Resource  Information  on  Radon
 &  Radon-Resistant  Construction
   This resource guide was prepared
 to provide architects, builders, code
 officials, contractors and other bi ild-
 ing professionals with general and
 technical information on  radon ,md
 radon-resistant construction.
   Radon's  proven  link to  lung
 cancer, combined with its  prevalence
 throughout the United States, has
 increased public demand recently for
 radon-free home environments.
   In turn,  consumers are  seeking
 building professionals for  advice and
 expertise in dealing with  radon und
 radon-protection systems.
   Radon is a known human carcin-
 ogen,  and the  nation's  second
 leading cause of lung cancer after.
 smoking. It is  believed responsible
 for some 15,000 deaths every your.
   This colorless, odorless radio-
 active gas  occurs from the  natjral
 breakdown of uranium found in soil
 and rocks,  and can seep  into hones
 through foundation cracks and other
 openings.
   Scientists estimate that  nearly
 one of every 15 homes in the nation
 has elevated indoor radon levels. In
 addition, mapping studies suggest
 that more than one-third  of  all U.S.
 counties are potentially at  risk for
 high indoor radon readings.
   Radon's carcinogenicity and the
 need for protecting  home dwel.ers
 from its health  risks have  baen
 recognized  by  scores of scientific,
 medical, government and consumer
 groups, including  the U.S. Surgoon
 General, Consumer  Federation of
 America, National Medical Associa-
 tion,  American  Lung Association,
 National  Association of  Counties,
 Environmental Law Institute, and the
 National Safety Counca.
 Nation* Problem
   The dangers of radon were first
publicized in the early 1980s, wtten
extremely  high indoor levels  were
found in parts of Pennsylvania, New
Jersey and New York.
   By 1988, Congress had passed
the indoor Radon Abatement Act,
which called for efforts to eventually
ensure that indoor building air would
be made "as free  of radon as the
ambient air outside of buildings."
Cooperative Effort
   Since  that  time, hundreds  of
experts in both the public and private
sectors  have worked to lay the
groundwork for  a  radon-protected
housing stock in the United States.
   Several of these advances will
have a long-lasting impact on the
U.S.  housing industry and its allied
professions:
   •The  Environmental  Protection
Agency (EPA) and the U.S.  Geo-
logical   Survey   have   developed
extensive  maps   and  information
outlining the potential radon levels of
every county in the nation.
   •Recognized health and medical
institutions in the U.S. and abroad
have carried out additional studies of
radon to develop  more accurate
knowledge of "how" radon induces
lung cancer and to develop updated
risk assessments.
   •Commercial testing laboratories,
in cooperation with government and
research organizations, have devel-
oped improved testing devices and
monitoring methods.
   •Radon offices have been estab-
lished in every state  to  provide
consumers,  as  well  as building
professionals, with general and local
information on  radon and radon-
resistant construction techniques.
   •Model  radon-resistant building
standards, methods and techniques
have been developed and/or adopt-
ed for use by the EPA, the National
Association of Home Builders, the
American Society  for  Testing and
Materials, the Council  of American
Building Officials, and many others.
  •State  and  federal certification
programs have been developed  to
ensure that contractors  providing
radon testing and  radon reduction
for  existing  homes  have  the
necessary knowledge and expertise
to carry out radon work competently.
  •State  and  local officials have
begun to adopt a variety of radon-
protection   laws,  including radon
testing for all residential real estate
transactions, mandatory radon test-
ing of schools and the adoption  of
radon-resistant building codes.
  All of  the above subjects and
more are discussed in greater detail
on the following pages.
    INSIDE
                    **»
         Radon Zone  Map
         and discussion of zone
         classifications       2


         Radon and  Cancer,
         a look at the radioactive
         decay process      3


         Building  Methods
         for radon-resistant
         construction       4


         Testing  Procedures
         and how to best obtain
         reliable results       6

         Radon Legislation,
         a quick review of laws
         regarding radon      7


         StateRadon Offices
         for obtaining local help
         and information      8

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 EPA Maps, Studies Offer  In-Depth  Radon  Data
   Because it is impossible to know
 in  advance  if a  building  site  will
 produce hfgn radon readings,  EPA
 radon maps and their accompanying
 studies provide  excellent predictive
 information  and  guidance for build-
 ing professionals.
   In  the   late  1980s,  Congress
 directed EPA to identify areas of the
 United States with the potential for
 producing elevated levels of radon.
   In response, the EPA,  U.S. Geo-
 logical Survey and the Association of
 American State Geologists began
 developing  a  detailed map  that
 would target  those areas  of  the
 country  with  the  potential   for
 elevated indoor radon levels.
   The result, known simply as  the
 Map of Radon Zones, classifies the
 radon potential of all 3,141 counties
 in the United Slates.
   To foster lay interpretation of  the
 underlying technical  data,  counties
 were given  one of three possible
 ratings: Zone 1,  Zone 2, or  Zone 3.
   Zone 1 counties have the highest
 potential for elevated radon levels,
 with predicted indoor readings that
 match or exceed the lake  action"
 level of 4.0 picocuries per liter of air
 (pCM).
   By  comparison,  Zone 2 areas
 have predicted readings of 2.0 to 4.0
 pCl/l.  Zone 3 areas have the lowest
 potential for elevated  radon, with
 predicted  indoor readings  of  2.0
 pCly) or less.
   Generally speaking,  the  bulk of
the nation's Zone  1 counties are
found in the northern  half of the
 United States, in a broad  arc that
begins in the Northeast and moves
down  along  the   Appalachians,
spreads  across  the  Central  and
 Northern Plains, and sweeps up the
 RocWes to the Canadian border.
   Each county's zone designation
was determined by  in-depth analysis
of  the   region's  geology,  aerial
radioactivity, soil parameters,  sample
indoor radon  measurements,  and
foundation types.
   While the Map of Radon Zones is
a targeting tool for characterizing an
An EPA map breaks the nation's 3,141 counties into radon zones.  Zone 1 areas have
predicted potential radon levels of 4.0 picocuries per liter of air (pCi/l) or greater. Zone 2
predicted readings are between 2.0 and 4.0pCi/l. Zone 3 readings are predicted at 2.0 or less.
area's likely radon potential, it should
never be considered  a verification
document; only  in-structure  testing
can accurately provide indoor radon
measurements.
   Instead, it is designed for use by
building professionals  as a starting
point for gaining general knowledge
of an  area's radon potential,  after
which a state-specific  radon  zone
map and its accompanying  booklet
should be studied.
   Even  then,  it  is  important  to
remember that in order to  give  a
county a specific zone classification,
data has to  be extrapolated  from a
geological area to the often artificial
boundaries of a county.
   In the process, significant highs
and lews  within  a county may be
masked. In addition, "hot spots" can
and do occur in any zone, and radon
readings can vary  dramatically from
one home to the next in the same
neighborhood.
   Because of the vagaries of accu-
rately predicting indoor radon levels,
building professionals may  wish to
install a radon-reduction system as
"basic health insurance" for a home,
regardless of the area's radon zone
classification.
                                     To the iaft are details of bedrock and
                                     soil-type maps from the  Vermont study
                                     document  for EPA's map  of radon
                                     zones. Similar in-depth, radon zone
                                     study  documents  are  available  for
                                     every slate.

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                                    ; =•
Area's  Geologly

Is  Key Factor  i

In Radon  Levels

 Certain Rock, Soil Types
  Likely Radon Candidates

   Because radon is  a byproduct of
uranium, the geology of  an area's
rock and soil can prove invaluable in
predicting the potential for elevated
indoor radon levels.           ':
   Although such variables as soil
permeability, moisture,  barometric
pressure   and  temperature   can
significantly affect radon concentra-
tions, certain rock types  are  more
likely to cause elevated indoor radon
readings.
   Rock types likely to be associated
with elevated radon readings include
the  carbonaceous   black  shales,
glauconite-bearing sandstones* and
certain fluvial  sandstones,  chalk,
phosphorites, and  karst-prodi icing
carbonate rocks.             ':
   Certain glacial deposits, bauxite,
uranium-rich granite,  metamcrphic
granite,  silica-rich  volcanic rbcks,
some coals  and contact meUimor-
phosed rocks, as well as numerous
types of  sheared  or faulted  Pocks
should also be included  as  likely
candidates.                 '
   Of special note are fault and sheer
zones  associated   with  localized
uranium concentrations. To date, the
highest known indoor  radon levels
have been found in Boyertown, Pa.,
and Clinton, N.J. -  sites of sheared
fault zones with localized  uranium
concentrations.
   Geologists say that the rocks least
likely to  cause  radon   problems
include marine quartz sands, non-
carbonaceous shales and siltstones,
certain days, silica-poor metamcrphic
and igneous rocks, and basalts.
   Localized uranium deposits in any
of these rocks, however, significantly
increases the probability of elevated
radon readings.
                                                                          Thorium 234
                                                      Uranium 238


                                                   Protactinium 234

                                                         Uranium 234
                                                                         The uranium-238 decay series
                                                                         and their modes of decay.
                                  Radioactive Decay Process Defines
                                  Nature of Radon's Carcinogenicity
Radon-Resistant Ceasti-aetiion;
        Tecbniqw for the
  Within the world's scientific and
medical   communities,   the  link
between radon and  lung cancer is
well understood.
  But for most people, the thought
of an invisible gas bringing cancer
into their home has a hard-to-believe
science-fiction quality to it.
   Unfortunately, radon's health risks
are all too real.  Radon gas is a Class
A carcinogen, accounting  for  an
estimated 15,000 deaths every year.
A recent  study  released  by  the
National Cancer Institute now pegs
one  in every ten lung  cancers to
indoor radon exposure.
   How does radon gas trigger lung
cancer, and why is it most commonly
found in the home? The  answers
begin with  an  understanding  of
radon's role in the radioactive decay
of uranium.
   Radon's genesis is uranium, and
uranium is ubiquitous to the earth's
soil and rock. As uranium begins its
natural radioactive decay, it produces
thorium,  which  in  turn  produces
radium.     . .
   Radium then decays into radon.
Unlike thorium and radium, which are
solids that remain in the earth, radon
is a gas that moves up through  soil
and rock to areas of lower pressure.
  When  radon  gas  reaches  the
atmosphere unimpeded, it diffuses
quickly and harmlessly  into  the
outdoor air.
  But when radon's  escape from
soil or rock is impeded by a building,
it   frequently  seeps  into   that
structure,  usually  through  small
foundation  cracks  and  openings,
where it remains unless diverted by
some means to the outside.
   Once  inside a building,  radon's
radioactive decay continues  in the
form  of   microscopic  solids  or
particles.  These  decay  products
carry an  electrostatic charge  that
allows them to easily attach to dust or
other particles in the air.
   When  radon's radioactive decay
products  are inhaled, they may be
deposited in the  lungs before  they
can be naturally cleared out by the
mucus of the bronchi. As the decay
process continues within the lungs,
high-energy  alpha   particles   are
produced.
   These  alpha  products give off
massive  jolts of  electron  energy,
which can kill sensitive cells and/or
transform cell DMA. Once a cell has
been transformed in this  manner, it
has a significant potential for devel-
oping into lung cancer.

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 A  Primer on  Radon-Resistant  Construction  T
     When  the simplicity and  minor
  costs  of  Installing  a  radon-control
  system are compared to the health
  risks and prevalence of  radon, it's
  easy  to  see  why  many  experts
  believe radon-reduction techniques
  will soon  be standard  to  a large
  percentage of new  U.S.  residential
  construction.
    The vast majority of today's radon-
  reduction  techniques,  whether  for
  new or retrofit installations,  achieve
  their   effectiveness  through  soil
  suction or depressurization.
    Because the air pressure inside a
  building is generally lower than that
  of the soil around and beneath  a
  structure,  the pressure difference
  wiM cause a  building to act  like  a
  vacuum deaner.
    This means that soil ar (as weH as
  radon)  will be dragged up  into  a
  building through  any  foundation
  cracks  or other small openings that
  mayexfet
  Understanding the Bask*
    The  use of radon-resistant  con-
 struction techniques  prevents this
 by (1) creating a physical barrier to
 the Indiscriminate entry of gas into a
 structure, and (2) providing a  con-
 trolled  means  of tunneling  and
 redirecting the gas to the outdoors.
    Currently, the EPA estimates the
 average cost of installing a passive
 radon  system for new  residential
 construction   between  $350  and
 $500. However, many builders who
 are already using similar methods for
 moisture control and drainage report
 a substantially lower figure.
   Although methods vary by locale
 and foundation type,  most radon-
 resistant techniques  employ  the
 following basb steps (see Rgure 1):
   • Before concrete slabs or other
 floor systems that directly contact the
 ground are  put into place, a uniform
 and gas-permeable  layer of  dean
 aggregate or sand is put down. This
 layer of aggregate/sand should be at
 least 4 inches thick.
   * A minimum 6-mit (or 3-mi! cross
laminated)  polyethylene  sheet  or
equivalent sheeting materials is then
placed on top of the aggregate layer.
    *A PVC or other gas-tight venting
 pipe is embedded vertically into the
 sub-slab aggregate.  This venting or
 suction pipe should be at least  3
 inches in diameter, and secured with
 a T" fitting or similar support.
   •The  venting  pipe  is extended
 vertically through the building floors,
 terminating at least one foot above
 the surface of the roof, and at least
 10  feet away from any window or
 opening. The venting pipe serves to
 direct the radon  from under the
 foundation,  up through the house
 and  to  the  outdoors,  where  it
 dissipates quickly and harmlessly.
   •All openings in and around the
 foundation are sealed and caulked,
 and  an  electrical junction  box  is
 roughed in, should a venting fan be
needed in the future.
  While   the  above  steps  are
generally applicable to new homes
 with slab foundations, passive radon
 systems for crawlspace foundations
 employ similar techniques.
   One difference is that  instead of
 using  a layer  of  aggregate,  the
 polyethylene  sheeting  is   placed
 directly on the ground.
   Lengths of perforated drain pipe
 are  then   placed   beneath  the
 sheeting  around  the  foundation
 perimeter and  connected  to  the
 venting pipe.  The sheeting is then
 sealed  to all foundation walls  and
 piers (see Figure 2).
 Passive vs. Active
   The only difference between a
 "passive" and an  "active"  radon-
 control  system is whether a venting
fan is in operation.  When a fan is not
 used,  the  system  is considered
 passive; use of  the  fan makes the
system  active. In many  cases,  a
passive system is all that is needed
  Figure 1

  Passive Radon System
  For New Construction
        Concrete  Slab
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hniques for  Building Professionals
    to effectively reduce radon levels.
      However, all  new homes should
    be tested after a passive system has
    been  installed  to ensure that" the
    indoor radon level is below 4.0 pCi/1.
    If not, a fan should be installed- and
    operated continuously  to actively
    draw radon from the soil and into the
    venting pipe (see Figure 3).
    Retrofitting
      Retrofit   installation  of  radon-
    control systems  generally use the
    same concepts as new-construction
    systems, although most are  active
    rather than passive in design.
      For slab  foundation  retrofits, sub-
    slab, drain-tile or sump-hole suction
    techniques  are the most  frequently
    used. Sub-slab suction calls for the
    venting pipe to be inserted through
    the  floor slab into the  aggregate or
    soil  below and then actively vented
    to the outside air.            *
                                      For  slab foundations  with  drain
                                    tiles in place, suction on the tiles can
                                    often  effectively  reduce  elevated
                                    indoor radon levels.  With sump-hole
                                    depressurization, the sump can be
                                    capped to serve as the location for a
                                    radon suction pipe.
                                      For  crawl space-type  retrofits, a
                                    common solution  is sub-membrane
                                    depressurization with suction  pipes
                                    as well as  additional venting of the
                                    crawl space area.
                                      As to be expected, retrofitting is
                                    more  costly than installing a new-
                                    home radon control  system. In fact,
                                    retrofit systems generally  run  from
                                    $500 to $2,500, depending on the
                                    size of the home,  its foundation type
                                    and the reduction method chosen.
                                    Increasing Use
                                      Because radon systems are far
                                    more  simple and  inexpensive  to
                                    install during the construction phase,
the  EPA  is  encouraging building
professionals  to  routinely  include
them as a basic new-home feature.
   The National Association of Home
Builders already recommends pass-
ive  radon  systems  for  all   new
residential construction in Zone 1
areas. Also, the Council of American
Building Officials  recently adopted
radon-reduction techniques for use
in high-radon areas.
   Model  building  standards  for
radon-resistant construction in  new
homes are available from the EPA as
well  as the  American  Society for
Testing and Materials (ASTM).
   Building professionals  living in
areas where  soil conditions or  local
building practices appear to preclude
the  use of  these  model building
standards are encouraged to contact
their State Radon Offices for infor-
mation on practical alternatives.
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     Testing:  Sole  Method  for  Measuring Indoor  Radon

         Modern radon testing devices are popular, accurate, inexpensive
    In-structure testing  is the  only
  known method for measuring indoor
  radon levels.
    Fortunately,  the  technology  for
  monitoring radiation has progressed
  to the point that accurate radon tests
  are easily obtained at relatively  little
  cost.
    Radon testing  is  recommended
  for al existing homes and is often
  required for the dosing of residential
  real estate transactions.
     In addition,  testing  is generally
  needed to verify the effectiveness of
  a  radon-resistant  system installed
 during construction of a new home.
    Testing can be  conducted  with
 do-rt-yourself kits or  by an EPA or
 state-certified  radon  tester. While
 hiring a  certified tester  is generally
 more expensive, test results may be
 obtained more quickly or prove more
 reliable,  depending  on the type of
 device used.
 Length of Testing
   Radon tests  are  classified  as
 either short term (2-90 days) or long
 term (more than 90 days). Practically
 speaking, most  short-term   tests
 require two to seven days; long-term
 tests are  usually measured at dose
 to 90 days.
   Short-term tests  generally have
 one- to two-week waiting periods to
 receive lab results;  long-term tests
 take two to four weeks  for results.
 Many  companies offer  results  by
 phone or fax, which can shorten the
 wailing period.
   Short-term test kits  are the most
 popular, given their abbreviated time
 frames.  However,  long-term  kits
 "smooth   out" daily  and seasonal
 radon  fluctuations to yield a better
 measure  of the average year-round
 radon reading.
 Types of  Device*
   All radon testing devices, whether
 short-term or long-term, are dassified
 as passive or active.
   By definition, passive  testing de-
vices do not require a power source.
 Common passive testing devices in-
 dude charcoal canisters, alpha-track
 detectors, charcoal liquid scintillation
 devices,  and electret ion  chamber
 detectors.
    With the exception of the latter,
 which  often   are   available  only
 through laboratories,  passive  test
 devices are  readily  available  in
 hardware and building supply stores
 for $10 to $25.
    By  comparison,  active testing
 devices require a power source. In
 addition, they require operation by a
 trained technidan.
   Active testing devices will monitor
 the indoor air continuously,  and can
 usually record unusual  swings in
 radon levels.  Many detect testing
 interference,  making  them  popular
 for use in real estate transactions.
  Common Passive Testing Devices
  Charcoal canisters are popular short-
 term  passive testing  devices; most
 take  48-hour readings.  A  lab then
 measures the number of radon particles
 absorbed by the activated charcoal.
  Alpha-track detectors are often used
 for long-term passive  testing. Radon
 decay or alpha particles strike a special
 plastic dish at the base of the device.
 A lab then counts the "strike" spots.
   In all of these testing scenarios,
the threshold measurement at which
action should be taken to reduce the
indoor radon level is 4.0 picocuries
per Iter (pCi/l) or greater.
 Recommendations
    The EPA generally recommends
 that in the case of short-term tests
 using  passive devices,  two  tests
 should be  taken  and  the  results
 averaged.
   The two tests can be conducted
 simultaneously or repeated 48 hours
 apart.  If an active device is employed,
 only   one   short-term  reading  is
 considered necessary.
    When results are dose to the 4.0
 threshold, another  round of  short-
 term tests  or a  long-term reading
 may be advisable.
   In  all  cases,   testing  devices
 should be placed at least 20 inches
 above the floor in  the basement or
 lowest level of the home suitable for
 occupancy.
   The kit or device should  also be
 placed in an area where it will not be
 disturbed, away from drafts, exterior
 walls and areas of high temperature
 or  humidity.  Testing should  be
 avoided during severe storms.
   In   addition,   short-term  tests
 require "closed-house" conditions at
 least 12 hours prior to and during the
 testing period.
    If testing is being conducted in a
 home with an active radon-reduction
 system in place, the fan should be in
 operation at least 24 hours  prior to
 and during the testing period.
 Consumer Reports

 Rates Radon Kits

   Consumer Reports magazine, in
its July 1995 issue, tested and rated
a variety of short-term and long-term
passive testing devices.
   For the most part, the magazine
found the  majority of the kits to be
accurate and widely available.
   The report also discusses  what
consumers should  know and  do if
they obtain test results at the  lake
action" level of 4.0 pCi/l or greater.
6

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States Continue  to Pass Radon-Protection  Laws
   During the past ten  years, law-
makers  around the  country have
passed a significant number of radon
protection laws.
   Many of the earliest  radon laws
focused on developing  certification
programs for contractors  providing
radon mediation services.
    This was followed by a wave of
legislation  to inform  individuals of
any potential indoor radon problems
before purchasing a home.
    Much  of the radon legislation
currently  under  consideration  is
centered  on   introducing  radon-
reducing features into  the nation's
new housing stock.
Red Estate
   State laws requiring indoor radon
measurements  be disclosed  to the
buyer as part of a real estate sale or
transfer probably affect the greatest
number of Americans every year.
    At least 15 states currently have
radon-disclosure real estate laws in
place,  and similar legislation  has
been introduced in several more.
    In many  areas  of  the  country
where radon  levels are generally
high,  but   radon testing  is  not
 required by  law,  home  inspection
firms routinely  recommend radon
 testing prior to closing.
     Between  these  voluntary and
 mandated  radon  disclosures,  an
 estimated 16 percent of the nation's
 annual real estate transactions now
 involve a radon test
 Certification
    To protect consumers requesting
 radon testing and mitigation, many
 states  also  have  developed  pro-
 grams to register, license and certify
 radon  testing  professionals  and
 mitigation  service  providers.  The
 EPA also  certifies such  individuals
 through  its own  Radon Proficiency
 Program or RPP.
    Types  of Radon  Legislation Enacted by States
                 Certification     R.E.  Disclosure
   Under the RPP  program,  con-
tractors must take a rigorous exam
and  follow  specific  standards  in
carrying out mitigation work.
   RPP contractors  are certified as
qualified to review testing results, to
evaluate radon problems  and  to
provide  detailed remediation pro-
posals.
   In addition, they are qualified to
design and  install  radon  reduction
systems,  and  to ensure that the
installed system  effectively reduces
elevated  radon  levels.  Most  state
radon  certification   programs  are
similar to that of the EPA.
Code Changes
   In recent years, some states have
added radon-resistant construction
provisions  to  their  building codes.
Most of these code  changes are
patterned  after  the  EPA  model
standards  for controlling   radon  in
new residential buildings.
   In addition, the Council of Ameri-
can Building  Officials (CABO) has
adopted radon-resistant techniques
for use in  all  new homes located in
high-radon areas.
    CABO is  a nationally recognized
model-code organization.  Because
many cities and other municipalities
automatically   adopt  CABO  code
modifications  into their own building
codes, the number of new homes
featuring  radon-resistant  construc-
tion should increase dramatically  in
the future.
                                      FmADDTTIONAL INFORMATION
   The Environmental Protection AgencyCoffers tou8dlng professionals complete information on radon and radon-resistant
   construction, including model standards and architectural drawings, at no charge. To obtain these or other documents:

                                        PHONE 1-800-SS-RADON

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State Radon Offices
** f f
Every state radon office can provide building professionals with complete information on radon in general, regional radon
studies, and radon-resistant construction techniques. Please note that the "800" numbers are for in-state use only.
Alabama
Alaska
Arizona
Arkansas
California
Colorado
Connecticut
Delaware
DtslofCol
Rorida
Georgia
Hswal
Idaho
Knots
Sndtana
owa

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