In order to assist you in understanding more about radon, its health effects,
and some common methods for testing and mitigating, we have provided information and resources.
Radon is a gas that is created in the soils where uranium and radium are found. These elements can be found everywhere in the world, therefore any building has the potential for elevated levels of radon. The more uranium found in the soil, the higher the potential for elevated radon levels within a building constructed above this soil. It is not a question of, Is there radon? but rather, How much radon is there?
Radon primarily comes from natural deposits of uranium in the soil. It is not because of a man-made landfill or other suspicious sources. Uranium breaks down to radium, which in turn decays into radon gas.
Radon is an inert gas, which means that it does not react or combine with the elements in the ground. Because of this, radon gas can move up through the soil into the atmosphere, where it is easily diluted and presents little concern. However, when it enters a building constructed on top of this soil, it can build up and become a health concern.
You cannot see or smell radon. There is no way that your body can sense the presence of radon, yet it can have a detrimental effect on the inhabitants by increasing their likelihood of developing lung cancer.
Buildings are typically at a lower pressure than the surrounding air and soil. This causes radon and other soil gases to be drawn into the building.
There are several reasons why this occurs. One cause is the effect that exhaust fans have when removing air from a building. When air is exhausted, outside air enters the building to replace it. Much of this replacement air comes in from the underlying soil.
When interior temperatures are higher than outside temperatures, thermal effects occur inside of the building. Just as warm air causes a balloon to rise because the surrounding air is cool, warm air rises within a building and is displaced by cold, dense outside air. Some of the outside air, which is displacing and replacing the interior air, comes from the soil.
Whenever air enters a building from underneath, radon will most likely come in as well if radon is present in the underlying soil.
The forces that draw radon into a structure vary, which in turn effects the entry rate of radon. Measurement devices that average radon levels over long periods of time provide a better indication of the amount of exposure to radon.
The minimum duration of any test, the results of which could be used as a basis for determining the need for remediation, is 48 hours.
Radon also varies from season to season as a function of climate and the use of the home by occupants (open windows-closed windows). It would be ideal if a year-long test could be conducted, however, such timing would be unrealistic for the purpose of a real estate transaction.
Short-term tests are utilized to determine the potential of a home for having elevated levels of radon, independently of how the house is operated. The tests involve closing all windows and doors, except for normal exit and entry, and testing on the lowest occupiable location in the home. This technique has become the method for testing homes during real estate transactions.
Once radon enters a building it is easily dispersed through the air. The radioactive decay process that leads to the creation of radon does not stop. This causes the radon to decay into several radioactive elements called radon decay products. These decay products are made up of different forms of polonium, lead and bismuth.
Unlike radon, which is a gas, the radon decay products produced from radon are solid particles. These particles become suspended in the air when they are formed from the decaying radon gas. These particles are extremely small and cannot be seen.
Because they are extremely small particles, radon decay products are easily inhaled and can attach to lung tissue. They have very short “half-lives” which means that they will decay relatively quickly after they are formed. In fact, if they are inhaled, they will decay in the lungs before the lungs have an opportunity to clean themselves.
It is the radon decay products that actually present the health risk associated with radon gas.
When radon decay products are inhaled they will stick to sensitive lung tissue. Being short-lived, they will break down while they are in the lungs, thereby exposing the lung tissue to radiation.
When radon decay products decay, they release alpha, beta and gamma radiation. It is actually the alpha radiation (in the form of particles) from the two radon decay products - polonium 218 and polonium 214 - that are the most hazardous.
The alpha particles, that come from the decay of radon decay products, will impact the sensitive lung tissue. In most cases they will kill the lung tissue cell, which can be replaced by the body. However, the alpha particles can impact the DNA, or create a chemical reaction that will affect the DNA. When this occurs the cell can become mutated.
This is the mechanism by which prolonged exposure to radon and radon decay products can increase the potential of lung cancer.
When radon decay products are inhaled they stick to sensitive lung tissue. Being short-lived, they will break down while they are in the lungs. This exposes the lung tissue to radiation.
If the alpha particle which is released hits a live cell, and within the cell it hits the nucleus, and within the nucleus it hits the DNA, and within the DNA it hits and damages the cancer suppressant gene and increased risk for contracting lung cancer can exist. In addition to the alpha particle causing, the alpha particle can also cause ionization of material around the DNA that can also damage it (shown on right of DNA strand).
This is the mechanism that radon (and more specifically the radon decay products) can lead to an increased risk of lung cancer.
What is the probability of this happening? It is based on how much you are exposed to and for how long. Being exposed to radon does not mean that you will contract lung cancer. To develop lung cancer from radon the radiation released from its decay has to strike a lung cell and within that lung cell it has to strike a specific location.
Since the radiation is released in a random manner, the potential for lung cancer increases with exposure, whether that be exposure to a small amount of radon for a long period of time or a high amount of radon for a short period of time.
The probability of contracting lung cancer is like a blind folded person tossing darts at dartboard. If the person tosses a single dart at a time, it is probable that it will take a considerable period of time before the person strikes the bulls eye.
On the other hand, if the person throws a handful of darts at a time, it is likely that less time will pass before the person strikes the bulls eye.
This analogy can be used to understand that the probability of an alpha particle striking a sensitive part of a lung cell in a manner that will cause cancer depends on dose and time of exposure, or
Lung cancer risk from radon is a function of:
The effects of radon have been around a long time. Its effects were first noted as an unknown disease in the 1400’s. Lymphosarcoma was first identified in autopsies conducted in 1879 on European miners.
In modern times (1950’s to present), a higher than expected occurrence of lung cancer has been noted in uranium miners within the U.S., Czechoslovakia, France and Canada. Excess lung cancers have also been observed in other underground (not uranium) miners in Newfoundland, Sweden, Britain, France, China, and the U.S.
The presence of radon at elevated levels in above ground structures, such as homes, commercial buildings and schools was not well known until the mid 1980s. Remember, you cannot see or smell radon. Many homes and schools have been measured with radon levels in excess of underground mine concentrations.
Today the effects of radon are well known. The issue is not if radon causes cancer, but rather, how to control the radon exposure in our homes, workplaces, and schools.
Based upon current and past studies, the EPA established a guidance for non-occupational exposures to radon. This guidance level was arrived at by analyzing both the health risks and the cost of fixing buildings with elevated levels. That is, the 4.0 pCi/L guidance is both a health and an economic based number.
The 4.0 pCi/L guidance is not a safety standard. Levels below 4.0 pCi/L still represent some risk. Even the outdoor air contains some radon. So, avoid making comments such as “the house tested safe,” or “there is no radon in the home.” Just because a house is below the EPA’s action level does not mean that there is no risk at all.
The conclusion that radon is a serious health risk is supported not only by the US EPA, but also the American Lung Association, the National Academy of Sciences and the National Council on Radiation Protection, among others.
Due to the amount and strength of data that has been collected, radon is placed in the highest category of cancer causing agents. This category is referred to as Group A, which contains materials that are known to cause cancer in humans.
Being a Group A carcinogen certainly underscores the reasons there are concerns about radon. Being a Group A carcinogen also strengthens concerns about liability when a home or commercial building is sold. This is why radon testing has become more common at the time of sale.
The comparison above is from the US EPA’s Citizens Guide to Radon. It compares the estimated number of deaths in the U.S. due to radon, with other more widely known causes of death. This comparison provides one reason why the EPA and other health organizations are so concerned about the radon issue. Furthermore, because radon is so easy to detect and also easy to fix, one can see why radon detection and remediation has become such a priority.
The US EPA and the National Academy of Sciences estimate that approximately 11% of the lung cancer deaths in the United States each year can be attributed to radon exposure. This translates to somewhere between 15,000 and 22,000 radon-induced lung cancer deaths each year in the U.S. This includes radon-induced cancer in both smokers and non-smokers.
Applying the U.S. data to the rate of lung cancer deaths in the state of Colorado for the year 2000 and also adjusting for the higher radon exposure in Colorado, it is estimated that 350 lung cancer deaths occur each year in Colorado due to radon exposure.
Notes: per Colorado Dept of Public Health, there were 1,426 lung cancer deaths (LCD) recorded in Colorado during the year 2000. Assuming these were lifetime residents exposed to the Colorado average long-term radon exposure of 2.59 pCi/L, one can factor the U.S. data as follows:
18,600 radon LCD (US1995) X 2.59 pCi/L (Colo. Avg.) X 1,426 Colorado LCD (2000) = 350 radon induced Colo. LCD/year
157,400 total LCD (US 1995) X 1.25 pCi/L (US average)
The U.S. EPA’s concerns about radon are shared by many other independent health based agencies.
During the mid 1980s, the EPA was perceived by some as taking a “Chicken Little” attitude towards radon. That is, they were accused of making too much out of the issue. After all, radon is something that you cannot see or smell. It has been with us for a long time - so what’s the big deal?
However, after several other health based organizations reviewed the data that the National Academy of Sciences used to develop the EPA’s health risk assessments, they joined the EPA as Cooperative Partners to assist in educating the public about this significant environmental health concern.
In addition to the entities listed on the slide, the EPA is joined by many cooperative partners such as the National Association of Counties, The American Lung Association, The National Environmental Health Association.
NO! Since the late 1980’s, radon measurements have been taken throughout the United States. This data has been collected and compared to geological formations to yield the map shown above. This map was originally developed for the purpose of establishing the degree of radon reduction methods that should be incorporated into the construction of new homes and buildings. However, it has served as a tool for focusing public awareness efforts on radon. It has also become a tool for relocation companies and lenders to develop their radon testing policies. The zone classifications are based upon being able to predict the likelihood of finding certain ranges of radon concentrations when conducting short-term measurements (as is often done at the time of a real estate transaction).
Key:
In comparing zones on the map above, one should remember that the US EPA and Surgeon General recommend that people not be exposed, on a long-term basis, to levels of radon in excess of 4.0 pCi/L. Additionally, one should realize that significant variations can occur within a county and there is no substitute for testing to verify individual conditions.
Radon Measurement Key Points
There is no "totally safe" level of radon exposure
4 picoCuries per liter is the "action level" recommended by the EPA
All radon problems can be fixed
Radon levels in homes can typically be reduced to between 2-4 picoCuries per liter
How to Test for Radon
There are reliable ways to measure indoor radon for short-term test periods that last only a few days, and for long-term test periods that may range from a few months to more than a year. Using recommended measurement devices, you can determine the radon potential of the home under "worst case conditions" (short-term test), or measure actual radon exposure under normal living conditions, (long-term test).
Homebuyers and sellers often prefer to have a radon test performed by a trained professional tester. In that case, EPA strongly recommends the use of a qualified radon measurement professional who has been trained in the proper placement of radon measurement devices and the interpretation of their results.
Often, at the time of sale, it is desirable to know a building's potential for radon exposure, independent of how the building is currently used. Short-term tests are typically conducted over a two or three day period. Results of short-term tests represent the radon potential of the home, rather than the actual exposure encountered under normal living conditions, unless residents keep the home's windows and doors closed year-round. That's because EPA guidelines for short-term radon tests require "Closed-House Conditions," to promote maximum radon concentration during the brief test period.
The placement of the device within the home must follow the manufacturer's instructions and is dependent on whether or not the test is being conducted for a real estate transaction.
Short-term tests are usually 2 to 7 days long and are done under "closed-house" conditions that begin at least 12 hours before the test and remain in effect for the duration of the test.
Short-term, "closed house" radon tests should not be conducted during rainy weather, especially when the rain is accompanied by persistent winds. Changes in barometric pressure and other forces can cause indoor radon levels to rise during a rain storm and skew the test results higher than found under otherwise normal conditions.
Note: Placing the test device in a closed room or leaving doors and windows open during the test is improper and can invalidate a test.
Radon Test Devices
There are several devices on the market. EPA recommends that you begin with a short-term test device placed in the home for a minimum of two days. The devices in most home test kits are actually small containers of activated charcoal. Look for kits approved by one of the national certification programs (NEHA NRPP or NRSB).
You can purchase a kit from hardware stores or other retail outlets, as well as through non-profit organizations such as the National Safety Council (800-767-7236). Most of the kits range in price from $10 to $20. The cost usually includes the test device, the price of postage to mail the detector back to the laboratory, and the written report you receive by return mail.
There are two types of short-term test devices:
It is not appropriate to use "Grab Samples," which test for less than 48 hours, as this is more of a diagnostic device and will not provide a representative radon potential measurement for the home.
If a short-term radon test is conducted correctly for a minimum of two days, under closed-house conditions, one can reasonably say:
The location of a radon test depends upon whether the test is being done for a real estate transaction or not. Since the purpose of the first, short-term test is to be able to identify homes that are clearly below 4.0 pCi/L, it is necessary to place the test device in a part of the home that would be expected to have the highest radon level.
The device should be placed in a room that is frequently occupied, but where high humidity in the air would not be expected. Examples of good locations would be bedrooms, dining rooms, and family rooms. Never place the device in a closet, crawl-space, storage area, kitchen, garage or bathroom.
In order to have confidence in the radon reading, the device should be placed in the lowest occupied space, for non-real estate transactions. A finished basement is normally chosen in those parts of the country that typically have basements.
In the case of a real estate transaction, the device should be placed in the lowest portion of the house that could be finished and occupied by future occupants.
If the radon measured is below 4.0 pCi/L, there is good reason to believe that the rest of the home is also below 4.0 pCi/L. Furthermore, if the closed-house test protocols are followed, there is good reason to believe that a low short-term test result (below 4.0 pCi/L) means that the average radon throughout the year will probably also be below 4.0 pCi/L, during normal use of the house.
Remember, short-term tests determine the radon potential of a home, independent of how future homeowners may operate or occupy the house.
Test Device Placement
A proper location must be selected to obtain an accurate measurement of radon in air that represents the breathing space of the home. The test device should be at least 20 inches from the floor, 4 inches from another object, 12 inches from an exterior wall, and 3 feet from an outside window. The device can be placed near an interior wall, perhaps on a book shelf, but should be at least four inches from the wall or the back of the shelf, to allow good air circulation.
Devices that are designed to be hung by a string should be approximately 12 inches from the ceiling.
Test devices should also be located away from drafts and should not be placed in rooms with excess humidity.
Long-Term Tests - Actual Radon Exposure
For the occupants of a home, actual radon exposure depends on how they use the home, where in the home the occupants spend their time, and how much freshair is brought into the living area. Since these factors may vary over time, the only reliable way of measuring the actual radon exposure is to conduct a long-term test for at least three months, under normal living conditions.
In the past, prospective homeowners have often been reluctant to purchase a home before performing a long-term test, for fear of not being able to correct a radon problem afterward. However, improved technology and the proven durability of radon mitigation systems have served to reduce much of that concern.
This does not mean that a short-term test is less valuable as part of a home inspection process; but rather, if the results of that test show a potential radon concern, a long-term test can more accurately show actual average radon levels. By conducting a long-term test after moving into a home, the homeowner can control test conditions and, if needed, make decisions on how a mitigation system will be installed.
The placement of the test device within the home must be in accordance with the manufacturer's instructions.
Test Results
If you perform the short-term test and the results are higher than 4.0 pCi/L, the EPA recommends you take further action. The next step should be to retest the home on a long term basis, ideally for a year, then decide if mitigation is necessary.
However, if the initial short-term test finds radon levels are significantly elevated, such as 10 pCi/L or more, you may want to repeat the short term test using a different test device to confirm the radon is still elevated. You can then average the two results and base your mitigation on the average.
The health risk from radon is cumulative, increasing over time if the radon level is elevated and not corrected. The health risks from radon occur over a long period of time and radon concentrations vary from season to season. An average radon level, measured over all four seasons, is a better indicator of actual health risk over time.
On the other hand, if your initial readings are significantly elevated, you should take action to quickly confirm these readings and then proceed to mitigate the home. Again, you may want to repeat the short-term test, using a different test device to confirm the radon is still elevated, then average the two results and base your mitigation on the average.
Radon decay products can also be measured using a special monitor that reports in Working Levels (WL). This can be done as an initial measurement or, more typically, after initial measurements have identified a potential concern in commercial buildings or homes with relatively low initial radon readings. The EPA guidance for radon decay products (comparable to 4.0 pCi/L of radon) recommends people should avoid long-term exposures in excess of 0.02 WL of radon decay products.
Radon in the ground can dissolve into water that finds its way to a well. When well water that contains radon is brought directly into a building, the dissolved gas is released indoors as the water leaves the faucet, showerhead or other outlet.
The amount of radon brought into the building will depend upon the amount of water used and the amountof radon in the water. Given typical water usage rates and radon concentrations found in wells, this entry mechanism only accounts for about 1-2% of the radon that enters homes in the U.S.
Most indoor radon comes from the soil. Thus, most remediation efforts concentrate on reducing the entry of radon from soil rather than water. As a rule of thumb, it takes 10,000 pCi/L in the water to add 1pCi/L to the air in a home, after the radon dilutes and dissipates within the large volume of air indoors. This is above and beyond that which comes from the soil.
The US EPA has recommended maximum contaminant levels (MCL) ranging from a low of 300 pCi/L to as high as 4,000 pCi/L of water for community water supplies. The regulation, as proposed, would not impact private wells, and no firm implementation date has been set.
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The system should be installed in accordance with the U.S. EPA's Radon Mitigation Standards if no local building codes exist. The EPA model standards provide helpful, specific guidance. For example:
The discharge shall be at least 10 feet above grade, 10 feet away from an opening which is two feet below the discharge, and above or at the eave of the roof.
If the exhaust pipe is routed outside the home, the discharge must still meet the above criteria
System fans should not be located inside the home or in a crawlspace. They can be in an attic, outdoors, or in a garage, provided there is no living space above the garage.
There should be an indicator located in a prominent place that will easily let the occupant know if the system is functioning properly.
Power to the fan should be supplied in accordance with local electric codes; including permits where required.
All portions of the system are to be labeled and a simple instruction manual, with warranties, provided to the homeowner.
All homes with mitigation systems should be retested no sooner than 24 hours nor later than 30 days after installation, to verify reduction. The home should also be retested every two years.
Reliable techniques exist for reducing radon levels in homes. Experience with radon mitigation systems has developed to the point that virtually any home can be fixed, either by a trained radon contractor, or in some cases, by homeowners who accomplish the repairs themselves.
Research by public and private agencies, combined with years of extensive hands-on mitigation experience and long-term follow-up studies on the durability of mitigation systems form a strong knowledge base of proven mitigation techniques. The techniques are straightforward and, for a typical single family residence, can be done in one day by a qualified contractor. Radon reduction requires more than just sealing cracks in a foundation. In fact, caulking and sealing of foundation openings, on its own, has proven NOT to be a reliable or durable technique. However, sealing is done in conjunction with other mitigation steps.
Active soil depressurization (ASD) has proven to be a very cost-effective and reliable technique for radon reduction. ASD systems collect the radon from beneath the building before it can enter. The systems can be simple or complex depending upon the design of the building. Operating costs of the system fans are modest, due to their low power consumption (typically less than 90 watts per fan).
The system draws the radon-laden soil gas from beneath the foundation and exhausts it outside of the building, far enough away from windows and other openings that it will not reenter. The system typically consists of a plastic pipe connected to the soil either through a hole in a slab floor, through a sump lid connection, or beneath a plastic sheet in a crawl space. Attached to the pipe is a quiet, continuously operating fan that discharges the radon outdoors.
The system's design depends on the construction of the home, rather than the indoor radon concentrations. For example, a home with more than one foundation can present challenges to collecting the soil gas from under all portions of the building. However, trained mitigation contractors can sometimes connect multiple systems together so that only one fan system is required.
This kind of mitigation system also helps reduce moisture in the crawl space.
A length of perforated pipe is laid on top of the soil running the length of the crawl space. The pipe will collect the radon from beneath the plastic sheeting when connected to a fan.
Perforated pipe used to collect soil gas laid on floor of crawl space
A high density, cross laminated polyethylene sheeting is then laid on the soil. This type of sheeting is very durable and resists tearing.
High density polyethylene lay on dirt with edges and seams sealed
The seams should be overlapped and sealed. The edges should also be sealed to the walls of the crawl space, to ensure system efficiency and to help keep the plastic stationary. The use of a durable plastic prolongs the life of the system and may allow storage in the crawl space.
After the plastic has been installed, a solid PVC pipe is connected to the perforated pipe beneath the plastic. The PVC pipe is then routed to the radon fan.
At least one four to six inch hole is cored (drilled) through the slab. A small pit is hollowed out beneath the hole, and a PVC pipe is inserted. This pipe is routed to a fan that creates a vacuum beneath the slab. The number of suction points depends on the permeability of the soil beneath the slab and the number of footings within the building.
A single radon vent pipe is often all that is required in a residence. A general "rule of thumb" suggests the use of one vent pipe for roughly ever 2,000 square feet of floor space at ground level.
For a home that has a slab-on-grade or a basement, suction through a hole in the slab is applied. Radon-laden soil gas is drawn laterally through the rock and soil beneath the slab and then exhausted outside. The more permeable the soil, the better the system works.
If the soil is tightly compacted or if there are obstructions such as intermediate foundations under the slab, more than one suction point may be needed. If multiple suction points are needed, they can often be connected to a single depressurization fan.
Homes that have sumps or French drains for control of rainwater can be effectively mitigated utilizing the sump to collect radon from the underlying
soil. Two types of drainage systems can be readily adapted to collect radon from the soil below a house and exhaust it safely outside.
When the drainage system includes a sump, a lid with vent piping is placed on the sump pit. A radon fan connected to the vent pipe is used to draw radon from the soil and through the sump, to an outside exhaust point above the home's roof. When placing a lid on the sump pit, it is important to remember to allow for future removal of the lid, to allow servicing of the sump pump.
The second technique for using a drainage system works well when there is no sump but a foundation drain is in place that runs to daylight. A saddle can be used to tie into the drain and connect it to a pipe and fan. The pipe continues to a safe discharge point. Special check valves are used to seal the daylight end of the foundation drain. These check valves allow the fan to create a vacuum at the same time they allow water to drain. When using a drainage system to collect radon it is important to maintain the drainage characteristics of the drainage system.
In some homes, return-air ductwork for the forced-air conditioning system is located beneath a slab floor. Although this can increase usable interior space and reduce the noise of recirculating air inside the home, the sub-floor ductwork, if unsealed, can add to radon problems. When the air conditioner fan is on, a fairly large vacuum created in the buried ductwork can draw radon-laden soil gas through the ducts and into the living space.
Even with this type of construction, there are effective ways to reduce radon. For example, if a house has a sump, a four-inch pipe connected to a sealed lid on the sump can route incoming soil gases to the radon fan. If the house has a perimeter foundation drain (French Drain), the vent pipe can be connected to the drain, taking care not to interfere with water drainage or sump pump function.
However, many homes have a slab floor; most of them without sumps or French Drain. For those houses, radon drawn inside through sub-floor ducts may require extra attention.
Radon laden soil can be drawn into a home through very small openings in the ductwork, especially when a forced air unit sits over a large opening in the slab.
Not all homes that have air return ducts under the slab floor will have radon concerns. The only way to know is to test. If a long-term test confirms elevated radon levels in a home that also has under-slab air returns, the following options should be considered.
This is the last resort and very expensive. Although some contractors may recommend this solution first, it may be prudent to explore a few other options before replacing ductwork.
| Pipe Material | PVC or ABS |
| Thickness | Schedule 40 |
| Pipe Rating | DWV (Cellular Core) |
| Size | Four Inch |
Slope pipe back to suction point to avoid build up of condensation (1/8" per foot)
Support pipe every eight feet, vertically and every six inches horizontally
Place "Radon Deduction System" label on pipe on each level where visible
Two 45 degree fittings can be used to offset pipe
When penetrating fire walls with vent pipe, maintain fire wall rating with fire collars or appropriate fire caulk
Allow 30" of vertical space for installation of the fan in an attic
downspout (3" x 4") is used outside for aesthetic reasons
The suction piping is connected to a radon fan that must be located in an unoccupied attic, a garage, The suction piping is connected to a radon fan that must be located in an unoccupied attic, garage, or outside the home. These fans are quiet and use about 60 watts of electricity. Because radon is constantly generated in the soil beneath the home, the fans should operate continuously.
The fan discharge is routed through the roof or along an outside wall to a high point on the house. It must be pointed upward to force the collected radon up and away from the home. It is very important that the discharge not be near the ground. Otherwise, the radon might re-enter the structure and increase the level of radon in the home. Radon concentrations in excess of 2000 pCi/L have been measured in some discharge pipes.
Rain caps interfere with system efficiency and are not needed. However, screens should be placed on the discharge to keep birds and squirrels from entering the pipe.
As part of the installation of a depressurization system, an indicator must be installed which will tell the homeowner if something has changed the performance of the system. This is in addition to retesting the home for radon after the installation and repeating this test at least every two years.
Since it is the decay products of radon that actually present the risk from elevated radon levels, some homeowners have installed high efficiency air filters (HEPA) in their homes to not only reduce the the amount of decay products, but also to reduce other airborne particulates that can complicate allergies. The reduction of radon by air filtration systems is a relatively new approach that can be accomplished by three different methods, depending upon the type of heating or air conditioning system you presently have.
| Heating or A/C System | Approach |
|
Connect air filtration system to return duct in a manner that takes a portion of the air stream, filters it and re-injects it into the return duct. |
|
Install a stand-alone central HEPA filtration system that circulates air from the interior of the home, filters it and routes it back into the home. |
|
Install console unit HEPA filter systems for each frequently occupied room. |
Although it is typically more common that an active soil depressurization systems is installed, if you have allergies and your radon levels are relatively low, you may want to consider this approach. If you do, it is important to note the following:
The cost of a radon mitigation system installed by a certified contractor can be $2,000 or more, although EPA often cites a national average of $1,200 to $1,500. The actual cost may depend on the contractor, the construction and foundation type of the home, location of the home site, and aesthetic factors. For instance, a vent-pipe system routed outside of the home may cost less to install than one routed through an interior closet and attic space. EPA suggests that you obtain bids from certified contractors and compare costs.
The cost of a mitigation system may vary according to the home's design, size, foundation, construction materials and the local climate.
Part of the mitigation cost can depend upon what is required to conceal the system and maintain the aesthetic value of the home. For example, a retrofit system routed outside the house can reduce radon quite well, but it may not be as visually pleasing as one routed through an interior closet.
| Average U.S. installation cost: | $1,200 |
| Average operating cost: | $3 / month |
| Expected life span of fan: | 11 years |
| Fan replacement cost: | $145 - $300 |
| Periodic maintenance: | None |
To find qualified radon contractors, EPA recommends that you contact one or both of the two privately-run national certification programs listed below.
National Environmental Health Association
National Radon Proficiency Program (NEHA NRPP)
PO Box 2109; Fletcher, NC 28732
800-269-4174; 828-890-4117
National Radon Safety Board (NRSB)
PO Box 703; Athens, TX 75751
866-329-3474; 903-675-3748
www.nrsb.org
In addition to asking about a radon contractor's training and credentials, homeowners should always:
Some homebuilders add construction elements to new homes that help make the homes radon-resistant. Some go so far as to install a full system with fan, even though building codes in most areas do not specifically require radon-resistant construction features. In some states, some homebuilders include radon-resistant construction elements as a value-added feature, or when requested by homebuyers.
There are advantages to installing a system when building a house:
The piping can be easily concealed in a chase;
The vent pipe can exit the roof and appear as a normal roof penetration;
The sub-grade can be prepared to make it easy to collect radon; and.
In many cases these systems work passively without need for fans.
This figure illustrates the basic concept of a typical "soil depressurization" radon control system installed during the construction of a home. These systems draw radon and other soil gases from beneath the floor and upward through a pipe that exits above the roof. Soil air travels readily through the layer of gravel or sand that usually forms the base for a concrete slab.
Other options include a soil-gas collection system consisting of a loop of perforated plastic pipe buried inside the foundation footing, or a loop of gas-permeable matting laid on the sub-grade material directly under the slab and connected to a riser pipe.
The pipe riser should be routed through the interior of the building if possible, to allow the riser to be warmed, thus creating a natural stack effect. When this riser is combined with the gas-collecting system component installed below the slab, it can draw significant amounts of radon from beneath the home. The performance of this natural convection system is enhanced by sealing openings in the slab and walls so the air drawn up through the system comes from beneath the building rather than from within the building.
The efficiency of these passive systems is further enhanced when the riser pipe is routed through the warmest spaces in the home, such as the wall-cavity plumbing chase where the furnace and/or hot water flues are located. The radon vent should be dedicated only the radon reduction system and must not be connected to any combustion flues. Allowance is always made for adding a suction fan to the vent pipe, usually in the attic area, if needed later to increase system capabilities.
This passive-system approach is usually not chosen for retrofit mitigation of homes, because existing houses lack the specialized gas-collecting system component, such as perforated pipe, that is installed ony during new construction. Test the home to be sure it reduces the radon to levels you desire.
Ask your builder about radon resistant features; and if a system is installed.
See below for EPA publications with more information.
| Attachment | Size |
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| buildradonout.pdf | 5.52 MB |
Downloadable Copy Below
This checklist provided by the EPA can help ensure accurate radon test results will be obtained. Radon testing is not a complicated process, but must be done properly. Otherwise, the test results may not be accurate and more testing may have to be done. Disturbing or interfering with the test device or the closed-house conditions will invalidate the test results.
The seller or a certified tester should be able to confirm that all the items in this checklist have been followed. If the tester cannot confirm this, another test should be performed.
EPA's Testing Checklist
Before the radon test:
During the radon test:
After the radon test:
Downloadable Copy Below
The EPA's Consumer's Guide to Radon Reduction provides the following guidelines for dealing with a radon mitigation contractor:
Choose a contractor to fix a radon problem just as you would choose someone to do other home repairs. It is wise to get more than one estimate, to ask for references, and to contact some of those references to ask if they are satisfied with the contractors' work. EPA suggestions for finding qualified radon contractors can be found at the end of the following checklist.
The Contract
Ask the contractor to prepare a contract before any work starts. Carefully read the contract before you sign it. Make sure everything in the contract matches the original proposal. The contract should describe exactly what work will be done prior to and during the installation of the system, what the system consists of, and how the system will operate. Carefully consider optional additions to your contract which may add to the initial cost of the system, but may be worth the extra expense. Typical options might include a guarantee that the contractor will adjust or modify the system to reach the promised radon level, or, an extended warranty and/or a service plan
Elements that should be included in the contract:
| Attachment | Size |
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| Testing_Checklist.pdf | 23.53 KB |
| Contractor_Checklist.pdf | 24.36 KB |

Why should I be concerned?
It has been shown in carefully controlled studies on animals, and on hard-rock miners, and most recently confirmed in residential case-control studies, that the effects of the radon decay products (due to prolonged exposure to elevated levels of radon) can significantly increase the potential of lung cancer. Radon is regarded as a Group A carcinogen; that is, it is known to cause cancer in humans with prolonged exposure. Many buyers are concerned about their health risk, as well as property resale value and want to test for and correct radon concerns. The United States Environmental Protection Agency and Surgeon General recommend that people not have long-term exposures in excess of 4.0 pico Curies per liter (pCi/L).
If I find a home with a radon problem should I look for another home?
The presence of high levels of radon should not keep you from buying the home of your dreams. If a properly performed test indicates an elevated level of radon in the home you wish to purchase, it is likely other homes in the same area will have elevated radon. So, if you like the house, consider taking a reasoned approach that will confirm levels and reduce the radon. Perhaps the best news about radon is that radon can be reduced, either before you buy the home, or after you buy it and move in. Of all the problems a house may have, radon is one of the easiest to identify and fix!
Over the last 15 years, reliable testing devices and methods have been developed to determine indoor radon exposures. When using approved measurement devices, you can either determine the radon potential over a short period of time, or an average of radon exposure over a longer period of time.
This is a short-term test, typically 2-5 days. It is conducted under closed building conditions 12 hours prior to and all during test. The test device is deployed on the lowest occupiable level of the home. This is commonly used at time of resale.
This is a long term test, at least 91 days, up to one year. It is conducted under normal lived-in conditions without special closed building conditions. The device is deployed on lowest occupied level of home. It is commonly used outside of a real estate transaction, or used as the basis of escrow fund release, especially if a short-term test has shown results between 4 and 10 pCi/L.
Yes, radon can dissolve in the groundwater and be released into the air of the home when it is used for showers, laundry, and other purposes. The concern with radon in water is not widespread and is primarily associated with homes whose water supplies are from wells or public water supplies that use groundwater. The major concern is not with drinking the water, but rather with the additional amount of radon added into the breathing space beyond that which comes from the soil. Normal radon in air tests will measure this contribution, if the house is occupied during testing. It takes a lot of radon in the water to have a measurable effect on the indoor radon concentrations. As a rule of thumb, it takes 10,000 pCi/L in the water to add one additional pCi/L of radon in the air. So always test the air first, before testing or becoming concerned with radon in the water. Your radon testing professional should be able to provide guidance.
Radon is mitigated by installing a system that will draw the radon-laden soil gas from beneath the foundation and exhaust it outside of the building, far enough away from windows and other openings that it will not reenter. A mitigation system typically consists of a plastic pipe connected to the soil either through a hole in a slab, via a sump lid connection, or access beneath a plastic sheet in a crawl space. Attached to the pipe is a quiet, continuously operating fan that discharges the radon outdoors.
The type of mitigation system is a function of the construction of the home, rather than the radon concentrations that exist. A home with more than one foundation can present challenges to collecting the soil gas from under all portions of the building. However, talented mitigation contractors typically can connect multiple systems together so that only one fan system is required. Crawlspace foundations can be more costly, since the contractor needs to install a high density plastic sheet over the soil, seal it to the walls and then route the piping to the fan. However, the added benefit of reducing moisture in the crawlspace, in addition to reducing radon, can be a real plus.
The cost of a mitigation system is a function of the extra effort taken by the contractor to conceal the system and to maintain the aesthetic value of your home. Although a system routed up the outside of the house will reduce radon quite well, it may not be as aesthetically pleasing as one that was routed through the interior of the house with trim installed to conceal it. An increasing number of buyers are getting involved in how these systems will be installed, or waiting until they occupy the house to better control the manner in which their system will be installed.
Most states recognize qualified credentialing organizations that certify radon measurement and mitigation professionals as well as analytical laboratories. Lists of these trained individuals can be found on the websites indicated below. In addition, your state may also have a listing on the state public health department website. Homeowners should also ask for references; require proof of certification, including agreement to follow protocols and codes of ethics; ask for proof of insurance including workers' compensation; and ask for a clear contract with details of guarantee and warranty.
Credentialing organizations:
Protecting Your Home From Radon© (2nd Edition)
The first edition of this book was written in 1993, to assist what was thought to be an occasional do-it-yourself homeowner. In reality, the number of individuals wanting to reduce radon levels themselves was much higher than anticipated. In addition, the manual was being utilized to better understand the radon mitigation process prior to hiring a contractor, and to design systems installed into homes during construction.
The overwhelming success of the book led to the distribution of several thousand copies to individuals and libraries. Its popularity identified the need to address the process of hiring contractors and installing passive and active systems in new home construction. The second edition, now readily available, has these two substantive additions.
This detailed manual describes the most common methods for reliably reducing radon in a home. Written in a non-technical format, the book includes step-by-step instructions and illustrations to guide homeowners through the radon mitigation process.
Cost $29.95
| Purchase |
| Chapter 1: Health Effects A discussion of the risks associated with radon. |
Chapter 7: Piping Systems A description of the fans, piping, and indicator systems that are connected to the three ASD systems detailed in Chapters 4, 5 and 6. |
| Chapter 2: Measurements A summary of the most common measurement methods. |
Chapter 8: Caulking and Sealing How caulking and sealing are used to improve the performance of ASD systems and reduce both operating costs and the potential for backdrafting. |
| Chapter 3: Radon Entry An explanation of radon entry and how it is minimized by mitigation systems that employ active soil depressurization techniques (ASD). |
Chapter 9: Combining Approaches How a combination of approaches is used in homes with multiple types of foundations. Phasing and alternate technologies requiring contractors are described. |
| Chapter 4: Crawl Space Systems A detailed description of how sub-membrane depressurization systems are installed in homes with crawl spaces. |
Chapter 10: Safety An in-depth discussion of safe installation practices, including personal protective gear and area ventilation. The need to check for backdrafting and post-mitigation radon testing is emphasized. |
| Chapter 5: Drainage Based Systems How existing sups and drain tiles can be modified for cost-effective radon reduction. |
Chapter 11: New Home Systems How to install cost-effective radon control systems during new home construction. |
| Chapter 6: Sub-Slab Systems How sub-slab depressurization systems are designed and installed in basement, slab-on-grade and multi-level homes. |
Chapter 12: Selecting a Contractor For people who want to make an educated decision about hiring a contractor to perform all or part of a mitigation system. |
The US EPA is a great resource for information and publications. The publications indicated below are available for download by clicking on the "PDF Version" link next to the description.
For more publications and other EPA resources, go to www.epa.gov/radon/pubs
Home Buyer's and Seller's Guide to RadonThis booklet is intended for anyone who is buying or selling a home, real estate and relocation professionals, home inspectors and others. [EPA 402-K-06-093, November 2006] PDF Version (PDF, 43 pp, 1MB) |
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A Citizen's Guide to RadonThe guide to protecting yourself and your family from radon. PDF Version (PDF, 16 pp, 859KB) |
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Consumer's Guide to Radon ReductionHow to Reduce Radon Levels in Your Home... PDF Version (PDF, 20 pp, 602KB) |
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A Radon Guide for TenantsThis guide, created by the Environmental Law Institute (ELI) with EPA's review, is for people who rent their apartments or houses. The guide explains what radon is, and how to find out if there is a radon problem in your home. The guide also talks about what you can do if there are high radon levels in your home. [EPA 402-K-98-004, 1996] PDF Version (PDF, 10 pp, 50 KB) |
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Building Radon Out: A Step-by-Step Guide on How to Build Radon-Resistant HomesThis 81-page, fully illustrated guide contains all the info you need in one place to educate home builders about radon-resistant new construction (RRNC), including: Basic questions and detailed answers about radon and RRNC; Specific planning steps before installing a system; Detailed installation instructions with helpful illustrations; Tips and tricks when installing a system, Marketing know-how when dealing with homebuyers; and, Architectural drawings. [EPA 402-K-01-002, April 2001] PDF Version (PDF, 84 pp, 5.52MB) |
To Order EPA Publications:
You can order Indoor Air Quality publications from EPA's National Service Center for Environmental Publications (NSCEP):
U.S. Environmental Protection Agency
National Service Center for Environmental Publications (NSCEP)
P.O. Box 42419
Cincinnati, OH 45242-0419Website: www.epa.gov/nscep
Phone: 1-800-490-9198
Fax: (301) 604-3408
E-mail: nscep@bps-lmit.com
NSCEP operates a Toll-free phone service for EPA Publication assistance with live customer service representative assistance Monday through Friday from 9:00am-5:30pm eastern time. Voice Mail is available after operating hours. You can fax or e-mail your publication requests. For technical assistance with NSCEP web pages, write to: nscep_nepis.tech@epa.gov. Indicate the EPA Document Number, which is bolded, when ordering from NSCEP.