two dozen ecological wastewater treatment plants have been built, ranging from small systems serving individual schools, to medium-sized municipal systems serving several thousand households, to waste treatment plants for industries designed to treat specialized waste-water flows.

Using the natural cycles of plant and animal life instead of chemicals and mechanical systems to process wastewater holds a great deal of attraction. Conventional sewage treatment systems already rely on bacteria to do much of the work, but these organisms perform very restricted functions within a system that is generally mechanistic. Ecological engineering brings more highly evolved flora and fauna into the equation, providing an attractive and educational alternative for wastewater treatment.

 

Since the late 1980s about two dozen ecological wastewater treatment plants have been built, ranging from small systems serving individual schools, to medium-sized municipal systems serving several thousand households, to waste treatment plants for industries designed to treat specialized waste-water flows.

These systems are commonly known by the now-trademarked name Solar Aquatics™ or the term “living machines.”

 

What is ecological wastewater treatment?

All sewage treatment plants rely on living organisms to break down biological and chemical wastes. In conventional treatment plants, concentrated bacteria serve to partially decompose wastes in a series of aerated pools. Various chemicals are then used to precipitate out sludge and disinfect the effluent.

Ecological wastewater treatment plants function in ways that are fundamentally similar but use highly varied ecosystems with a wide range of organisms—algae, aquatic plants, marsh plants, worms, crustaceans, mollusks, and vertebrates—supporting the populations of bacteria that break down wastes and eliminate nutrients from the wastewater. This ecological community makes the systems more stable in the face of sudden doses of heavily contaminated water, known as shock flows, according to Steve Fluck, a process chemist at one such facility.

The principles of ecological wastewater treatment were developed by Dr. John Todd, a Woods Hole biologist who founded the New Alchemy Institute in 1969 and Ocean Arks International (OAI) in 1982. The nonprofit OAI is carrying out a broad range of living machine demonstration projects in different parts of the world. Meanwhile, Todd’s ideas are being pursued commercially by two different companies—Ecological Engineering Associates (EEA) of Marion, Massachusetts, which owns the tradename Solar Aquatics and certain proprietary aspects of Todd’s original treatment technology, and Living Technology, Inc. (LTI) in Burlington, Vermont, which is specializing in wastewater treatment for food processors and other industrial applications.

 

Though systems differ widely in their specifics, the schematic below provides a typical example of how an ecological wastewater treatment plant works.

Raw sewage flows into the system from an equalization tank, where grit is settled out and the wastewater is “seeded” with bacteria to jump-start biological activity. This stage can be part of the ecological system, or part of a larger, conventional plant from which the ecological system draws sewage.

Depending on the strength of the wastewater, anaerobic reactors may or may not be used for preliminary processing. From here, the wastewater flows through a series of aerated reactor tanks or silos. These tanks are connected in series, with wastewater flowing by gravity pressure from one to the next. Usually there are several parallel trains of these in-series tanks to increase retention time and provide redundancy in case of a malfunction. Each of the tanks provides a mini-ecosystem with a layer of floating aquatic plants at the top (often supported by mesh netting). The extensive root systems of these plants extend down into the water and provide habitat for the bacteria, which do most of the actual work in breaking down wastes. The tanks also support algae, small crustaceans, snails, and higher animals. The tanks later in the purification series are typically designed for an ecology of higher organisms, including vertebrates.

 

Clear or translucent plastic tanks are the hallmark (and most significant patent) of the Solar Aquatics plants designed by EEA—Todd calls it “using light in three dimensions.” In part to avoid patent conflicts, plants designed by LTI have larger

opaque tanks made of enameled steel, rigid non-chlorine plastic (polypropylene or polyethylene), or concrete. The tanks in LTI’s new 80,000 gallon-per-day (300,000 l/day) municipal sewage treatment plant in South Burlington, Vermont are 14 ft (4.25 m) deep and 17–18 ft (5.2–5.5 m) across and have artificial support structures for plants to facilitate ecosystem development deep underwater.

Following processing in this series of tanks, the water flows into a clarifier tank where solids are settled out as sludge. Some of these solids may be removed and used to seed the incoming sewage with bacteria; the rest is removed for storage, composting, or land application.

 

In EEA plants, the clarified water flows into a subsurface-flow constructed wetland (passing through a sand filter first in some facilities). The wetland maintains an anoxic environment in which anaerobic bacteria remove nitrogen from the water.

The constructed wetland is very similar to the subsurface-flow constructed wetlands described in an earlier

EBN article on alternatives to conventional on-site wastewater treatment (

Vol. 3, No. 2), except that in cold climates they are typically built in greenhouses to keep them warm enough for optimal biological activity year-round.

At LTI facilities, the constructed wetlands are partially or totally replaced by a new, more compact system to provide this denitrification: an

ecological fluidized bed. This system, recently developed by Todd and LTI, is essentially a submerged biofilter that does the job of the wetland in a much smaller area at a much lower cost.

The ecological fluidized beds are one example of a gradual shift in the technology, according to Bob Bastian, an environmental scientist with the U.S. EPA and project manager for a forthcoming report on ecological wastewater systems. “In many cases they have made changes from the original ecological engineering systems, making this a much more conventional design to make it more compact and efficient,” Bastian says. John Todd is no longer directly affiliated with EEA, but he is on Living Technologies’ board of directors. Todd presents this evolution in a different light, saying that, LTI has an excellent team of engineers, which “is focused on bringing the ecology part of ecological engineering into the language and workplace of mainstream civil engineering.”

Steve Fluck acknowledges that some aspects of the living machines function in fairly conventional ways, but argues that later stages are fundamentally different with their reliance on more complete ecosystems. From the constructed wetland or fluidized bed, water may undergo disinfection with ultraviolet (UV) light or another system prior to discharge into surface waters or into groundwater through an infiltration bed.

 

Performance of ecological wastewater systems

Proponents of Solar Aquatics and living machines describe their systems as more effective than conventional wastewater treatment for most criteria. An independent assessment of these systems for a forthcoming U.S. EPA report on ecological wastewater systems, however, is less generous. Consultant Sherwood Reed, P.E., author of the EPA report, feels that functionally these systems are at best comparable to conventional systems on most counts. “There are no wastewater parameters which I am aware of that are removed more effectively in their systems,” Reed states.

The performance of wastewater treatment can be measured in several different ways. BOD, or

biochemical oxygen demand, is one of the most common measures of purity. This is a measure of how much oxygen will be removed in the process of decomposing (oxidizing) organic matter in the water, measured in milligrams per liter over a specified number of days. BOD5 refers to that oxygen demand over five days. The higher the BOD, the greater the damage to natural ecosystems, which depend on dissolved oxygen in water. Typical residential wastewater has a BOD5 level of 200 to 290 mg/l, according to the U.S. Environmental Protection Agency (EPA), but levels may be considerably higher if wastes from garbage disposals are included. Ecological waste-water systems are generally effective at reducing BOD and the related but more persistent

chemical oxygen demand (COD).

Another measure of performance is nutrient removal. Wastewater contains high levels of both nitrogen and phosphorous. Nitrogen removal occurs through a biological process of nitrification and denitrification. In the first stage, aerobic nitrifying bacteria convert ammonia into nitrite and nitrate. In the second stage, anaerobic denitrifying bacteria convert nitrate into molecular nitrogen (N2) and release it into the atmosphere. This stage requires some carbon, but nearly all the naturally occurring carbon has been eliminated from the flow by this point. Ecological system designers are experimenting with various low-tech sources of added carbon, but to date the only cost-effective and reliable solution has been to use the same chemical process used at conventional sewage treatment plants—the addition of methanol. Fluck argues that they are using the methanol only until more organic sources of carbon are developed, and to establish that these systems can outperform conventional treatment when it comes to nitrogen removal.

Phosphorous removal has proven even more difficult than nitrogen removal for ecological systems. Natural uptake by plants can only remove up to 60% to 70% of the occurring phosphorous, according to Shaw. To achieve further reductions ecological systems would have to use conventional chemical precipitators, such as ferric chloride or polymeric compounds. They rarely do so, however, preferring to leave relatively high phosphorous levels in the effluent. This weakness in nutrient removal is not critical if the outflow goes into the ocean or soil, but it could be a problem for systems that feed into surface waters.

Other measures of wastewater treatment plant performance include removal of Coliform bacteria (which are considered indicator species for pathogenic bacteria and viruses), water clarity (turbidity), odor, and heavy metal concentrations. With the exception of a few specific compounds, ecological wastewater systems are generally effective for all these contaminants, according to current operating experience.

 

Comparing costs

 

As with most innovative new technologies, whether they succeed in penetrating the market often comes down to a matter of cost. If they can compete economically and do as well or better in terms of performance, the companies engineering and building these systems should be able to prosper. Both initial system costs and lifecycle costs, including operating and maintenance expenses, are important considerations.

Construction costs of ecological wastewater treatment plants have been highly varied. A 25,000 gallon-per-day (95,000 l/d) ecological wastewater plant designed by EEA and currently nearing completion in Ashfield, Massachusetts is costing a hefty $2.2 million. Because the technology is not yet “endorsed” by EPA, all sorts of obstacles had to be cleared in permitting it, and numerous redundancies had to be incorporated into the plant to provide for successful operation if a portion of the plant fails, since this will be the sole wastewater treatment plant for the town. These factors drove up the price.

 

A similar system recently built near Halifax, Nova Scotia with a design flow of 18,000 gpd (68,000 l/d), came in at $600,000 (Canadian) and was completed in a fraction of the time required for the Ashfield system.

This Bear River plant won out over conventional wastewater treatment technologies in competitive bidding, because the treatment plant could be located right in the center of a densely populated area, while the conventional plant would have necessitated several miles’ separation from the town center (because of odor). Even though the ecological wastewater plant was itself more expensive than the conventional plant, the savings achieved by not having to pipe the sewage an extra two miles brought the total package price lower.

An 80,000 gpd (300,000 l/d) plant completed this past February in South Burlington, Vermont by LTI came in at a total cost of $640,000. This plant cost so much less than the Ashfield system because it is a demonstration project working in conjunction with a much larger conventional facility—all pretreatment functions, such as screening and grit removal, and post-treatment functions, including discharge piping, disinfection, and outfall, are provided by that facility.

Operating costs for wastewater systems include labor, energy, and chemicals. John Todd estimates that labor costs for ecological systems should be comparable to those for conventional systems. Energy use in both conventional and ecological systems is primarily to power the pumps that circulate air through the tanks. Reed estimates that energy and chemical requirements for each type of system should be similar. Shaw of LTI reports that they are finding 25% reductions in energy costs, however, and that chemical costs of ecological systems should also be lower.

Studies done for the EPA report suggest that on a 20-year lifecycle basis, current ecological systems are comparable in cost to conventional wastewater treatment only for quantities of 50,000 gallons per day (180,000 l/day) or less, according to Reed. According to this analysis, at larger sizes the multiple greenhouses and tanks required become more expensive to build than the single large chambers used in conventional systems. System proponents contend that lower operating costs make ecological wastewater systems a less expensive choice in many cases.

 

Moving forward with ecological wastewater treatment

Ecological wastewater treatment is a different approach for treating wastewater that flies in the face of an inherently conservative civil engineering profession. To succeed on a municipal level, proponents of the technology have to convince multiple layers of government bureaucrats on local, regional, state, and sometimes even federal levels that the systems will work and can be operated economically. Bidding and contracting typically require cumbersome, drawn-out procedures that make innovation difficult at best. Given these challenges, the fact that systems have been built at all may be remarkable. Some plants, such as the facility in Ashfield, Massachusetts, have taken as long as five years to move through from concept to operation. These stumbling blocks are one of the reasons that Living Technologies, Inc. has focused more on industrial facilities, where decision making and contracting can proceed more quickly.

Ecological wastewater treatment is currently proceeding largely in the demonstration phase. The systems being installed tend to vary considerably from one another as the researchers continually modify and improve the technology. As performance data is collected from these systems over the coming year or two, certain design aspects are likely to emerge as preferable to others. Eventually, simple, turn-key plant designs may become available that can be specified and contracted out fairly quickly. Once that stage is reached, assuming that performance matches expectations, the potential for more rapid implementation of the technology should be very good.

 

Because ecological wastewater treatment plants operate odor-free and can be esthetically pleasing, they are unlikely to generate as much NIMBY (not-in-my-backyard) opposition, and they can be situated in populated areas.

The fact that they can be integrated into an attractive landscape gives them a strong advantage for some food-processing and industrial sites—its positive experience with a living machines in Henderson, Nevada and Waco, Texas has spurred the M&M/Mars Company to order three additional systems for plants in other parts of the world. These advantages should help them attain significant market penetration.

On the other hand, possible relaxation of water pollution standards and loss of federal support for new water treatment plants could be major obstacles to greater use of these systems. Unless effective ecological means of removing phosphorous can be found, ecological systems will be forced to depend on more conventional technologies before releasing treated effluent into surface waters.

Another obstacle that may inhibit greater penetration of this technology is the real or perceived infighting that has been occurring among the technology developers. Both EEA and LTI have sought to commercialize ideas of Dr. Todd, and Todd maintains an interest in both companies. But proprietary aspects of ecological wastewater systems threaten to prevent the ideas from making it into the mainstream, because even the terminology has to differ from one company to the other due to trademarks and patents. The technology used to be widely known as Solar Aquatics, but this name is now owned by EEA, along with a patent for use of clear or translucent solar tanks. LTI has its Living Machine terminology with opaque tanks (which they claim to have found work just as well as the translucent ones), and they have patented their Ecological Fluidized Bed concept, though company president Michael Shaw told

EBN the company willingly shares the technology.

EEA and LTI should recognize that each needs the other to be successful if they want their ideas to be widely implemented. Confusion that is generated in the marketplace by inconsistent terminology and differences in technology based on legalities rather than differences in performance is not healthy. With greater cooperation, ecological wastewater treatment stands a good chance of establishing itself firmly in conventional practice.

 

 

For more information:

 

Susan Peterson, President

Ecological Engineering Associates

13 Marconi Lane

Marion, MA 02738

508/748-3224, 508/748-9740 (fax)

Sherwood Reed, P.E.

Environmental Engineering Consultants

RR 1, Box 572

Norwich, VT 05055

802/649-1230, 802/649-5725 (fax)

Michael Shaw, President

Living Technologies, Inc.

431 Pine Street

Burlington, VT 05401

802/865-4460, 802/865-4438 (fax)

Dr. John Todd

Ocean Arks International

One Locust Street

Falmouth, MA 02540

508/540-6801, 508/540-6811 (fax)

 

 

Published July 1, 1996

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