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    nbraden@jeffco.us
    303-232-6301

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    645 Parfet Street
    Lakewood, CO 80215

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    645 Parfet Street Lakewood, CO 80215
    303-232-6301
    Fax: 303-239-7088

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    1711 A & B Sheridan Blvd Edgewater, CO 80214
    303-271-5780
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  • Radon Gas

     

    Where does Radon Come From?  |  Health Effects of Radon  |  Radon and the EPA  |  Radon Entry  |  Radon Measurement  |  Radon Mitigation  |  Radon in Water

    Summary

    Radon is a cancer-causing, radioactive gas. It is colorless, odorless and tasteless. When people breathe radon, they increase their chances of getting lung cancer. In fact, the U.S. Surgeon General has warned that radon is the second-leading cause of lung cancer in the U.S. today.

    Radon comes from rocks, soil and well water that contain uranium and radium. Radon is found throughout the United States and is particularly prevalent in Colorado. The U.S. EPA has ranked Colorado as a Zone 1 area, meaning the average house will probably exceed the EPA's action level for indoor radon.

    Testing for radon is easy and inexpensive. Having a radon mitigation system installed by a contractor listed with the National Environmental Health Association (NEHA) or National Radon Safety Board (NRSB) usually costs between $700 and $1,200.

    Where does Radon come from?

    Radon is produced as a decay product from uranium and radium. This naturally occurring radioactive gas is found in most soil, rock and ground water. All buildings contain some radon; as does outdoor air, although at very low levels.

    Since radon is a gas, the inert element can easily travel through cracks and pores without being chemically bound or attached to other elements. Voids and porous materials are found under every building, allowing radon easy entry.

    The radioactive decay process begins with uranium. Uranium decays through several intermediate elements to produce radium and radon. The following diagram illustrates this process:

    U238 > Ra226 > Rn222
    Po218 > Pb214 > Bi214 > Po214 > Pb210

    The decay products from radon are called radon decay products (RDPs) or progeny. These progeny are solids; only radon is a gas.

    Radon has a half-life of 3.8 days, meaning half of the element will decay into RDPs in that time. The RDPs are different from radon because they are short-lived (less than 30 minutes), they have a static charge, they are chemically reactive and are solid particles, which act as aerosols in the air.

    These properties enable RDPs to attach easily to solid objects. If they attach to dust and smoke in the air, they can be easily inhaled into the lungs.

    Units of Radiation

    Radiation from radon and its RDPs is measured in picocuries per liter (pCi/L).
    1 pCi/L = 2.2 disintegrations per minute. Radon is also expressed in working levels (WL) or working level months (WLM). These terms are used in the mining industry and are expressed by the formula: WL = (Rn X ER)/100. A WLM is the exposure to 1 WL for 170 hours, which is assumed to be one month.

    For measurement, most experts assume a .5 ER, which means that half the RDPs plate out (attach) to solid objects, such as walls, and half of the RDPs are in aerosol form, available for inhalation.

    Health Effects of Radon

    Radon is a known human carcinogen. As early as the 1400s, lung disease was associated with metal mining in Eastern Europe. In the 1800s, lung cancer was being reported in miners in the same region. A study of uranium miners on the West Slope of Colorado in the 1950s and 1960s determined RDPs caused lung cancer.

    Radon was found in homes built with radium-containing materials and built on uranium mill tailings in the 1960s. In the 1980s, many homes were found to contain naturally occurring radon.

    Radon and the RDPs are inhaled, and the RDPs attach to the lung lining. Here, they decay, emitting high-energy alpha particles. The main culprits in the RDPs are Polonium-218 and Polonium-214, both of which emit alpha particles that can damage the DNA cells and potentially lead to lung cancer. This is why exposure to radon and its progeny doesn't mean you will contract cancer; but it increases your risk.

    Radon and the EPA

    In 1986, the United States Environmental Protection Agency (EPA) recommended all homes be tested for radon. In 1987, the National Institute for Occupational Safety and Health recommended that exposure for underground miners be reduced from 4 WLM to 1 WLM per year. In 1988, the U.S. Congress enacted the Indoor Radon Abatement Act, which set a national goal to reduce radon in buildings to the ambient level of outdoor air.

    As a result, the EPA set an action level of 4 pCi/L for indoor radon. If radon is found above 4 pCi/L, the EPA recommends people correct this in their homes. There is still some risk at levels below 4, so the EPA suggests that people mitigate their homes, getting them as close to ambient outside air as possible (outside air has approximately 0.4 pCi/L).

    Other countries have adopted different action levels, as listed below:

    Comparison of International Radon Action Levels

    Canada

    • For existing dwellings = 22 pCi/L
    • For new buildings = not established

     

    Finland

    • For existing dwellings = 22 pCi/L
    • For new buildings = 5 pCi/L

     

    Germany

    • For existing dwellings = 8 pCi/L
    • For new buildings = 8 pCi/L

     

    Ireland

    • For existing dwellings = 5 pCi/L
    • For new buildings = 5 pCi/L

     

    Norway

    • For existing dwellings = 22 pCi/L
    • For new buildings = 5 pCi/L

     

    Sweden

    • For existing dwellings = 11 pCi/L
    • For new buildings = 4 pCi/L

     

    Spain

    • For existing dwellings = 11 pCi/L
    • For new buildings = 5 pCi/L

     

    Switzerland

    • For existing dwellings = 5 pCi/L
    • For new buildings = not established

     

    United Kingdom

    • For existing dwellings = 5 pCi/L
    • For new buildings = 5 pCi/L

     

    United States

    • For existing dwellings = 4 pCi/L
    • For new buildings = 4 pCi/L

     

    Radon Entry

    Radium containing soil, rock well water and building materials produce radon. Elevated radon levels within structures depends upon:

    • The strength of the radon source
    • How easily radon is delivered into the structure, and
    • To a lesser degree, the structure's ventilation rates

     

    In most buildings, 95 percent of the radon entering the structure comes from the rock and soil underneath. The radon is pulled into the building by air pressure differentials created by natural and mechanical ventilation. Natural ventilation occurs due to stack effect (hot air rising in the home), wind and temperature differences between inside and outside air. Rain and low barometric pressure can also increase radon entry. Exhaust fans in the home, as well as negative pressure relative to the outdoors caused by heating systems, also increase radon entry.

    These factors cause radon to constantly vary, both daily and seasonally. The highest levels are expected during the winter. We would expect lower concentrations during summer because windows and doors are typically open.

    Well water and building materials may cause radon in homes, but these usually account for less than 5 percent of the radon that enters.

    Radon Measurement

    Even though radon's biological effect is caused by RDPs, radon gas is usually measured, not RDPs. This is because there are fewer variables in radon measurements, since gas concentration is not affected by circulation or plate out, it is easier to make time-weighted measurements of radon gas, and radon gas measurements are a good indicator of RDPs.

    Three basic methods are used for sampling radon:

    • Time-integrated sampling
    • Grab sampling
    • Continuous monitoring

     

    The most common measurement method is time-integrated sampling, where a device is exposed to the radon gas for a measured amount of time. Charcoal canisters and alpha-track devices are typical of passive devices used in most homes. Charcoal devices are usually left out for two to seven days, then sealed and sent to a laboratory where they are analyzed. Alpha-track devices are usually left for longer periods, typically three months to one year. Both types are simple and inexpensive to use.

    Continuous monitors and grab sampling usually require expensive, complex electronic equipment. These require constant calibration to maintain accuracy. Professionals and scientists doing research use this type of equipment.

    For short-term devices, the following protocols should be followed:

    • Closed house conditions must be maintained during the test, and if the test is only two or three days, the house must be closed up 12 hours before the test.
    • The test devices must be placed in the lowest living level of the home. For real estate measurements, an unfinished basement would be tested.
    • The device should not be placed near doors, windows, air currents, sunlight or heat sources. Areas of high humidity should be avoided. Devices should be placed at least 20 inches off the floor, 4 inches from other objects, 12 inches from walls and 12 inches from ceilings.

     

    Results of the test, if above 4 pCi/L, should be verified by either deploying a second device in the same location or by deploying a long-term device.

    The National Environmental Health Association View exit disclaimer policy page for links to third-party websites. and the National Radon Safety Board View exit disclaimer policy page for links to third-party websites. lists people who have taken a course and passed an exam based on measurement protocols and theory. These lists are available from their respective websites or from the Colorado Department of Public Health and Environment. View exit disclaimer policy page for links to third-party websites.

    Radon Mitigation

    Radon mitigation can be accomplished by mitigating one or more of the following factors:

    • Sources of radon in the soil, building material or well water
    • Transport mechanisms that drive radon into a building, usually pressure differentials
    • Radon entry pathways that allow radon to enter a structure, usually cracks or openings in the foundation, or open crawlspaces
    • Accumulation of radon and RDPs in the building.

     

    Of these, controlling radon transport by pressure driven entry is the most common mitigation technique used in Colorado. This is called Active Soil Depressurization (ASD). This technique creates a suction or area of low pressure beneath the structure that is stronger than the partial vacuum applied to the soil by the building.

    ASD systems consist of pipes connected to a fan, which draws gasses from under the building. Radon is captured and vented to the outside before it has a chance to enter the home.

    Several types of ASD systems exist:

    • Sub-slab depressurization systems
    • Drain tile depressurization systems
    • Sub-membrane depressurization systems
    • Block-wall depressurization systems, and
    • A combination of the above methods

     

    All of these ASD systems require expert installation, additional sealing of openings into the home, and of course, testing to verify that radon levels have been reduced to below 4 pCi/L.

    Details of design, location, installation and safety precautions are available in the manual "Protecting Your Home From Radon," D.L. Kladder and Associates., Colorado Vintage Companies, Colorado Springs, CO. This manual is available in all Colorado public libraries and is available at the Jefferson County Department of Health and Environment.

    Professional radon mitigators, like those doing measurements, are also listed by NEHA and NRSB.

    Radon in Water

    Soil gas is the largest natural source of radon in homes; however, well water can be a significant factor if high concentrations of dissolved radon is found.

    High radon levels in water are required to significantly elevate radon in air. The EPA uses a "rule of thumb" of 1:10,000. That is, if you have 10,000 pCi/L of radon in water, you might increase indoor radon concentrations by 1 pCi/L.

    Recent studies indicate that elevated radon levels in water are an inhalation threat and may be an ingestion hazard, increasing the risk of stomach cancer.

    In 1992, the EPA proposed a maximum contaminant level (MCL) of 300 pCi/L for public water supplies. At this time, this MCL has not been promulgated. There is also an alternate MCL being proposed, of 4,000 pCi/L, but what the water supplier must do to be eligible to qualify has not been established. As a result of these proposed MCLs, radon may become the most common treated-for contaminant in well water. In Colorado, radon in well water averages well above the proposed MCL.

    Treatment for Radon in Water

    There are three recognized treatment methods to remove radon from water:

    • Storage of the water until the radon decays
    • Aeration to strip the radon from the water
    • Granular activated carbon filter

     

    Storing water until the radon decays is somewhat impractical  because it takes 27 days for radon to decay (99 percent). A typical family of four using 300 gallons of water per day would need 8,100 gallons of storage. A tank this large is impractical and expensive.

    Aeration is the preferred method for treating radon in water. As the water is aerated, radon is released and piped outside. This method requires another pump to pressurize the pressure tank, a radon fan and biological treatment of the aerated water - becuase it may be contaminated by the air used for aeration.

    Granular activated carbon (GAC) removes radon in water by adsorbing the radon onto the carbon; however, gamma radiation results from the RDPs that accumulate in the filter. To prevent radiation hazards to the occupants, the filter must be shielded or remotely located.

    Other Resources

    Jefferson County Environmental Health Services: 303-271-5700
    Western Regional Radon Training Center: 1-800-513-8332
    Colorado Radon Hot Line: 1-800-846-3986

     

    Last Updated: 4-23-2013