ATSDR -Radon Toxicit Radon-1

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    AGENCY FOR TOXI C SUBSTANCES AND DI SEASE REGI STRY

    CASE STUDI ES I N ENVI RONMENTAL MEDI CI NE ( CSEM)

    Radon Tox ici t yCourse : CB/ WB158 5

    CE Or i g i na l D ate : 06 / 01 / 2010CE Exp i r a t i on Da te : 06 / 01 / 2012

    Key Concep ts The U. S. Environmental Protection Agency estimatesthat indoor radon exposure may result in 21,000lung cancer deaths annually in the United States.

    Radon may be second only to smoking as a cause oflung cancer. Increased use of medical radiation also

    contributes to the annual radiation dose. The combination of smoking and radon exposure results

    in a higher health risk. Current technology can easily decrease the

    concentration of radon in indoor air, and radonsassociated risk for producing lung cancer.

    Abou t T h i s

    and O t he rCase Stud ies

    inEnv i r onm en t a l

    Medic ine

    This educational case study document is one in a series of

    self-instructional modules designed to increase the primarycare providers knowledge of hazardous substances in theenvironment and to promote the adoption of medicalpractices that aid in the evaluation and care ofpotentiallyexposed patients. The complete series ofCase Studies inEnvironm ental Medicineis on the ATSDR Web siteat: http://www.atsdr.cdc.gov/emes/topics/. In addition, thedownloadable PDF version of this educational series andother environmental medicine materials provide content inan electronic, printable format, especially for those who maylack adequate Internet service.

    H o w t o A p p ly

    f o r and

    Receive

    See Internet address: http://www2.cdc.gov/atsdrce/ formore information about continuing medical educationcredits, continuing nursing education credits, and other

    http://www.atsdr.cdc.gov/emes/topics/http://www2.cdc.gov/atsdrce/http://www2.cdc.gov/atsdrce/http://www.atsdr.cdc.gov/emes/topics/
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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    C on t i nu ing continuing education units.Educat ion

    Credi t

    A c k n o w l e d g em e n t s We gratefully acknowledge the work that the medical writers,editors, and reviewers have provided to produce thiseducational resource. Listed below are those who havecontributed to development of this latest Case Study inEnvironm ental Medicineversion.

    Please Not e: Each content expert for this case study hasreported no conflict of interest that would bias the case studycontent.

    CDC/ ATSDR Author ( s ) : Oscar Tarrag, MD, MPH, CHES

    CDC/ ATSDR Plan ner s: Charlton Coles, Ph.D.; John Doyle,MPA; Kimberly Gehle, MD, MPH; Sharon L. Hall, Ph.D.;Michael Hatcher, DrPH; Ronald T. Jolly; Trang Nguyen, MPH;Barbara M. Riley, RN; Delene Roberts, MSA; Oscar Tarrag,MD, MPH, CHES; Brian Tencza, BS, MEd.

    CDC/ ATSDR Cont r ib ut ors : Sam Keith, MS, CHP

    CDC/ ATSDR Ext ern a l Peer Rev iew : Jonathan M.Samet, MD, MS.; Mark Upfal, MD.

    Disc la imer CDC, our planners, and our presenters report no financialinterests or other relationships with the manufacturers ofcommercial products, suppliers of commercial services, orcommercial supporters.

    Presentations include no discussion of the unlabeled use of aproduct or a product under investigational use.

    No commercial support was received for this activity.

    U.S. Depar t m ent o f Hea l th and Hum an Serv ices

    Agency fo r Tox ic Substan ces and Disease Regis t r y

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    Div ision o f Tox ico logy and Env i ron m enta l Med ic ine

    Env i ron m ent a l Medic ine and Educat iona l Serv i ces

    Branch

    Table of Contents

    How to Use This Course ....................................................................... 4

    What are the Potential Health Effects from Exposure to Increased Levels ofHow do you Clinically Assess a Patient Potentially Exposed to Increased How Should Patients Potentially Exposed to Increased Levels of Radon Be What Instructions Should Be Given to Patients to Reduce Potential Health

    Annex I: Methods of Detection and Mitigation for Increased Levels ofRadon .75

    Initial Check ....................................................................................... 7What is Radon?................................................................................. 12Where Is Radon Found? ..................................................................... 16What Are the Routes of Exposure to Radon? ......................................... 22Who Is at Risk of Radon Exposure?...................................................... 25What are the Standards and Regulations for Environmental Radon Levels? 34Radon?.............................................................................................37 Levels of Radon?................................................................................41Treated and Managed?........................................................................47 Risks from Exposure to Radon?............................................................50Sources of Additional Information........................................................ 54Assessment and Posttest.................................................................... 59Literature Cited................................................................................. 69Tables and Figures ............................................................................ 74

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    How t o Use Th is Cour se I n t r o d u c t i o n The goal of Case Studies in Environmental Medicine (CSEM)

    is to increase the primary care providers knowledge of

    hazardous substances in the environment and to help inevaluation and treatment of potentially exposed patients.This CSEM focuses on radon toxicity.

    Ava i lab i l i t y Two versions of the Radon Toxicity CSEM are available.

    The HTMLversion http://www.atsdr.cdc.gov/csem/radon/ providescontent through the Internet.

    The downloadable PDF version provides content in anelectronic, printable format, especially for those whomay lack adequate Internet service.

    The HTML version offers interactive exercises andprescriptive feedback to the user.

    I n s t r u c t i o n s To make the most effective use of this course:

    Take the Initial Check to assess your current knowledgeabout radon toxicity.

    Read the title, learning objectives, text, and key pointsin each section.

    Complete the progress check exercises at the end ofeach section and check your answers.

    If you wish to obtain continuing education credit,complete and submit your assessment and posttestresponse online. Continuing education certificates canbe printed immediately on completion.

    I n s t r u c t i o n a l This course is designed to help you learn efficiently. TopicsF orm a t are clearly labeled so that you can skip sections or quickly

    scan sections with which you are already familiar. Thislabeling will also allow you to use this training material as ahandy reference. To help you identify and absorb importantcontent quickly, each section is structured as follows:

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    http://www.atsdr.cdc.gov/csem/radon/http://www.atsdr.cdc.gov/csem/exphistory/docs/exposure_history.pdfhttp://www.atsdr.cdc.gov/csem/exphistory/docs/exposure_history.pdfhttp://www.atsdr.cdc.gov/csem/radon/
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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    Sect ionElement

    Purpose

    Title Serves as a focus question that you should be able toanswer after completing the section

    LearningObjectives

    Describes specific content addressed in each section andfocuses your attention on important points

    Text Provides the information you need to answer the focusquestion(s) and achieve the learning objectives

    Key Points Highlights important issues and helps you reviewProgressCheck

    Enables you to test yourself to determine whether you havemastered the learning objectives

    Answers Provides feedback to ensure you understand the content andcan locate information in the text

    Learn ingObjec t i ves

    On completion of the Radon CSEM, you will be able to

    Cont en t Area Ob jec t i ves

    What is Radon? Explain what radon is, and Describe the main source of human exposure to

    alpha radiation.

    Where is RadonFound?

    Identify the main source of indoor radon, and Describe how you can determine whether you are

    exposed to increased levels of radon in your home.

    What are the Identify the most important route of exposure toRoutes of radon.Exposure toRadon?

    Who is at Risk ofRadon Exposure?

    Identify the population with the highest risk ofexposure to increased levels of radon gas,

    Describe those at risk from exposure to radon as anenvironmental cause of lung cancer deaths, and

    Describe the estimated risk of lung cancer fromradon exposure for persons who smoke cigarettesas compared with those who have never smoked.

    What are the Identify the U.S. Environmental Protection AgencysStandards and (EPA) recommended maximum indoor residentialRegulations for radon level.Environmental

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    Radon Levels?

    What are thePotential Health

    Describe the primary adverse health effect fromexposure to increased radon levels.

    Effects fromExposure toIncreased Levelsof Radon?

    How do you Describe the clinical assessment of a patientClinically Assess a potentially exposed to increased radon levels.Patient PotentiallyExposed toIncreased Levelsof Radon?

    How Should

    PatientsPotentiallyExposed to

    Describe the clinical management of patientspotentially exposed to increased radon levels.

    Describe appropriate referrals for positive findingsduring clinical assessment.

    Increased RadonLevels be Treatedand Managed?

    What InstructionsShould Be Givento Patients to

    Describe instructions to patients on preventivemeasures they can take to reduce potential healthrisks from exposure to radon.

    Reduce PotentialHealth Risks fromExposure toRadon?

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    I n i t i a l Check I n s t r u c t i o n s This Initial Check will help you assess your current

    knowledge about radon toxicity. To take the Initial Check,

    read the case below, and then answer the questions thatfollow.

    Case A 56-year-old homemaker seen at your office has a 3-monthhistory of chronic, nonproductive cough with chest painassociated with the cough. The cough has recently becomeunresponsive to over-the-counter liquid cough suppressants.She denies having

    Shortness of breath, Wheezing, Hemoptysis, Fever, Chills, Sore throat, Hoarseness, or Postnasal drip.

    Her cough is independent of time of day, physical activity,weather conditions, and exposure to dust or householdcleaning agents. Her daughter's cigarette smoke does not

    seem to aggravate the cough. She notes that she has beenfeeling fatigued and, without dieting, has lost 18 poundsover the past 6 months.

    Her past medical history is noncontributory. She is anonsmoker and nondrinker. She does not come in contactwith any known chemical substances or irritants other thantypical household cleaning agents. Her father died at age 65of a myocardial infarction. Her mother had breast cancer atage 71. Her first husband died of a cerebrovascular accident3 years ago. Newly remarried to a retired shipyard worker,

    she and her current husband live with her 28-year-olddaughter and 9-year-old grandson in their New Hampshirehome. She has not been outside the New England area forthe last 5 years.

    Results of the physical examination, including head, eye,ear, nose and throat (HEENT) and chest examination are

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    normal. No cyanosis or clubbing of the extremities, and nopalpable lymph nodes. Blood tests, including a completeblood count and chemistry panel, are normal, with theexception of a total serum calcium level of 12.7 milligramsper deciliter (mg/dL) (normal range: 9.2 to 11.0 mg/dL). A

    chest radiograph reveals, however, a noncalcified,noncavitary 3.5 centimeter (cm) mass located within theparenchyma adjacent to the right hilum. No otherradiographic abnormalities appear. Results of a purifiedprotein derivative (PPD) skin test for tuberculosis arenegative. Urinalysis results are normal.

    I n i t i a l Check 1. Given the clinical findings to this point, which of theQues t ions following is most likely part of the differential diagnosis?

    Choose the one A. Chronic obstructive pulmonary disease (COPD).best answer B. Angina.

    C. Pulmonary Tuberculosis.D. Primary pulmonary malignancy.

    2. What further testing might you order?

    A. Search for previous chest radiographs forcomparison.

    B. Low-dose, computerized tomography (LDCT) scan of

    the lungs.C. Lateral chest X-ray.D. Sputum studies for cytology and cultures (standard

    pathogens, fungus, acid-fast bacilli).E. All of the above.

    3. Which environmental causes have been associated withthis patient's probable disorder?

    A. Daughters smoking and exposure to increased levelsof radon gas.

    B. Persistent organic pollutants.C. Exposure to pesticides from the homes foundation.D. Toxic products in the patients drinking water.

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    I n i t i a l Check

    A n s w e r s1. The best choice is D. Primary pulmonary malignancy.

    The differential diagnosis for the patient's radiographicsolitary pulmonary nodule would include

    Primary pulmonary malignancy, Metastatic malignancy, Granulomatous disease (e.g., tuberculosis,

    coccidioidomycosis, histoplasmosis, nocardiosis), Arteriovenous (av) malformation, Pulmonary hamartoma, Bronchial adenoma, Pulmonary abscess, Pseudonodule (e.g., nipple shadow, superficial

    skin lesion), and Sarcoidosis.

    The following increase the likelihood of a pulmonarymalignancy:

    Radiographic appearance of the lesion (size andlack of calcification),

    Age, Sex (current or former women smokers are at

    higher risk). Symptoms of cough and weight loss, Hypercalcemia, Absence of residence in or travel to an area

    endemic for coccidioidomycosis (southwest UnitedStates) or histoplasmosis (Ohio/MississippiValley),

    Absence of fever or evidence of infectious disease,and

    Negative ppd skin test. The latter does not ruleout tuberculosis, but makes it less likely.

    More information for this answer can be found in theHow Should Patients Potentially Exposed to Increased

    Levels of Radon Be Treated and Managed? sect ion.

    2. The best choice is E, All of the above. At this point,referral to a specialist such as a pulmonologist withexpertise and clinical experience diagnosing, treating,and managing lung disease would be reasonable.Additional testing and care based on the specialists

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    assessment and recommended treatment plan mayinclude further testing with additional referral(depending on the findings) to an oncologist, a chestsurgeon, or both. Initially, one or more of the followingtests might be appropriate:

    Search for previous chest radiographs forcomparison,

    Sputum studies for cytology and cultures(standard pathogens, fungus, acid-fast bacilli),

    LDCT scan, or Fiber optic bronchoscopy with bronchial brushings

    and specimens for cytology and culture.

    If a primary lung cancer is detected, a metastaticworkup (scans of the brain, liver, adrenals, and bones)might be indicated. Again, this would be guided byspecialist care and recommendations.

    More information for this answer can be found in the

    How Should Patients Potentially Exposed to Increased

    Levels of Radon Be Treated and Managed? sect ion.

    3. The best choice is A, Daughters smoking and exposureto increased levels of radon gas.

    Environmental causes of lung cancer may include

    Arsenic http://www.atsdr.cdc.gov/csem/arsenic/, Asbestos, Chloromethyl ethers, Chromium, Ionizing radiation (alpha, beta, gamma, or x-

    radiation), Nickel, Polycyclic aromatic hydrocarbons, Radon, and Tobacco smoke.

    As previously mentioned, referral to and consultationwith a specialist with expertise and experiencediagnosing, treating, and managing lung disease shouldguide treatment options. Referral options might includerecommendations for any additional referrals to an

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    http://www.atsdr.cdc.gov/csem/arsenic/http://www.atsdr.cdc.gov/csem/arsenic/
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    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    oncologist, a chest surgeon, or both. Depending onhistologic type, local extension into adjacent anatomicalstructures, presence of metastases, and the generalhealth of the patient, treatment options might includesurgical excision, radiation therapy, chemotherapy, and

    possibly immunotherapy. Again, specialist care and arecommended treatment plan should guide the choiceof options.

    More information for this answer can be found in the

    How Should Patients Potentially Exposed to IncreasedLevels of Radon Be Treated and Managed? sect ion.

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    W hat i s Radon? Learn ing

    Objec t i vesOn completion of this section, you will be able to

    Explain what radon is, and Describe the main source of human exposure to alpharadiation.

    I n t r o d u c t i o n German physicist Friedrich Ernst Dorn discovered radon in1900 while researching the natural radioactive decay ofradium.

    Radon is a radioactive element. Two of its isotopes (radon220 and radon-222) are progeny in two decay chains thatbegin with naturally occurring thorium and uranium,

    respectively, in rock, soil, water, and air.

    Because radon is a noble gas, it is colorless, odorless,tasteless, and imperceptible to the senses.

    The most common radon isotope is radon-222 (222Rn).The growing popularity of CT scans and nuclear medicine inmedical radiation have replaced radon as the primary sourceof ionizing radiation exposure (NCRP 2009).

    Radon has no commercial uses.

    Except where stated otherwise, this Case Study inEnvironmental Medicine uses radon to refer to radon-222and its progeny.

    D ef i n i t i on Radon (Rn) is a radioactive gas (Lewis 2001) that naturallyoccurs in different forms known as isotopes.

    Radon is a chemically and biologically inert noble gas. Its

    nucleus is heavily neutron-rich, making it radioactive.

    Radon's half-life is 3.8 days. Radon is present in air, water, and soil. Radon will undergo radioactive decay in the

    environment.

    Radon Decay Each parent atom (thorium-234 or uranium-238) decays

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    several times to become a radium atom (Ra-224 or Ra-226),then radon (Rn-220 or Rn-222), and several more timesthrough a series, creating radioactive substances known asradon daughters or progeny. The atom finally decays into astable lead atom.

    As radon progeny undergo radioactive decay, radiation isreleased in forms that include

    High-energy alpha particles, Beta particles, and Gamma radiation.

    Once formed, radons noble gas nature releases it fromchemical bonds in rock, soil, water, and building materials.Radons half-life provides sufficient time for it to diffuse fromits origin and into the atmosphere. This allows for entry intobuildings and homes, where further disintegration producesradon progeny. These progeny tend to be electricallycharged and tend to attach to dust particles.

    Radon progeny include four isotopes with half-lives offewer than 30 minutes. These are the major source ofhuman exposure to alpha radiation (high-energy, high-mass particles, each consisting of two protons and twoneutrons).

    Alpha radiation maydirectly or indirectlydamageDNA and other cell components, which could result inradon-induced lung diseases or cancer.

    Radon and its progeny are measured in different terms forenvironmental/residential and occupational exposures.

    Environmental/residential radon is usually measured interms of its quantity of radioactive material, or activity (inunits of curies or becquerels).

    A curie (Ci) is the amount of air, soil, or other materialin which 37 billion atoms transform each second, and 1Ci = 3.7 x 1010 Bq.

    A Becquerel (Bq) is the amount of material in which 1atom transforms each second.

    Prefixes are often used with these units, [e.g., pCi orpicocurie (10-12 curie)].

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    Occupational radon is measured in terms of working levelsor the total amount of energy imparted to tissue from radonprogeny. EPA recommends limiting indoor residential radonconcentrations to 4pCi/L, which is generally about a 0.016

    working level.

    Radon gas has been identified as a leading cause of lungcancer, second only to cigarette smoking (ACS 2006; EPA2009a).

    Radon gas is responsible for an estimated 21,000deaths from lung cancer annually (NCI 2004; EPA2009b).

    The risk of cancer due to radon exposure is increasedfor smokers, as the radiation emitted by tobaccosynergizes when in the presence of radon gas.

    Key Po in t s Radon is the result of radium atom decay. Radon gas and its progeny are imperceptible to the

    senses. Radon progeny are a significant source of human

    exposure to alpha radiation. In 2009, due primarily to the popularity of CT scans and

    nuclear medicine, medical radiation supplanted radon asthe largest source of exposure to ionizing radiation.

    Alpha radiation may alter cells, which could result inradon-induced lung diseases or cancer. In 2009, radon gas was identified as the second leading

    cause of lung cancer.

    Progress

    Check

    Ques t ions

    Choose theone best

    answer

    1. What is radon?

    A. Colorless, odorless gas imperceptible to the senses.B. Radiation emitted by smoke detectors.C. Ultra violet (UV) radiation from the sun during solar

    explosions.D. The product of decay from nuclear waste.

    2. Of the following choices, which is/are the mostsignificant source of human exposure to alpharadiation?

    A. UV rays from the sun.

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    B. Radiation emitted by smoke detectors.C. Occupational exposures from working in a nuclear

    reactor.D. Radon progeny.

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    Progress

    Check

    A n s w e r s

    1. The correct answer is A. Radon is colorless, odorlessgas imperceptible to the senses.

    To review relevant content, see Definition in this section.

    2. The correct answer is D. Radon progeny are asignificant source of human exposure to alpha radiation.

    To review relevant content, see Radon Decay in this

    section.

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    W here i s Radon Foun d? Learn ing

    Objec t i vesOn completion of this section, you will be able to

    Identify the main source of indoor radon, and Describe how you can determine if you are exposed toincreased levels of radon in your home.

    I n t r o d u c t i o n Radon is a natural product of the environment and theprincipal natural-background, radiation exposure source inthe United States (Krewski et al. 2005).

    Radon gas moves freely through the air, groundwater,and surface water.

    The main source of indoor radon gas infiltration is fromsoil into buildings.

    Due to radon progenys charged state and solid nature, theyrapidly attach to most surfaces they encounter, includingairborne particles (e.g., dust), walls, floors, ventilationequipment, and clothing.

    Increased levels of radon have been identified in every state.

    Only special equipment can detect or measure radon in thehome and in the environment. In 2006, the American CancerSociety estimated 8 million homes in the United States hadincreased radon levels (ACS 2006). The U.S. EnvironmentalProtection Agency (EPA) estimates that approximately 6million homes have concentrations of radon above 4picocuries per liter (pCi/L) (EPA 2009c).

    Soi l and Ai r Radon gas is a ubiquitous element found in rock and soil.The burning of coal and other fossil fuels also releases radon.

    When radon escapes from soil or is discharged from emission

    stacks to the outdoor air, it is diluted to levels that arenormally, but not always, lower than indoor air.

    W a t e r Radon gas in rocks and soil can move to air, groundwater,and surface water. Radon may also enter homes through thewater supply.

    The concentration of radon in water from wells may be

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    higher than that from surface sources. Compared withsurface water, groundwater tends to have more direct andlonger contact with rocks and soil, allowing more of theuranium and thorium decay chain progeny to leach out.

    This may cause increased radon concentrations,especially when the water passes through areas rich inuranium and thorium, such as in Canada and northernNew England.

    In typical municipal water or surface reservoirs, most ofthe radon volatizes to air or decays before the waterreaches homes. Decay of the uranium and radium inthat water results in only a small amount of residualradon.

    Natur a l Gas Radon is also present in natural gas. Natural gas hadpreviously been in contact with underground uranium andthorium-bearing rock and soil that continually release radon.The radon and its progeny remain with the natural gas as ittravels through distribution pipes and into homes. Radon andits progeny are released to breathing air when the gas isburned in

    Fireplaces, Furnaces Heaters,

    Stoves, and Water heaters.

    H om es and

    Bu i l d i ngsEvery state in the United States has homes with measuredradon levels above the EPA recommended concentration.

    All homes should be tested regardless of geographiclocation.

    Homes with increased levels of radon have been foundin all zones.

    Radon can enter the home through

    Diffusion from the ground, Gas appliances, even if they are properly vented, Pressure-driven flow of air in the homethe most

    important mechanismand

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    Water supply, especially from private wells.

    The pressure-driven mechanism occurs when radon escapingthe soil encounters a negative pressure in the home relativeto the soil. This pressure differential is caused by

    Exhaust fans (kitchen, bathroom, and clothes dryers),and

    Rising warm air created byo Fireplaceso Furnaces,o Ovens, ando Stoves

    Basements and crawl spaces under the houses allow moreopportunity for entry of radon gas from soil.

    The U.S. Environmental Protection Agency (EPA) estimatesthat 6%, or approximately 6 million U.S. homes, haveconcentrations of radon above 4 picocuries per liter (pCi/L)(EPA 2009c).

    Radon gas can enter a building and then become trappedindoors. This can especially occur during a temperatureinversion, which reduces radons escape potential from abuilding and thereby increases the indoor radon level.

    The following list and graphics were extracted from EPA2009, A Citizens Guide to Radon (accessed 4-242010), http://www.epa.gov/radon/pubs/citguide.html

    Radon can enter the home through

    1. Cracks in solid floors2. Construction joints3. Cracks in walls4. Gaps in suspended floors

    5. Gaps around service pipes6. Cavities inside walls7. Gas appliances

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    http://www.epa.gov/radon/pubs/citguide.html(accessed%204-24-2010http://www.epa.gov/radon/pubs/citguide.html(accessed%204-24-2010
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    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    Figure 1. Sources of Radon and Common Entry Points

    Radon is also released from materials inside the homes, suchas

    Brick and mortar, Cinder block walls, Concrete floors, Gravel for heat sumps, Sheet rock, and Stone products.

    Cooking with a gas stove and showering are householdactivities during which radon may be released from gas andwater to the air (see water and natural gas above).

    The U.S. Congress has mandated that each state set up anoffice to deal with requests for radon assistance. Many statesprovide free-of-charge radon detection kits such as the

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    charcoal canister.

    Radon

    Tes t ingThe amount of radon emanating from the earth andconcentrating inside homes varies considerably by regionand locality. In 1988, EPA and the Office of the Surgeon

    General jointly recommended that all U.S. homes below thethird floor be tested for radon.

    Currently, the only way to determine indoor radonconcentration is by measuring it.

    Radon only needs to be measured in inhabited areas ofhomes.

    Measurement is the key to identifying the problem.

    Doit-yourself radon detection kits are available inmost hardware stores.

    Radon testing can also be done through a radondetection and remediation company.

    Radon testing is required for all government buildings.

    Additional information is available in Annex I on Homes andBuildings, Methods of Detection, Real EstateTransactions, and EPA Map of Radon Zones.

    Key Po in t s The main source of indoor radon is radon gasinfiltration from soil into buildings.

    Rock and soil produce radon gas. Building materials, the water supply, and natural gas

    can all be sources of radon in the home. Basements allow more opportunity for soil gas entry

    than slab-on-grade foundations. Showering and cooking can release radon into the air

    by aerosolizing household water (from a well) andburning natural gas.

    Currently, testing is the only way to determine indoorradon concentration.

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    Progress 3. What is the main source of indoor radon gas?Check

    Ques t ions A. UV radiation from the sun.B. Radon gas infiltration from soil into buildings.

    Choose the C. Microwave ovens.

    one best D. Acid rain.answer

    4. Which of the following is the best method ofdetermining whether you are potentially exposed toincreased environmental levels of radon in your home?

    A. If you have an earthy/moldy smell in your basement.B. Measuring your homes indoor radon levels.C. Asking neighbors if they have increased levels of

    radon in their homes.D. With a radon-specific blood test.

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    Progress

    Check

    A n s w e r s

    3. The correct answer is B. The main source of indoorradon gas is infiltration from the soil into buildings.

    To review relevant content , see Soil and Airand Homesand Buildings in t his section.

    4. The correct answer is B. The preferred method fordetermining whether you are potentially exposed toincreased environmental levels of radon in your home isby measuring your homes indoor radon gas levels.

    To review relevant content , see Homes and Buildings inthis section.

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    W hat a re th e Rou t es o f Exp osure t o Radon? Learn ing

    Objec t i vesOn completion of this section, you will be able to

    Identify the most important radon exposure route.

    I n t r o d u c t i o n The average person in the United States receives anestimated 625 millirem/year dose from ionizing radiation.The largest percentage is from medical radiation (48%, 300mrem), primarily due to the popularity of CT scans andnuclear medicine. This is followed by radon (37%, 228mrem), which is the largest source of background radiation.While the dose from radon has remained the same over theyears, the percentage that it represents has dropped from55%, based on 1980s data, to 37% using 2006 data. Due to

    the increased use of certain medical procedures, this trend isexpected to continue (NCRP 2009). The dose of ionizingradiation from radon comes from soil, water, natural gas,and building materials.

    The primary pathway for human exposure to radon isinhalation from soil vapor intrusion into dwellings andbuildings. Indoor radon levels can, however, also originatefrom water usage, outdoor air infiltration, and the presenceof building materials containing radium (EPA 2003).

    Dermal exposure is not considered an important exposureroute.

    I n h a l a t i o n The main source of inhalation exposure is radon gas that isreleased from the soil to trapped indoor air.

    Radon is a gas, but its radon progeny are charged andoften attached to dust.

    Radon progeny are present in nearly all air. Radon gas itself is breathed in and out without

    imparting much dose. It is primarily the progeny-carrying dust particulates

    that deposit in the lungs and give a radiation dose tothe lung tissue.

    Background levels of radon in outdoor air are generally quitelow and represent a goal for reducing indoor levels. But

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    radon levels can vary based on location and soil geology.

    In indoor locations, such as homes, schools, or officebuildings, levels of radon and radon progeny are generallyhigher than are outdoor levels. This is especially true of

    newer construction that is more energy-efficient. In newconstruction, indoor radon levels may actually increase, duein part to decreased air entry or exit (i.e., natural ventilationfrom outdoors) in such energy-efficient homes.

    Radon releases from groundwater also contribute toexposure. Radon can be released from water into the air,resulting in inhalation exposure when

    Clothes are washed, Dishes are washed, Toilets are flushed, and Water splashes during showering.

    Radon is released into the air when natural gas or propane isburned in a stove or furnace.

    Because tobacco is naturally sticky, many radon decayproducts actually stick to tobacco products. When smoked orotherwise used, these radon progeny may enter your body.

    I n g e s t i o n Exposure to radon by the oral route can occur as a result ofradon gas dissolving in water. Radon and its progeny arepresent in rocks and soil; the water that contacts the rocksand soil will dissolve out some radon. As such, in mostdrinking water radon and its progeny are naturally present.

    Some radon and its progeny swallowed in drinking waterpass through the stomach walls and intestine (Ishikawa etal. 2003; NAS 1999). Yet radon is biologically inert; after itreaches the lungs, it is readily breathed out throughpulmonary circulation.

    D erm a l Data are very limited regarding the absorption of radonExposure following dermal exposure (ATSDR 2008). Because radon is

    a noble gas, transfer across the dermis should be bydiffusion only and should involve no active transport. Thelayers of dead skin protect the body from exposure to alpharadiation from radon and its progeny. Dermal exposure to

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    radon is not considered a significant exposure route.

    Key Po in t s For the U.S. general public, radon is second only tomedical radiation as the principal ionizing-radiationexposure source.

    Inhalation is the most important radon exposure route. Data are limited regarding the absorption of radon

    following dermal exposure. But dermal is not considereda significant radon exposure route.

    Progress

    Check

    Ques t ion

    Choose theone bestanswer

    5. The most important radon exposure route is

    A. Ingestion.B. Inhalation.C. Dermal contact.D. Endogenous sources.

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    Progress

    Check

    A n s w e r

    5. The correct answer is B. Inhalation is the mostimportant route.

    To review relevant content, see Introduction andI nhalation in t his section.

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    Agency fo r Tox ic Subs t ances and D isease Reg ist r y Radon Tox ic i t y

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    W ho I s at R isk o f Radon Exp osure? Learn ing

    Objec t i vesOn completion of this section, you will be able to

    Identify the population with the highest risk of exposureto increased levels of radon gas,

    Identify those at risk from exposure to radon as anenvironmental cause of lung cancer deaths, and

    Identify the estimated risk of lung cancer from radonexposure for persons who smoke cigarettes ascompared with those who have never smoked.

    I n t r o d u c t i o n Everyone is exposed to radon, but some populationsdescribed in the literature are at higher risk of exposure toincreased radon levels. In addition, some populations are

    more at risk of adverse health effects from radon exposure.

    Radon exposure is, after tobacco smoke, the leadingenvironmental cause of lung cancer death (Copes 2007; EPA2009a). Thus for nonsmokers, radon exposure is the leadingcause of lung cancer death, period (EPA 2009b).

    The risk of lung cancer from radon exposure is estimated atbetween 10 to 20 times greater for persons who smokecigarettes as compared with those who have never smoked.

    Radon

    Exposure

    Dose

    Theory holds that everyone is at risk from radon exposure,and this health risk increases linearly with dose.

    Approximately 6 million homes in the United Stateshave radon levels above 4 picocuries per liter (pCi/L),which is the remediation level EPA recommends.

    Miners in uranium, tin, silver, coal, and other types ofunderground mines may have increased radonexposure. Good ventilation can effectively reduce theincidence of lung cancer in miners.

    The risk of lung cancer from radon exposure isestimated between 10 to 20 times greater for personswho smoke cigarettes as compared with those whohave never smoked. The added risk is unclear regardingmedical exposure, which can exceed that from radon.

    Env i r onm en t a l

    Cau ses ofLung cancer is a leading cause of cancer death worldwide(Wakelee 2007). In the United States, lung cancer remains

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    Lung Cancer

    D ea t hs

    Es t imated

    Risk o f

    Deve lop ing

    Lung Cancerf r om Radon

    Exposure

    the leading cause of cancer death in both men and women.Exposure to tobacco smoke is the leading cause of lungcancer, with active smoking causing most cases. But passivesmoking also contributes to the lung cancer burden.

    Radon exposure is the second-leading environmental causeof lung cancer death, after tobacco smoke (Copes 2007; EPA2009a), and the leading cause of lung cancer death fornonsmokers (EPA 2009b).

    Radon exposure is responsible for about 21,000 lungcancer deaths per year in the United States (NCI 2004;EPA 2007; EPA 2009b).

    Some estimates suggest that approximately 14% of the300,000 annual lung cancer cases in the United States areattributable to radon (EPA 2009b).

    The World Health Organization (WHO) estimates thatradon causes between 6% and 15% of lung cancersworldwide (WHO 2005). Everyone is exposed toenvironmental radon.

    In 1999, the National Research Council of the NationalAcademy of Sciences published the Biological Effects ofIonizing Radiations (BEIR) VI report, Health Effects of

    Exposure to Radon(NAS 1999), which concludes that indoorradon is the second leading cause of lung cancer aftercigarette smoking (NRC 1999; EPA 2003).

    EPA estimates that exposure to high radon levels is theleading environmental cause of death in the United States(EPA 2003).

    EPA estimates that at its recommended guideline of 4 pCi/L,the risk of developing lung cancer for a lifetime exposure toradon is

    1% for nonsmokers, 3% for former smokers, and 5% for smokers.

    These estimates can change based on factors that influencea population groups risk. In determining the risk of radon in

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    homes or offices with the same concentration, assessorsmust consider not only the average level of radon, but alsothe occupants and their lifestyles. For example, the highestradon levels are typically found in the lowest level of thehouse.

    Many factors influence the risk of radon-related lung cancerdue to exposure, such as

    Age during exposure, Duration of exposure, Concentration of radon as a function of age and

    duration, Cigarette smoking, Time spent and concentrations in different portions of

    the home, in transportation routes, and in the office,(e.g., where and how long persons sleep, work, andrecreate).

    Source of water - if well water is the major radonsource, upper floors can be affected more than lowerfloors (e.g., showers),

    Climate and time of yearin colder climates, radonlevels are often higher in the winter and lower in thesummer,

    Static-prone times of yeardegree to which radonprogeny attach to dust particles can increase during

    static-prone times (e.g., in April and October) and, Time elapsed since initiation of exposure.

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    EPA Rado n

    Risk

    Eva lua t ion

    Figure 2 shows the risk of developing lung cancer over alifetime of exposure to radon gas at different exposurelevels. This figure provides risks for both, smokers andnonsmokers, as well as recommended solutions to reducethose levels of exposure and risk.

    Figure 2. Radon risk evaluation chart for smokers andnonsmokers (Modified from EPA 2009)

    Radon l ev e l I f 1 , 000 peop le w ho

    s m ok ed w e re ex pos ed t o

    th is leve l over a l i f e t im e. .. *

    W HAT TO DO:

    St op Sm ok ing

    and. . .

    20 pCi/L About 260 persons could getlung cancer

    Fix your home

    10 pCi/L About 150 persons could getlung cancer

    Fix your home

    8 pCi/L About 120 persons could getlung cancer

    Fix your home

    4 pCi/L About 62 persons could getlung cancer

    Fix your home

    2 pCi/L About 32 persons could getlung cancer

    Consider fixinghome between 2and 4 pCi/L

    1.3 pCi/L

    0.4 pCi/L

    About 20 persons could getlung cancerAbout 3 persons could getlung cancer

    (Reducing radonlevels below 2pCi/L is difficult)

    0 pCi/L Calculated absence of risk Impossible toaccomplish. Thelowest feasibleconcentrationequals outsidebackground.

    Note: If you are a former smoker, your risk may be lower than a currentsmoker.

    * Lifetime risk of lung cancer deaths from EPA Assessment of Risks fromRadon in Homes (EPA 402-R-03-003).

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    Radon l ev e l I f 1 , 000 peop le w ho d id no t

    s m ok e w e re ex pos ed t o

    th is leve l over a l i f e t im e. .. *

    W HAT TO DO:

    Av o id sm ok e

    and. . .

    20 pCi/L About 36 persons could getlung cancer

    Fix your home

    10 pCi/L About 18 persons could getlung cancer Fix your home

    8 pCi/L About 15 persons could getlung cancer

    Fix your home

    4 pCi/L About 7 persons could getlung cancer

    Fix your home

    2 pCi/L About 4 persons could getlung cancer

    Consider fixingbetween 2 and4 pCi/L

    1.3 pCi/L About 2 persons could getlung cancer

    (Reducing radonlevels below 2pCi/L is difficult)0.4 pCi/L

    On average, fewer than 1person (0.7) could get lungcancer

    0 pCi/L Calculated absence of risk Impossible toaccomplish. Thelowest feasiblelevel equalsoutsidebackground.

    Note: If you are a former smoker, your risk may be higher.

    * Lifetime risk of lung cancer deaths from EPA Assessment of Risks fromRadon in Homes (EPA 402-R-03-003).

    Publ ic s

    Assessment

    o f Radon

    Exposure

    Risk

    The public often underestimates the potential risk of cancerdue to radon. This could discourage assessment andabatement measures in the home, as given that the generalpopulation does not see the problem.

    In fact, several studies have noted optimistic biases in thepublic's assessment of radon exposures potential healthrisks. For the most part, the general public thinks radon

    exposure does not pose a risk.

    H o m e

    D w e l l er s and

    I n d o o r R ad o n

    Exposure

    Risk

    An extensive body of literature now addresses the risks ofexposure to indoor radon (NRCC 1999; Darby 2005; Krewskiet al 2005). Populations with the highest nonoccupationalexposure risk to increased radon gas levels include homedwellers, particularly when they dwell in homes that

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    Have high concentrations of radon gas trapped indoors,(i.e., released into the air from soil, water, natural gasuse, and building materials) and,

    Are built with or atop tailings from mines and mills.Chi ld r en andRadon

    Exposure

    Risk

    Due to lung shape and size differences, children have higherestimated radiation doses than do adults. Children also havebreathing rates faster than those of adults.

    Risk of lung cancer in children resulting from exposureto radon may be almost twice as high as the risk toadults exposed to the same amount of radon.

    If children are also exposed to tobacco smoke, the riskof getting lung cancer increases at least 20 times.

    Miners and

    Radon

    Exposure

    Risk

    Among underground miners, radon was the firstenvironmental respiratory carcinogen linked to increasedlung cancer risk. Many epidemiologic studies of those whomine uranium and other ores have established exposure toradon daughters as a lung cancer cause (NRCC 1999). Otherrecognized or suspected carcinogens in mine air include silicadust, cigarette smoke, arsenic, and diesel exhaust particles.

    Miners long-term exposure effects to radon are well known.Investigation is ongoing to determine the potential of othermine air contaminants as study confounders. For example, at

    one mine accounting for arsenic reduced the calculatedradon risk rate by a factor of three (Nourgalieva et al. 2003).

    Accounting for silica would be expected to reduce further thecomputed risk of radon exposure, although this is yet to beattempted.

    As early as the 16th century, Paracelsus and Agricoladescribed a wasting disease in miners. In an 1879investigation of miners in Schneeberg, Germany,Herting and Hesse identified this same condition as lungcancer (ATSDR 2008).

    Since the 1970s, indoor radon daughters have beenwidely recognized as a potential problem in Europe andin Scandinavian countries.

    Due to the high airborne levels of radon and its progeny, themost frequent occupational exposures to radon typically

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    Other Types

    o f W o r k e r s

    and Radon

    ExposureRisk

    result from employment in underground uranium and otherhard- rock mining (NIOSH 2006).

    Although persons engaged in uranium mining are believed toreceive the greatest exposures, the number employed in

    uranium mining in the United States has greatly decreased.

    Additionally, continuous improvements in engineeringcontrols have greatly increased ventilation, thus reducingradon exposure in underground mines (NIOSH 1987).Enhanced ventilation systems have also reduced exposure toother actual and potential carcinogens.

    A list of common occupations with potential for high radonand progeny exposure include employees of

    Excavators, Fish hatcheries, Health mines and spas, Hospitals, Natural caverns (in releases from exposed walls), Natural gas and oil piping facilities, Nuclear waste repositories (in releases from tunnel

    walls), Oil refineries, Phosphate fertilizer plants,

    Fossil fuel power plants (in release to air after fuel isburned),

    Sites radioactively contaminated with radium (becausemost radioactively contaminated sites are notcontaminated with radium, radon is not an issue atthese sites),

    Utility and subway tunnels (in releases from walls),and

    Water treatment plants (in releases during aeration).

    (EPA 2003; Field 1999; Fisher et al. 1996)

    In some areas of the country, higher exposure can also occurto farmers, radon mitigation professionals, and scientistsstudying radon or other radionuclides, although exposure tolocal radon sources can occur in any occupation (Field 1999).

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    Key Po in t s Radon is considered a significant environmental causeof lung cancer deaths.

    Radon gas in homes and outdoors exposes the generalpopulation to radiation.

    The public and medical community often underestimatethe potential risk of cancer due to radon exposure.

    Miners while working in underground mines may be athigh risk of increased exposure to radon.

    Smokers exposed to radon are at greater risk for lungcancer than are nonsmokers similarly exposed.

    Due to differences in lung shape and size and fasterrespiration rates, children receive higher estimatedradiation doses than do adults. These differences placechildren at greater radon-exposure health risk thanadults.

    Progress 6. Which of the following best identifies populations havingCheck the highest risk of exposure to increased levels ofQues t ions radon?

    Choose the A. Women and children living at high altitude.one best

    B. Pregnant women and their fetuses.answer

    C. Elderly people living in Florida.D. People living in homes so tightly sealed for energy

    efficiency that the homes cannot breathe and expelcontaminants.

    7. In 2007, exposure to radon was considered

    A. One of the most important causes of blooddyscrasias.

    B. The most important cause of radiation burns.C. The second most important environmental cause of

    lung cancer deaths.D. An important disruptor of prostaglandins.

    8. What is the relative risk of lung cancer mortality fromradon exposure for people who smoke cigarettes ascompared with those who have never smoked?

    A. 0.8-1.4 times greater.B. 2-4 times greater.C. 5 times greater.D. 10-20 times greater.

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    Progress

    Check

    A n s w e r s

    6. The correct answer is D. Of the answer choices, peopleliving in tightly sealed, energy efficient homes are atgreater risk due to the buildup of high radon gasconcentrations. The quality of home ventilationidentifies a population with greater risk of exposure to

    increased radon levels.

    To review relevant content, see I ntr oduction and Home

    Dwellers and Indoor Radon Exposure Risk in this section.

    7. The correct answer is C. Radon is the second leadingenvironmental cause of lung cancer deaths.

    To review relevant content, see Introduction in this section.

    8. The correct answer is D. The risk of lung cancer fromradon exposure is estimated at 10-20 times greater forpeople who smoke cigarettes as compared with thosewho have never smoked.

    To review relevant content, see Introduction and Radon

    Exposure Dosein t his section.

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    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    W hat a r e the St andard s and Regu la t ion s fo r

    Env i r onm ent a l Radon Leve ls?

    Learn ing On completion of this section, you will be able toObjec t i ves

    Identify the U.S. Environmental Protection Agencys(EPA) recommended maximum indoor residential radonlevel.

    I n t r o d u c t i o n Currently, no federal regulations govern acceptable radonlevels for indoor residential and school environments. Butguidelines are available. EPA based its guidelines not only onrisk considerations, but also on technical feasibility.

    Regulators periodically review radon standards and

    guidelines, and changes may occur over time. Consult EPA orstate health departments for the most up-to-date standards.

    Some estimates are that if homes with radon concentrationsexceeding the EPA action level were to reduce concentrationsbelow that level, approximately one-third of radon-inducedlung cancer could be avoided. Eliminating all radon exposureis, however, not possible (ACS 2006).

    EPA EPA has set guidelines for maximum environmental radonM a x i m u m levels based on limiting the risk of developing lung cancerRecom m ended from radon exposure. EPA has also developed methods forLevel

    Gu ide l inesremediating sites to reduce radon levels effectively.

    The EPA environmental radon level recommends remediationat a maximum of 4 picocuries/liter (pCi/L) of radon in air,with the caveat that radon concentrations below this levelstill carry a risk and in many cases are reducible (EPA2009c).

    For example, an area of a house has concentrations of radon

    between 2-4 pCi/L and this area is inhabited or heavilyusedespecially by children. To minimize potential healthrisks, consider remediating and lowering the environmentalradon level.

    Th e I n d o o r

    Radon

    Aba t em en t

    In October 1988, Congress enacted the Indoor RadonAbatement Act (EPA 1988), which established a long-termgoal of indoor air as radon-free as the ambient, outside air.

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    Act o f 19 88 The law authorized funding for radon-related activities at thestate and federal levels to

    Establish state programs and providing technicalassistance,

    Conduct radon surveys of schools and federalbuildings, Establish training centers and a proficiency program

    for firms offering radon services, Develop a citizen's guide to radon, and Develop model construction standards.

    Tab le 1 . Stand ards and regu la t ions fo r r adon in a i r

    Source* Focus Leve l Com m ents

    Indoor Radon

    Abatement Act

    Indoor air

    (residential)

    Indoor =

    outdoor (~0.4pCi/L

    National goal

    NationalCouncil onRadiationProtection andMeasurements(NCRP)

    Indoor air(residential)

    2 WLM= 8-10 pCi/L ifthe equilibriumratio is 40-50%

    NCRP 1993 Guideline

    (EPA) Indoor air(residential)

    Schools

    4 pCi/L

    4 pCi/L

    Current action level

    Guideline for action

    NIOSH Occupational(mining)

    1 WLM/yearand ALARA

    Advisory; exposure limit

    OSHA Occupational 4 WLM/year100 pCi/Laveraged overa 40-hour workweek

    Regulation20CFR1910.1096

    MSHA Mining 4 WLM/year

    1 WL in active,working mines

    Regulation

    NRC Occupational 7000 pCi/L9 pCi/L4000 pCi/L30 pCi/L

    220Rn w/o daughters220Rn w/daughters222Rn w/o daughters222Rn w/daughters

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    Case Stu d ies in Env i r onm enta l Med ic ine ( CSEM)

    USNRC Annual averageeffluent airconcentration

    20 pCi/L0.03 pCi/L10 pCi/L0.1 pCi/L

    220Rn w/o daughters220Rn w/daughters222Rn w/o daughters222Rn w/daughters

    WHO (2009) Residential 2.7 pCi/L(preferred)8.1 pCi/L (if thelower level isunreachabledue toprevailingcountry-specificconditions).

    Proposed nationalreference level

    * NCRP = National Council for Radon Protection; EPA = U.S. Environmental ProtectionAgency; NIOSH = National Institute for Occupational Safety and Health; OSHA =Occupational Safety and Health Administration; MSHA = Mine Safety and HealthAdministration; USNRC = U.S. Nuclear Regulatory Commission; WHO = World HealthOrganization EPA recommends action below 4 pCi/L in schools on a case-by-case basis WLM = working level month; a unit of measure commonly used in occupationalenvironments (since WLM bears a complex relationship to pCi/L, physicians withresponsibility for mine workers are urged to contact NIOSH or EPA for further information) ALARA = As low as reasonably achievable

    Key Po in t s Currently, no federal, enforceable regulations controlindoor radon levelsonly guidelines withrecommendations and a national goal.

    EPA recommends abatement or remediation whenindoor radon air concentrations equal or exceed 4 pCi/L.

    Progress

    Check

    Ques t ion

    Choose theone bestanswer

    9. At which of the following levels would EPA recommendindoor radon remediation?

    A. 0.4 pCi/L.B. 1.3 pCi/L.C. 2 pCi/L.

    D. =>4 pCi/L.

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    9. The correct answer is D. The EPA recommendsabatement or remediation when the indoor radon airconcentration equals or exceeds 4 pCi/L.

    To review relevant content, see EPA Maximum

    Recommended Level Guidelines in this section.

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    W hat a r e the Po ten t ia l Heal th Ef fec ts f rom

    Exp osure t o I nc reased Radon Leve ls?

    Learn ing

    Objec t i vesOn completion of this section, you will be able to

    Describe the primary adverse health effects fromexposure to increased radon levels.

    I n t r o d u c t i o n At levels normally encountered in the environment, radonexposure causes no acute or subacute health effects, noirritating effects, and has no warning signs.

    The primary adverse health effect of exposure toincreased levels of radon is lung cancer.

    For lung cancer to develop may take years. For smokers, exposure to elevated radon levels

    increases their already heightened lung cancer risk.

    Children exposed to radon will have higher estimatedradiation doses than will adults. This is due to the differencesin lung shape and size and childrens faster respiration rate,all of which increase childrens risk of adverse health effectsfrom radon exposure.

    Lung Disease Due to radon progenys charged state and solid nature, theytend to attract dust particles. The progeny can be inhaled

    either as free particles (i.e., the unattached fraction) orattached to airborne particulates (i.e., the attached fraction).The attached fraction is 2-3 orders of magnitude morecarcinogenic. The smaller the dust particle, the deeper intothe lungs it can travel and deposit, together with the radonprogeny it carries (ATSDR 2009).

    Epidemiologic studies of miner cohorts have reportedincreased frequencies of chronic, nonmalignant lung diseasessuch as

    Emphysema, Chronic interstitial pneumonia, and Pulmonary fibrosis,

    all of which increased as cumulative exposure to radiationand cigarette smoking increased (ATSDR 2009).

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    Carc inogenic i ty Researchers have studied the prevalence of radon-inducedlung cancer in mining and residential populations. In miners,statistically significant increases in lung cancer have beenobserved, exceeding 465 WLM (Roscoe et al. 1989) and inresidential populations exceeding an average 14.65 pCi/L.

    As charged particles, the unattached radon progeny canadhere to lung fluid or the respiratory epithelium. But theattached fraction is what clings more effectively to therespiratory epithelium. Through mucociliary action, thoseprogeny floating unattached in lung fluid are rapidly clearedfrom the respiratory tract. And because of the alphaparticles short track length, only the fluid is exposed to anyreleased radiation, with no adverse health effects.

    When progeny transform within the lungs and theirenergy deposits in tissue (and not fluid), the geneticmaterial of cells lining the airways can be damaged. If acell lives but repair is incomplete, lung cancer candevelop (NRCC 1999).

    Attached progeny preferentially deposit in the bronchi,the site of most lung cancers.

    The total amount of energy deposited in successivetransformations of the progeny is several times thatproduced in the initial radon decay.

    An exact systematic description of how cancers form as aresult of exposure to radiation is only partially understood.Cancer is a monoclonal disease that starts as a single cellwith heritable damage to the deoxyribonucleic acid (DNA);this damage confers a proliferative advantage relative tonormal cells (Iannaccone 1987). Most of the lung cancersassociated with radon are bronchogenic, with all histologictypes represented.

    Smaller lungs and faster respiration rates in childrengenerally results in higher estimated radiation doses to

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    childrens lungs relative to adults.

    Cigarette smoking and radon decay products synergisticallyinfluence lung cancer risk in a supra-additive manner. Minerstudies found that if smoking started before occupational

    radon exposure, the effect was submultiplicative, or, if theseoccurred in the opposite order, more-than-multiplicative(ATSDR 2009).

    The analysis of results from thirteen European residentialcase-control studies showed an increase in lung cancer riskproportionate to the unit increase in radon concentration,similar in lifelong nonsmokers and cigarette smokers (ATSDR2009).

    The lung cancer risk for cigarette smokers may be up to 25times greater than that of nonsmokers exposed to highresidential radon levels (up to 10.8 pCi/L) (Darby et al.2005, 2006).

    The lung cancer risk due to radon exposure is second only tothat of smoking (Alberg 2007; Copes 2007; EPA 2009a).

    Although the synergistic mechanism(s) of cigarettesmoking and radon exposure are unknown, thecombinations adverse health effects are well known.

    Among both smoking and nonsmoking populations ofunderground miners, small-cell carcinoma occurs at a higherfrequency in the initial years following exposure comparedwith the pattern of similar histologic types in the generalpopulation. This is believed due to the high levels of radonexposure underground, but could be due in part to high-levelsilica dust exposure.

    Other types of lung cancers seen in radon exposed minersinclude

    Adenocarcinoma, Large cell carcinoma, and Squamous cell carcinoma.

    Reproduc t i ve

    Ef fec tsNo evidence supports the suggestion that environmentalradon exposure is causally associated with adverse

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    10. The correct answer is C. Lung cancer is the onlyestablished human health effect currently associatedwith exposure to increased radon levels.

    To review relevant content, see Carcinogenicityin this

    section.

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    How do you Cl in ica l ly Assess a Pat ien t Pot ent ia l ly

    Ex posed to I ncr eased Leve ls o f Radon?

    Learn ing

    Objec t i vesOn completion of this section, you will be able to

    Describe the clinical assessment of a patient potentiallyexposed to increased radon levels.

    I n t r o d u c t i o n Risk Factors for lung cancer include increased exposure toradon gas, personal traits such as a family history of lungcancer, and smoking status and environmental tobaccosmoke (ETS) exposure. The NRC, Biological Effects ofIonizing Radiations (BEIR) VI report, Health Effects ofExposure to Radon concludes that indoor radon is the

    second leading cause of lung cancer after cigarette smokingThe EPA estimates that among nonsmokers, increased radonexposure is the leading cause of lung cancer. (NRC 1999;EPA 2003). This is important information when deciding onappropriate assessment strategies, even if the patient is notexhibiting symptoms.

    In cases where increased exposure to radon is suspected,the medical evaluation might include

    An exposure history

    A medical history with review of organ systems, A physical examination, and Additional laboratory testing as clinically indicated.

    Patients with potential exposure to increased radon levelsshould undergo a thorough medical evaluation.

    Currently no effective, community-wide screening methodsare available for medical prevention or early diagnosis andtreatment of lung cancerradon-induced or otherwise.

    Neither the American Cancer Society (ACS) nor any othermedical/scientific organization recommends for or againstscreening for the detection of early lung cancer inasymptomatic persons (AAFP 2010; CTFPHC 2003; Smith2009; USPSTF 2004).

    Exposure

    H is t o r yA detailed exposure history is an important step inevaluating a patient who may be at risk for health outcomes

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    related to increased radon exposure. In general, radon levelstypically encountered in a communitys outdoor ambient airhave not resulted in short- or long-term adverse healtheffects. That said, increased exposure doses may besignificant for some and could result in more serious health

    outcomes requiring further evaluation and treatment.

    An exposure history as part of the patient history will aid inassessing potential exposure to increased levels of radon.The exposure history may include

    A work history of any current and past occupations isrelevant in evaluating this and other exposures,especially occupations in which the patient may havebeen exposed directly or indirectly to radon.

    Age of home (to determine how tightly the building maybe sealed).

    Family history of lung cancer. Number and type of gas appliances used in the home.

    Are the appliances vented to the outside? Do they havedouble wall pipe? (This will identify improperly ventedgas-fed stoves and fireplaces, gas dryers, and waterheaters).

    Presence and numbers of smokers in the home. Testing results from radon measurements in their

    home.

    Time spent in the basement or lower level of thestructure (depending on the type of home). Type of home foundation (e.g., built on a slab, with a

    crawl space, finished or unfinished basement). Types of ventilation (opening windows and frequency)

    systems in the home.

    The ATSDR Case Studies in Env ironm ental Medicine: Takingan Exposure HistoryCourse provides more information and asample form to use when taking an exposure history (ATSDR2009,http://www.atsdr.cdc.gov/csem/exphistory/ehcover_page.html).

    Medica l Knowing the complete medical history of a patient who hasH is t o r y been exposed to increased radon levels can help in making

    an accurate diagnosis. To ask about lung function isespecially importantthe lung is the target organ for inhaled

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    radon.

    No signs and symptoms are specific to increased levels ofradon gas exposure.

    Typically, radon-associated lung cancer has a long latencyperiod; many patients exposed to increased levels of radonmay be asymptomatic for years. Clinical manifestation oftarget organ toxicity is based on

    Route of exposure Dose Genetic factors Frequency, duration, and intensity of exposure, and Time elapsed since exposure.

    Phys ica l Increased radon exposure can result in lung cancer. But theExam exposure has no acute or subacute health effects, no

    irritating effects, and no warning signs at levels normallyencountered in the environment.

    A physical examination of patients with potential exposure toincreased radon levels needs to focus on signs andsymptoms of the respiratory system. Although physicalexamination may not provide radon-specific information, todetermine whether radon exposure has or has not occurred

    is important. The physical examination might beindeterminate for assessing lung cancer specific to radonexposure. Still, to proceed is clinically reasonable, given thatradon is a significant environmental cause of lung cancerdeaths and may cause lung disease.

    Lung cancers clinical presentation may vary; some patientsmay be asymptomatic. In fact, about 25% of people withlung cancer do not have advanced cancer symptoms fromwhen their lung cancer is detected (Humphrey 2004). Whenpresent, lung cancer symptoms may include

    Shortness of breath, Persistent cough, Wheezing, Hemoptysis, and Chest pain.

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    Other lung cancer-related changes that can sometimes occurmay include repeated bouts of pneumonia, changes in theshape of the fingertips, and swollen or enlarged lymph node(glands) in the upper chest and lower neck (Harrison 2008).

    Clinical presentation and clinical judgment will dictate thenext steps in assessment, using the data retrieved from thehistory and the physical exam. This may include testing,referral to a specialist, or both.

    Tes t ing To determine the most beneficial method(s) to test for lungcancer in an asymptomatic patient potentially exposed toincreased radon levels, more studies are needed. Methodsmay include using either low-dose computerized tomography(LDCT), chest x-ray (CXR), sputum cytology, or acombination of these tests (Smith 2009; USPSTF 2004). Still,whether these tests can help prevent deaths from lungcancer is currently unknown.

    For more information about lung cancer diagnosis andtreatment, visit the National Cancer Institutes (NCI)Physician Data Query (PDQ)sites. http://www.cancer.gov/cancertopics/pdq

    C o m m u n i t y Screening at the community level for lung cancer inW i d e asymptomatic persons involves both benefits and risks.Screen ing

    Screening is best described as tests to assess the likelihoodof a disease or condition in an apparently healthy person.The fundamental purpose of screening is to prevent theonset of disease through early diagnosis and treatment.

    Currently no effective, community-wide screening methodsare available for medical prevention or early diagnosis andtreatment of lung cancerradon-induced or otherwiseinasymptomatic persons. Neither the American Cancer Society(ACS) nor any other medical/scientific organization

    recommends for or against screening for the detection ofearly lung cancer in asymptomatic individuals (AAFP 2010;CTFPHC 2003; Smith 2009; USPSTF 2004).

    But consider: screening for lung cancer that involves takinga CXR adds to the persons radiation dose and increases the

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    risk of lung cancer.

    The sensitivity of LDCT for detecting lung cancer is fourtimes greater than the sensitivity of CXR. Compared withCXR, however, LDCT is associated with a greater number of

    false-positive results, more radiation exposureup to 100times the radiation dose of a CXRand increased costs.

    Because of the high rate of false-positives, lung cancerscreening will subject many patients to invasive diagnosticprocedures. Although the morbidity and mortality rates fromthese procedures in asymptomatic individuals are notavailable, mortality rates because of complications fromsurgical interventions in symptomatic patients reportedlyrange from 1.3 to 11.6%; morbidity rates range from 8.8 to44%, with higher rates associated with larger resections(USPSTF 2004).

    Other potential screening hazards are potential anxiety andconcern from false-positive results and misplacedreassurance from false-negative results. These hazards,however, have not been adequately studied.

    The benefit of screening for lung cancer has not beenestablished in any group, including asymptomatic high-riskpopulations such as older smokers. The balance of harms

    and benefits becomes increasingly unfavorable for persons atlower risk, such as nonsmokers (USPSTF 2004).

    Key Po in t s Because exposure to increased radon gas levels isconsidered a significant environmental cause of lungcancer deaths, clinical assessment to include historyand physical exam is reasonable for patients potentiallyexposed to increased radon levels.

    Risk factors for exposure to increased levels of radoncan be obtained during the patient history, including anexposure history and an organ systems review (ROS).

    Testing the home and background air can detectenvironmental levels of radon and its progeny. Thisinformation can be helpful when assessing exposurerisk.

    No specific signs and symptoms are associated withexposure to increased levels of radon gas.Nevertheless, in a clinical setting signs and symptoms

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    A. The correct answer is D. Clinically assess adults andchildren potentially exposed to increased radon levelsby initially taking a patient history that includes anexposure history and review of organ systems anddoing a focused physical exam targeting the respiratory

    system. Increased environmental radon levels may bedetected by appropriately measuring levels of radon gasin the patients dwelling or place of employment. Thishelps in the assessment of exposure risk to increasedradon levels. Radon exposure does not yet have specificbiomarkers.

    To review relevant content, see Introduction, ExposureHistory, Medical History, Physical Exam and Community

    Wide Screening in this section.

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    How Shou ld Pa t ien t s Po t en t ia l l y Exp osed t o

    I ncr eased Leve ls o f Radon Be Tr eated and

    Managed?

    Learn ing On completion of this section, you will be able to describeObjec t i ves

    The clinical management of patients potentially exposedto increased radon levels.

    Appropriate referrals for positive findings during clinicalassessment.

    I n t r o d u c t i o n With radon, the most important preventive action is tominimize exposure to it. This requires appropriatemeasurement of environmental radon levels in the patientshome to determine whether the levels are 4 pCi/L or more. Ifradon levels are at 4 pCi/L or more, recommendations toabate the increased exposure risk may include having thepatient remediate radon levels in his or her home (reductionand abatement) to background, outdoor ambient air levels.

    More information on measuring and abating radon is in theAnnex I at the end of this case study (see the EPA radonlink there).

    Patients potentially exposed to increased radon levels at

    home should have a clinical assessment. If clinical findingsare positive, consider appropriate referrals.

    Care o f t he Clinical care is based on findings from the initial clinicalPat ien t assessment and the health care providers clinical judgment.Poten t ia l l y If a patient already has a respiratory condition, considerExpo sed to further testing, referral to a specialist, or both.I nc reased

    Levels of

    RadonThe following may increase the likelihood of the patienthaving a pulmonary malignancy:

    Radiographic appearance of a lesion (size and lack ofcalcification),

    Age, Sex (current or former women smokers are at higher

    risk). Symptoms of cough and weight loss, Hypercalcemia,

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    Absence of residence in or travel to an area endemicfor coccidioidomycosis (southwest United States) orhistoplasmosis (Ohio/Mississippi Valley),

    Absence of fever or evidence of infectious disease, and Negative PPD skin test, which does not rule out

    tuberculosis, but makes it less likely.

    Patient care based on the physicians assessment mayinclude further testing or, depending on the findings,additional referrals to an oncologist and chest surgeon.Initially, one or more of the following tests might be ordered:

    Search for previous chest radiographs for comparison, Sputum studies for cytology and cultures (standard

    pathogens, fungus, acid-fast bacilli), LDCT scan, and Fiber optic bronchoscopy with bronchial brushings and

    specimens for cytology and culture.

    If a primary lung cancer is detected, a metastatic workup(scans of the brain, liver, adrenals, and bones) might beindicated. Depending on histologic type, local extension intoadjacent anatomical structures, presence of metastases, andthe general health of the patient, treatment options mayinclude surgical excision, radiation therapy, chemotherapy,and possibly immunotherapy. Again, specialist care and his

    or her recommended treatment plan should guide suchtreatment.

    Referral to a specialist with expertise and experience treatinglung disease is reasonable, given positive findings from theinitial clinical assessment.

    The patient should be apprised of the positive findingstogether with the reason for referral.

    Key Po in t s Preventive steps can minimize exposure to radon. Preventive actions to reduce environmental levels of

    radon below 4 pCi/L include home remediation. Findings from the initial clinical assessment and the

    health care providers clinical judgmentincludingappropriate referral and follow up as clinicallyindicatedguide treatment and management of patientspotentially exposed to increased radon levels.

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    Wh at I ns t r uc t i ons Shou ld Be Given t o Pa t i en t s t o

    Reduce Po t en t ia l Hea l th Risks f rom Exp osure t o

    Radon?

    Learn ingObjec t i ves

    On completion of this section, you will be able to

    Provide instructions on preventive measures patientscan take to reduce potential radon exposure and healthrisks.

    I n t r o d u c t i o n Primary health care providers should assist patients inunderstanding applicable clinical follow-up instructions aswell as preventive strategies to identify and abate increasedradon gas exposure.

    Chronic exposure to radon and its progeny can cause lungcancer. A physician should then advise patients to have theirhomes tested for radon. If radon concentrations are at4pCi/L or higher, the physician should recommend thatpatients take abatement or remediation actions in theirhomes to lower both radon levels and potential radonexposures.

    Providing existing, authoritative EPA or public health radonremediation resources may help patients take the necessary

    steps to minimize their radon exposure.

    The physician should discuss with the patient exposure risks(i.e., a hazard source that presents an opportunity foruptake into the body) and a completed exposure pathway(i.e., the route between the hazard source and actual uptakeinto the body). The patient should be counseled about otherrisk factors such as smoking that increase the risk ofdeveloping lung cancer from radon exposure. The RadonToxicity Patient Education and Care Instruction Sheetavailableat http://www.atsdr.cdc.gov/emes/health_professionals/instruction_sheets.htmlmay help facilitate this discussion.

    Be sure to let your patient know when to return for the next

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    medical appointment.

    S e l f Ca r e Preventive messages that allow patients to take action toavoid increased radon exposure are important in lung cancerprevention. Provide to your patients guidance on

    Radon testing Risks associated with combined exposures to tobacco

    smoke and radon Nutritional practice that support cancer prevention

    Supplying the patient with take-home information willincrease the likelihood of compliance with instructions fromyou or your staff.

    G e n e r a l

    p r e v e n t i v em e s sa g e s t o

    r e d u c e t h e

    r i s k o f

    c a n c e r

    General preventive messages to prevent lung cancer include

    Stop smoking and avoid second hand smoke.o The combination of smoking and radon exposure

    results in a higher lung cancer risk.

    Eat plenty of fruits and vegetables.o Eating a diet high in fruits and vegetables may help

    protect against lung cancer.

    Consider taking beta carotene supplements.o Beta carotene is an organic compound that may

    help protect against lung cancer. It contributes tothe orange color of many different fruits andvegetables. Vietnamese gac (MomordicaCochinchinensisSpreng) and crude palm oil areparticularly rich sources, as are yellow and orangefruits such as mangoes and papayas, orange rootvegetables such as carrots and yams, green leafy

    vegetables such as spinach and kale, and sweetpotato and sweet gourd leaves.

    More lung cancer-prevention information forpatients is available at:

    http://www.cdc.gov/cancer/lung/basic_info/prev