Orders of magnitude (radiation)
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Recognized effects of higher acute radiation doses are described in more detail in the article on radiation poisoning. Although the International System of Units (SI) defines the sievert (Sv) as the unit of radiation dose equivalent, chronic radiation levels and standards are still often given in units of millirems (mrem), where 1 mrem equals 1/1000 of a rem and 1 rem equals 0.01 Sv. Light radiation sickness begins at about 50–100 rad (0.5–1 gray (Gy), 0.5–1 Sv, 50–100 rem, 50,000–100,000 mrem).
The following table includes some dosages for comparison purposes, using millisieverts (mSv) (one thousandth of a sievert). The concept of radiation hormesis is relevant to this table – radiation hormesis is a hypothesis stating that the effects of a given acute dose may differ from the effects of an equal fractionated dose. Thus 100 mSv is considered twice in the table below – once as received over a 5-year period, and once as an acute dose, received over a short period of time, with differing predicted effects. The table describes doses and their official limits, rather than effects.
|Level (mSv)||Level in standard form (mSv)||Duration||Hourly equivalent (μSv/hour)||Description|
|0.001||1×10−3||Hourly||1||Cosmic ray dose rate on commercial flights varies from 1 to 10 μSv/hour, depending on altitude, position and solar sunspot phase.|
|0.01||1×10−2||Daily||0.4||Natural background radiation, including radon|
|0.06||6×10−2||Acute||-||Chest X-ray (AP+Lat)|
|0.07||7×10−2||Acute||-||Transatlantic airplane flight.|
|0.09||9×10−2||Acute||-||Dental X-ray (Panoramic)|
|0.1||1×10−1||Annual||0.011||Average USA dose from consumer products|
|0.15||1.5×10−1||Annual||0.017||USA EPA cleanup standard|
|0.25||2.5×10−1||Annual||0.028||USA NRC cleanup standard for individual sites/sources|
|0.27||2.7×10−1||Annual||0.031||Yearly dose from natural cosmic radiation at sea level (0.5 in Denver due to altitude)|
|0.28||2.8×10−1||Annual||0.032||USA yearly dose from natural terrestrial radiation (0.16-0.63 depending on soil composition)|
|0.46||4.6×10−1||Acute||-||Estimated largest off-site dose possible from March 28, 1979 Three Mile Island accident|
|0.48||4.8×10−1||Day||20||USA NRC public area exposure limit|
|0.66||6.6×10−1||Annual||0.075||Average USA dose from human-made sources|
|1||1×100||Annual||0.11||Limit of dose from man-made sources to a member of the public who is not a radiation worker in the US and Canada|
|1.1||1.1×100||Annual||0.13||1980 average USA radiation worker occupational dose|
|2||2×100||Annual||0.23||USA average medical and natural background |
Human internal radiation due to radon, varies with radon levels
|3||3×100||Annual||0.34||USA average dose from all natural sources|
|3.66||3.66×100||Annual||0.42||USA average from all sources, including medical diagnostic radiation doses|
|4||4×100||Duration of the pregnancy||0.6||Canada CNSC maximum occupational dose to a pregnant woman who is a designated Nuclear Energy Worker.|
|5||5×100||Annual||0.57||USA NRC occupational limit for minors (10% of adult limit)|
USA NRC limit for visitors
|5||5×100||Pregnancy||0.77||USA NRC occupational limit for pregnant women|
|6.4||6.4×100||Annual||0.73||High Background Radiation Area (HBRA) of Yangjiang, China|
|7.6||7.6×100||Annual||0.87||Fountainhead Rock Place, Santa Fe, NM natural|
|10||1×101||Acute||-||Lower dose level for public calculated from the 1 to 5 rem range for which USA EPA guidelines mandate emergency action when resulting from a nuclear accident|
|14||1.4×101||Acute||-||18F FDG PET scan, Whole Body|
|50||5×101||Annual||5.7||USA NRC/ Canada CNSC occupational limit for designated Nuclear Energy Workers(10 CFR 20)|
|100||1×102||5 years||2.3||Canada CNSC occupational limit over a 5-year dosimetry period for designated Nuclear Energy Workers|
|100||1×102||Acute||-||USA EPA acute dose level estimated to increase cancer risk 0.8%|
|120||1.2×102||30 years||0.46||Exposure, long duration, Ural mountains, lower limit, lower cancer mortality rate|
|150||1.5×102||Annual||17||USA NRC occupational eye lens exposure limit[clarification needed]|
|170||1.7×102||Acute||Average dose for 187 000 Chernobyl recovery operation workers in 1986|
|175||1.75×102||Annual||20||Guarapari, Brazil natural radiation sources|
|250||2.5×102||2 hours||125 000||(125 mSv/hour) Whole body dose exclusion zone criteria for US nuclear reactor siting (converted from 25 rem)|
|250||2.5×102||Acute||-||USA EPA voluntary maximum dose for emergency non-life-saving work|
|260||2.6×102||Annual||30||Calculated from 260 mGy per year peak natural background dose in Ramsar|
|400-900||4–9×102||Annual||46-103||Unshielded in interplanetary space.|
|500||5×102||Annual||57||USA NRC occupational whole skin, limb skin, or single organ exposure limit|
|500||5×102||Acute||-||Canada CNSC occupational limit for designated Nuclear Energy Workers carrying out urgent and necessary work during an emergency.|
Low-level radiation sickness due to short-term exposure
|750||7.5×102||Acute||-||USA EPA voluntary maximum dose for emergency life-saving work|
|1000||10×102||Hourly||1 000 000||Level reported during Fukushima I nuclear accidents, in immediate vicinity of reactor|
|3000||3×103||Acute||-||Thyroid dose (due to iodine absorption) exclusion zone criteria for US nuclear reactor siting (converted from 300 rem)|
|4800||4.8×103||Acute||-||LD50 (actually LD50/60) in humans from radiation poisoning with medical treatment estimated from 480 to 540 rem.|
|5000||5×103||Acute||-||Calculated from the estimated 510 rem dose fatally received by Harry Daghlian on August 21, 1945, at Los Alamos and lower estimate for fatality of Russian specialist on April 5, 1968, at Chelyabinsk-70.|
|5000||5×103||5 000 - 10 000 mSv. Most commercial electronics can survive this radiation level.|
|16 000||1.6×104||Acute||Highest estimated dose to Chernobyl emergency worker diagnosed with acute radiation syndrome|
|20 000||2×104||Acute||2 114 536||Interplanetary exposure to solar particle event (SPE) of October 1989.|
|21 000||2.1×104||Acute||-||Calculated from the estimated 2100 rem dose fatally received by Louis Slotin on May 21, 1946, at Los Alamos and lower estimate for fatality of Russian specialist on April 5, 1968 Chelyabinsk-70.|
|48 500||4.85×104||Acute||-||Roughly calculated from the estimated 4500 + 350 rad dose for fatality of Russian experimenter on June 17, 1997, at Sarov.|
|60 000||6×104||Acute||-||Roughly calculated from the estimated 6000 rem doses for several Russian fatalities from 1958 onwards, such as on May 26, 1971, at the Kurchatov Institute. Lower estimate for fatality of Cecil Kelley at Los Alamos on December 30, 1958.|
|100 000||1×105||Acute||-||Roughly calculated from the estimated 10000 rad dose for fatality at the United Nuclear Fuels Recovery Plant on July 24, 1964.|
|10 000 000 000||1×1010||The most radiation-hardened electronics can survive this radiation level.|
|70 000 000 000||7×1010||Hourly||70 000 000 000 000||Estimated dose rate for the inner wall in ITER (2 kGy/s with an approximate weighting factor of 10)|
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Orvieto town, Italy
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- 10 CFR Part 100.11 Section 1
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high as 260 mGy/year
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- Centers for Disease Control and Prevention (https://emergency.cdc.gov/radiation/ars.asp)
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- ieee.org - Radiation Hardening 101: How To Protect Nuclear Reactor Electronics
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- Henri Weisen: ITER Diagnostics, page 13. Accessed August 28, 2017
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