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Radiological Dispersal Devices (RDDs)



Radiological Dispersal Devices (RDDs):
Dirty Bomb, Other Dispersal Methods

  • Radiological Dispersal Device (RDD) is any device that causes the purposeful dissemination of radioactive material without a nuclear detonation.
  • Dispersion methods can be
    • "Dirty Bomb" = Explosive method of dispersion (See Figure 1)
      • Explosion produces radioactive and nonradioactive shrapnel and radioactive dust
      • Explosion causes
        • Radiation contamination, commonly (Animations)
        • Radiation exposure only in certain circumstances (Animations)
        • Physical injury
        • Burns
        • Panic, fear

      Figure 1. Dirty Bomb: Radiological Dispersal Device Using Explosive
      Dirty Bomb: Radiological Dispersal Device Using Explosive Exploding dirty bomb (RDD) Replay animation

      Adapted from:
      Armed Forces Radiobiology Research Institute
      Explosion disseminates radioactive and non-radioactive shrapnel and radioactive dust


    • Other Dispersal Methods
      • Passive or active dispersion of unsealed radioactive sources, e.g., deposit in soil or water, drop from airborne device (See Figure 2)
      • Radioactive sources can be solid, aerosol, gas, or liquid
      • Contamination of people may occur via air, water, soil, or food

      Figure 2. Dispersal of Radioactive Material by Aircraft
      Dispersal of radioactive material by aircraft Replay animation


  • Explosive RDDs cannot cause mass casualties on the scale of a nuclear explosion. All or most fatalities or injuries will probably due to explosion itself.
  • While large numbers of people in a densely populated area around the detonation of a RDD might become contaminated and require decontamination, few if any will be contaminated to a level that requires medical treatment.
  • Local health authorities will have to assess the persons who were very close to the point of release for the need for medical intervention.
  • The health and environmental consequences from RDDs, will depend on
    • The design of the device
    • Type and quantity of radioactive material
    • The pattern of dispersion following the release
  • RDDs may affect
    • Small, localized areas (e.g., a street, single building, or city block)
    • Large areas, up to several square miles, depending on the nature of the dispersion and the amount and type of radioactive material
  • Other hazards may also be present
    • Fire, smoke, shock, shrapnel (from an explosion)
    • Industrial chemicals
    • Secondary device
  • Radioactive decontamination of persons and areas affected may be required.
References:

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Potential Isotopes Used in RDDs


RDD Isotope Fact Sheets

 
Isotope
More Information: Fact Sheets
EPA***

Americium-241

View

View

View

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Californium-252

View

Cesium-137

View

View

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Cobalt-60

View

View

View

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Iridium-192

View

Plutonium-238

View

View

View

Polonium-210

View

   

View

Radium-226

View

View

Strontium-90 (Sr-90/Y-90)

View

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*    HHS/Centers for Disease Control and Prevention
**  HHS/Agency for Toxic Substances and Disease Registry
***Environmental Protection Agency

 
See also:
Radioactive Properties, Internal Distribution, and Risk Coefficients (PDF - 32 KB) (Human Health Fact Sheet, Argonne National Laboratory, August 2005)
Radiological and Chemical Fact Sheets to Support Health Risk Analyses for Contaminated Areas (PDF - 2.34 MB) (Argonne National Laboratories, 2007)


Basic Radiological Properties of RDD Isotopes


Basic Radiological Properties of Nine Key Radionuclides for RDDs

Isotope

Half-Life
(years)

Specific Activity
(Ci/g)

Decay Mode

Radiation Energy (MeV)

Alpha
(α)

Beta
(β)

Gamma
(γ)

Americium-241

430

3.5

α

5.5

0.052

0.033

Californium-252

2.6

540

α (SF, EC)

5.9

0.0056

0.0012

Cesium-137

30

88

β, IT

-

0.19, 0.065

0.60

Cobalt-60

5.3

1,100

β

-

0.097

2.5

Iridium-192

0.2 (74 d)

9,200

β, EC

-

0.22

0.82

Plutonium-238

88

17

α

5.5

0.011

0.0018

Polonium-210

0.4 (140 d)

4,500

α

5.3

-

-

Radium-226

1,600

1.0

α

4.8

0.0036

0.0067

Strontium-90

29

140

β

-

0.20, 0.94

-

SF = spontaneous fission; IT = isomeric transition; EC = electron capture. A hyphen means not applicable. The radiation energies for cesium-137 include the contributions of barium-137 metastable (Ba-137m), and those for strontium-90 include the contributions of yttrium-90.

Adapted from Radiological Dispersal Device (PDF - 380 KB) Human Health Fact Sheet, Argonne National Laboratory, August 2005

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Potential RDD Effects

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Radiation Response Worker Exposure Guides (PAGs) in the Early Phase 1-5

Explaining protective actions and guides (PAGs) | Phases of response: early, intermediate, late

Total Effective Dose Equivalent (TEDE)
Guideline 6

Worker Activity

Condition

5 rem (0.05 Sv)

All occupational exposures

  • All reasonably achievable actions have been taken to minimize dose.

10 rem (0.1 Sv)

Protecting valuable property necessary for public welfare (e.g., a power plant)

  • All appropriate actions and controls have been implemented; however exceeding 5 rem is unavoidable.
  • Responders have been fully informed of the risks of exposures they may experience.
  • Dose > 5 rem is on a voluntary basis.
  • Appropriate respiratory protection and other PPE is provided and used.
  • Monitoring is available to project or measure dose

25 rem (0.25 Sv)

Lifesaving or protection of large populations

RDD incident: this dose level unlikely to be reached for response workers

IND incident: this dose level is conceivable for response workers

  • All appropriate actions and controls have been implemented; however exceeding 5 rem is unavoidable.
  • Responders have been fully informed of the risks of exposures they may experience.
  • Dose > 5 rem is on a voluntary basis.
  • Appropriate respiratory protection and other PPE is provided and used.
  • Monitoring is available to project or measure dose.

1 Adapted from Planning Guidance for Protection and Recovery Following Radiological Dispersal Device (RDD) and Improvised Nuclear Device (IND) Incidents (PDF - 394 KB) (DHS/FEMA, published in Federal Register, August 1, 2008, Z-RIN 1660-ZA02)

2 In the intermediate and late phases, standard worker protections, including the 5 rem occupational dose limit, would normally apply.

3 Other decision points for restricting response workers' activities have been recommended by various other agencies, as noted in table below.

Agency

Summary Information

Original Document

National Council on Radiation Protection and Measurement (NCRP)

NCRP Radiation Protection Guidelines: Control of Radiation Dose in the Control Zones

Key Elements of Preparing Emergency Responders for Nuclear and Radiological Terrorism (NCRP Commentary No. 19, December 2005, page 19, purchase required; see Free Overview (PDF - 219 KB))

International Atomic Energy Agency (IAEA)

IAEA Emergency Worker Turn-back Dose Guidance

Manual for First Responders to a Radiological Emergency (PDF - 2.2 MB) (CTIF, IAEA, PAHO, WHO, October 2006, page 41)

Conference of Radiation Control Program Directors, Inc. (CRCPD)

CRCPD Turn-back Exposure Rates and Dose Guidelines

Handbook for Responding to a Radiological Dispersal Device (Dirty Bomb): First Responder's Guide: The First 12 Hours (CRCPD Publication 06-6) (PDF - 4.26 MB), page 28. Conference of Radiation Control Program Directors, Inc. Frankfort, Kentucky, 2006.

International Commission on Radiological Protection (ICRP)

ICRP Guidance for Occupational Exposure

Protecting People Against Radiation Exposure in the Event of a Radiological Attack (International Commission on Radiological Protection, ICRP Publication 96, 2005, page 51)

4 Because each incident is unique, it is impossible to develop a single turn-back dose level for all responders in all events. Therefore, the 5, 10, and 25 rem guidelines this table should not be viewed as absolute standards applicable to the full range of incidents covered in this guidance, but rather serve as decision points for making worker protection decisions during emergencies. Incident Commanders should use the "as low as reasonably achievable (ALARA)" principle. During planning and training, managers and responders should acquire the knowledge necessary to understand the acute and chronic risks of exposure, especially at higher radiation levels.

5 By agreement with the Environmental Protection Agency (EPA), guidance in this August 1, 2008 Federal Register document will be incorporated without change into the currently ongoing revision of the 1992 EPA Manual of Protective Actions for Nuclear Incidents (the PAG Manual). This Federal Register notice of final guidance will therefore, sunset upon publication of the new EPA PAG Manual.

6 For potential doses >10 rem, special medical monitoring programs should be employed, and exposure should be tracked in terms of the unit of absorbed dose (rad) rather than TEDE (rem).

See also: Personal Protective Equipment (PPE)



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