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radon testing

  Radon is a radioactive gas that comes from the breakdown of naturally occurring uranium in soil and rock.  It is invisible, order less and tasteless, and can only be detected by specialized tests.  Radon enters homes through openings that are in contact with the ground, such as cracks in the foundation, small openings around pipes, and sump pump pits.

  Radon, like other radioactive materials, undergoes radioactive decay that forms decay products.  Radon and its decay products release radioactive energy that can damage lung tissue in a away that causes the beginning of lung cancer.

  The more radon you are exposed to, and the longer the exposure, the greater the risk of eventually developing lung cancer.  Radon is the second leading cause of lung cancer in the United States, resulting in 15,000 to 22,000 deaths per year.

  Testing your home for radon is easy and homes with high levels of radon can be fixed (mitigated).  The New Jersey Department of Environmental Protection (DEP) recommends that all homes be tested for radon.

  The US Environmental Protection Agency (EPA) states about 1 in 15 homes has high radon levels.

EPA Map of Radon Zones

Radon Potential of Your Town

  A radon testing device is placed within the home for 2-6 days then mailed to a qualified licensed laboratory. Usually within a week or there after you are  provide with the laboratory results.

Protect your family. Test your home.

Test Your Home for Radon

 

  If high concentrations of radon is found in your home it may be necessary to limit the amount of radon getting into the home by sealing or otherwise obstructing the access points or a mitigation system. Typical radon mitigation systems can cost between $800 and $2500, according to the EPA.

 

The following statement is that of the State of New Jersey, Department of Environmental Protection.

  The Radon Section, as well as the US Environmental Protection Agency, has always stressed that there is no safe level of radon, and that homeowners should reduce their levels as much as possible.

 

CANCER AND RADON

Studies on the carcinogenicity of radon

  Radon's primary hazard arises from inhalation of the gas and its highly radioactive heavy metallic decay products (Polonium, Lead, and Bismuth) which tend to collect on dust in the air. The problem arises when these elements stick to the delicate cells lining the passageways leading into the lungs.

  An IARC Working Group reported that there is sufficient evidence for the carcinogenicity of radon and its decay products in humans. Increased incidences of lung cancer have been reported from numerous epidemiological studies of groups of underground hard rock miners occupationally exposed to high doses of radon. These groups include miners of uranium, iron-ore and other metals, and one group of fluorspar miners. Strong evidence for exposure response relationships has been obtained from several studies, in spite of uncertainties that affect estimates of the exposure of the study populations to radon decay products. Several small case-control studies of lung cancer have suggested a higher risk among individuals living in houses known or presumed to have higher levels of radon and its decay products than among individuals with lower presumed exposure in houses. Regarding lung cancer, the evidence on the interaction of radon and its decay products with cigarette smoking does not lead to a simple conclusion. The data from the largest study are consistent with a multiplicative or sub multiplicative model of synergisms and reject an additive model. In many studies of miners, and in one of presumed domestic exposure, small cell cancers accounted for a greater than expected proportion of the lung cancer cases. In one population of uranium miners, this proportion has been declining with the passage of time. Because of the limited scale of epidemiologic studies of non occupational exposure to radon decay products available at the time reviews were made, quantification of risk has been based only on data of miners' experience. An IARC Working Group considered that the epidemiologic evidence does not lead to a firm conclusion concerning the interaction between exposure to radon decay products and tobacco smoking. Most of the epidemiologic studies involve small numbers of cases, and the analytical approaches for assessing interaction have been variable and sometimes inadequate.

  Peripheral lymphocyte chromosomes from 80 underground uranium miners and 20 male controls in the Colorado plateau were studied. Taken into account were confounding factors such as cigarette smoking and diagnostic radiation. Groups that were increasingly exposed to radon and its decay products were selected. Significantly more chromosomal aberrations were observed among miners with atypical bronchial cell cytology, suspected carcinoma, or carcinoma in situ than among miners with regular or mildly atypical cells, as evaluated by sputum cell cytology.

  There is sufficient evidence for the carcinogenicity of radon and its isotopic forms, radon-222 and radon-220, in experimental animals. When administered by inhalation, preceded by a single exposure to cerium hydroxide dust, radon induced pulmonary adenomas, adenocarcinomas, invasive mixed adenosquamous carcinomas, and squamous cell carcinomas in male rats. Extra pulmonary metastases occurred in only one animal. Most or all of the tumors were believed to be bronchiolar or bronchio-alveolar in origin. In combination with uranium-ore dust, radon decay products induced a progression of activity from single basal cell hyperplasia in bronchioles to malignant tumors in male hamsters exposed by inhalation. Lung tumors observed were adenomas, adenocarcinomas, and squamous cell carcinomas; bronchiolar and alveolar metaplasia . Adenomatous lesions, fibrosis, and interstitial pneumonia were also observed. Radon-induced nasal carcinomas, epidermoid carcinomas, bronchio-alveolar carcinomas, and fibro sarcoma were observed in dogs of both sexes that had been administered, by inhalation, radon decay products, uranium-ore dust, and cigarette smoke. A significant increase in respiratory tract tumors was observed in rats and dogs compared to unexposed animals. A dose-response relationship was noted in experiments with rats in which radon was tested. In most instances, tumors at sites other than the lung were not reported, but one study has mentioned tumors of the upper lip and urinary tract in rats.

 

 

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