Radon: Exposure and Hazards

The World Health Organization (WHO) and the US Department of Health and Human Services, as well as EPA, have classified radon as a "Class A" known human carcinogen, because of the wealth of biological and epidemiological evidence and data showing the connection between exposure to radon and lung cancer in humans.

Radon is an odorless, colorless and chemically unreactive inert gas, which is the densest gas known (nine times denser than air). Radon is not produced as a commercial product. Radon is a naturally occurring radioactive gas and comes from the natural breakdown (radioactive decay) of uranium. Most soils contain varying amounts of uranium. It is usually found in rocks and soil, but in some cases, well water may also be a source of radon.

Radon is also fairly soluble in water and organic solvents. Although reaction with other compounds is comparatively rare, it is not completely inert and forms stable molecules with highly electronegative materials. Radon is considered a noble gas that occurs in several isotopic forms. Only two are found in significant concentrations in the human environment: radon-222, and radon-220. It is radon-222 that most readily occurs in the environment. Atmospheric releases of radon-222 results in the formation of decay products that are radioisotopes of heavy metals (polonium, lead, bismuth) and rapidly attach to other airborne materials such as dust and other materials facilitating inhalation.

The radon gas and its highly radioactive metallic products emit alpha and beta particles and gamma rays. Because it is a single atom gas (unlike oxygen, which is comprised of two atoms) it easily penetrates many common materials like paper, leather, low density plastic (like plastic bags, etc.) most paints, and building materials like gypsum board (sheetrock), concrete block, mortar, sheathing paper (tarpaper), wood paneling, and most insulation.


Depending on the geographic location, climate and seasonal changes Radon gas may be a problem in some homes. When the air containing radon is inhaled, it is possible to increase the risk of getting lung cancer. In fact, radon is the second leading cause of lung cancer in the
United States today. The risk of lung cancer becomes especially high for a cigarette smoker whose home has high radon levels.

Radon is a national environmental health problem. Elevated radon levels have been discovered in virtually every state. The EPA estimates that as many as 8 million homes throughout the country have elevated levels of radon. State surveys to date show that 1 out of 5 homes has elevated radon levels. Radon seeps into homes from the surrounding soil through cracks and other openings in the foundation. Indoor radon has been judged to be the most serious environmental carcinogen to which the general public is exposed. Based on current exposure and risk estimates, radon exposure in single-family houses may be a causal factor in as many as 20,000 of the total lung cancer fatalities which occur each year. Radon decay products (polonium) can attach to the surface of aerosols, dusts, and smoke particles which may be inhaled, and become deeply lodged or trapped in the lungs. Once lodged, they can radiate and penetrate the cells of mucous membranes, bronchi, and other pulmonary tissues.

A family whose home has radon levels of 4 pCi/l is exposed to approximately 35 times as much radiation as the NRC allows if they were standing next to the fence of a radioactive waste site. (25 mrem limit, 800 mrem exposure)

An elementary school student that spends 8 hours per day and 180 days per year in a classroom with 4 pCi/l of radon will receive nearly 10 times as much radiation as the NRC allows at the edge of a nuclear power plant.(25 mrem limit, 200 mrem exposure)

Most United States Environmental Protection Agency (EPA) lifetime safety standards for carcinogens are established based on a 1 in 100,000 risk of death. Most scientists agree that the risk of death for radon at 4 pCi/l is approximately 1 in 100.

Routes of Entry:

The primary routes of potential human exposure to radon are inhalation and ingestion. Radon in the ground, groundwater, or building materials enters working and living spaces and disintegrates into its decay products. In comparison with levels in outdoor air, the concentrations of radon and its decay products to which humans are exposed in confined air spaces, particularly in underground work areas such as mines and buildings, are elevated. Although high concentrations of radon in groundwater may contribute to human exposure through ingestion, the radiation dose to the body due to inhalation of radon released from water is usually more important.

Exposure:

Concentrations of radon decay products measured in the air of underground mines throughout the world vary by several orders of magnitude. The average radon concentrations in houses are generally much lower than the average radon concentrations in underground ore mines. Workers are exposed to radon in several occupations. Underground uranium miners are exposed to the highest levels of radon and its decay products. Other underground workers and certain mineral processing workers may also be exposed to significant levels. Exhalation of radon from ordinary rock and soils and from radon- rich water can cause significant radon concentrations in tunnels, power stations, caves, public baths, and spas.

Some scientific studies of radon exposure indicate that children may be more sensitive to radon. This may be due to their higher respiration rate and their rapidly dividing cells, which may be more vulnerable to radiation damage.

Radioactivity :
The rate of disintegration of a radioactive substance is commonly designated by its half-life, which is the time required for one half of a given quantity of the substance to decay.

For example, if you had a two liter bottle (think of the large soda bottle in the fridge) that was filled with radon gas and then tighly sealed, at the end of one half-life (approximately 92 hours or almost 4 days) there would only be one liter left in the bottle.

Another issue to consider is the *unusual* property of the radioactive decay chain of uranium/radium/radon. What makes this seem unusual is that a gas is produced from a radioactive solid element (a rock) and then the radioactive gas changes back into radioactive heavy metallic particles. This process and their atomic size (extremely small) makes possible the transport of radioactive atoms through a relatively static environment. In other words, radon's extended half-life (it takes about a month for a specific amount of it to decay to almost nothing) provides enough time for the gas to migrate through cracks and crevices in building foundations, then into the internal air volume where it changes into the more harmful radioactive heavy metals.

This gas and the resulting very small metallic particles (so small that they will float in air) move quickly through a building or home, contaminating the air. An analogy that makes this easier to understand is to think how easily some can detect the presence of a smoker in another part of the building or the cooking of coffee or bacon in the kitchen on Sunday morning. In other words, almost nothing will stop this gas from moving from the basement to other parts of a house if it makes its way into the basement in the first place.

Acceptable Level of Radon:

The US EPA has established the "action level" for deciding when you need to "do something" about the radon in your home, school, or work place is 4 pCi/l. pCi/l= picocuries per liter, the most popular method of reporting radon levels. For those interested in the numbers, a picoCurie is 0.000,000,000,001 (one-trillionth) of a Curie, an international measurement unit of radioactivity. One pCi/l means that in one liter of air there will be 2.2 radioactive disintegrations each minute. For example, at 4 pCi/l there will be approximately 12,672 radioactive disintegrations in one liter of air, during a 24-hour period.

Most Commonly Used Radon Testing Method:

There are two main methods used to test for radon gas and radon daughter products. The most popular involves the use of a "passive" device such as an activated charcoal test kit which collects radon gas atoms for counting later in a laboratory or an alpha track device that has a small strip of special plastic that is "marked" when hit by radon's alpha particles (also counted later in a laboratory). Another passive device called an electret has a plastic disc with a static charge. This type is only used by professional radon inspectors because of the expertise required and the expensive equipment needed for analysis.

The other main method involves the use of an "active" device called a CRM (continuous radon monitor). These are mostly used by professional radon inspectors for short-term (two days or 48 hours) radon testing during a real estate transaction. There are many different models of CRMs but they all require some formal training in order to be used properly.


Radon Resistant New Construction (RRNC):

According to the most recent survey of home builders conducted by the National Association of Home Builders (NAHB) Research Center:

  • 18.8% of approximately 1,126,000 single-family detached homes built during 1998 incorporated radon-reducing features, which translates to nearly 212,000 homes. This brings the cumulative total of single-family detached homes built with radon-reducing features since 1990 to over 1.6 million homes, based on the results of previous surveys conducted by the NAHB Research Center.
  • 43.3% of approximately 306,000 single-family detached homes built in Zone 1 (homes with high radon potential) during 1998 incorporated radon-reducing features, which translates to about 132,500 homes. This brings the cumulative total of single-family detached homes built in Zone 1 with radon-reducing features since 1990 to just over 1 million.

Radon Resistant Construction Techniques:

The techniques may vary for different foundations and site requirements, but the basic elements are:

A. Gas Permeable Layer
This layer is placed beneath the slab or flooring system to allow the soil gas to move freely underneath the house. In many cases, the material used is a 4-inch layer of clean gravel.

B. Plastic Sheeting
Plastic sheeting is placed on top of the gas permeable layer and under the slab to help prevent the soil gas from entering the home. In crawlspaces, the sheeting is placed over the crawlspace floor.

C. Sealing and Caulking
All openings in the concrete foundation floor are sealed to reduce soil gas entry into the home.

D. Vent Pipe
A 3- or 4-inch gas-tight or PVC pipe (commonly used for plumbing) runs from the gas permeable layer through the house to the roof to safely vent radon and other soil gases above the house.

E. Junction Box
An electrical junction box is installed in case an electric venting fan is needed later.

 

Figure 1. Radon Resistant Construction Techniques

LINKS:

Radon Awareness for Public Service Professionals

Unit One (31 frames) Introduction to Radon and Radioactivity

Unit Two (23 frames) Radon Entry and Behavior

Unit Three (27 frames)Radon Mitigation System Design and Installation

Model Building Standards and Techniques (EPA Site)

Building A New Home: Have You Considered Radon?

EPA Map of Radon Zones (USA)

EPA Map of Radon Zones (New York State)

 

 Last Update: January 9, 2007

By: Serdar Z. Elgun