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Tritium (), or hydrogen-3 (symbol T or H), is a rare and isotope of hydrogen with a half-life of 12.32 years. The tritium (t, sometimes called a triton) contains one and two , whereas the nucleus of the common isotope hydrogen-1 ( protium) contains one proton and no neutrons, and that of non-radioactive hydrogen-2 ( ) contains one proton and one neutron. Tritium is the heaviest particle-bound isotope of hydrogen. It is one of the few nuclides with a distinct name. The use of the name hydrogen-3, though more systematic, is much less common.

Naturally occurring tritium is extremely rare on Earth. The has only trace amounts, formed by the interaction of its gases with . It can be produced artificially by irradiation of or lithium-bearing ceramic pebbles in a and is a low-abundance byproduct in normal operations of nuclear reactors.

Tritium is used as the energy source in radioluminescent lights for watches, night sights for firearms, numerous instruments and tools, and novelty items such as self-illuminating key chains. It is used in a medical and scientific setting as a radioactive tracer. Tritium is also used as a fuel, along with more abundant , in reactors and is a vital component in . Tritium has also been used commercially in betavoltaic devices such as NanoTritium batteries.


History
Tritium was first detected in 1934 by Ernest Rutherford, and after bombarding with deuterons (deuterium nuclei). Deuterium is another isotope of hydrogen (of mass 2), which occurs naturally with an abundance of 0.015%.

Their experiment could not isolate tritium, which was first accomplished in 1939 by Luis Alvarez and , who also realized tritium's radioactivity.

(1987). 9780226813042, University of Chicago Press. .
recognized in 1954 that tritium could be used for radiometric dating of water and .


Decay
Tritium decays into helium-3 by as shown in this nuclear equation:
>

releasing 18.6  of energy in the process. The 's kinetic energy varies, with an average of 5.7 keV, while the remaining energy is carried off by the nearly undetectable electron antineutrino. from tritium can penetrate only about of air, and they are incapable of passing through the dead outermost layer of human skin. Because of their low energy compared to other beta particles, the amount of generated is also lower. The unusually low energy released in the tritium beta decay makes the decay (along with that of rhenium-187) useful for attempts at absolute mass measurement, none of which has yet succeeded.

The low energy of tritium's radiation makes it difficult to detect tritium-labeled compounds except by using liquid scintillation counting.


Production

Lithium
Tritium is most often produced in by neutron activation of lithium-6. The release and diffusion of tritium and helium produced by the fission of lithium can take place within ceramics known as . Production of tritium from lithium-6 in such breeder ceramics is possible with neutrons of any energy, though the cross section is higher when the incident neutrons have lower energy, reaching more than 900 barns for . This is an reaction, yielding 4.8 . In comparison, fusion of deuterium with tritium releases about 17.6 MeV. For applications in proposed fusion energy reactors, such as , pebbles consisting of lithium bearing ceramics including LiTiO and LiSiO, are being developed for tritium breeding within a helium-cooled pebble bed, also known as a breeder blanket.

+ → (2.05 MeV) + (2.75 MeV)

High-energy neutrons can also produce tritium from lithium-7 in an reaction, consuming 2.466 MeV. This was discovered when the 1954 Castle Bravo nuclear test produced an unexpectedly high yield.

Prior to this test, it was incorrectly assumed that would absorb a neutron to become , which would beta-decay to , which in turn would decay to two nuclei on a total timeframe much longer than the duration of the explosion.

+ → + +

The slowed neutrons from this reaction can still react with in the first, exothermic reaction; thus lithium can generate more tritium atoms than neutrons absorbed.


Boron
High-energy neutrons irradiating boron-10, also occasionally produce tritium:
+ n → 2 +

A more common result of boron-10 neutron capture is Li and a single .

Especially in pressurized water reactors which only partially neutrons, the interaction between relatively fast neutrons and the added as a produces small but non-negligible quantities of tritium.


Deuterium
Tritium is also produced in heavy water-moderated reactors whenever a nucleus captures a neutron. This reaction has a small absorption cross section, making a good neutron moderator, and relatively little tritium is produced. Even so, cleaning tritium from the moderator may be desirable after several years to reduce the risk of its escaping to the environment. Ontario Power Generation's "Tritium Removal Facility" is capable of processing up to of heavy water a year, and it separates out about of tritium, making it available for other uses.

typically produce of tritium per year, which is recovered at the Darlington Tritium Recovery Facility (DTRF) attached to the 3,512 MW Darlington Nuclear Generating Station in Ontario. The total production at DTRF between 1989 and 2011 was – with an activity of : an average of about per year.

Deuterium's absorption cross section for is about 0.52 millibarn, whereas that of oxygen-16 (O) is about 0.19 millibarn and that of oxygen-17 (O) is about 240 millibarns. While O is by far the most common isotope of oxygen in both natural oxygen and heavy water; depending on the method of isotope separation, heavy water may be slightly richer in O and O. Due to both and (n,) reactions (the latter of which produce C, an undesirable long-lived beta emitter, from O) they are net "neutron consumers" and are thus undesirable in a moderator of a natural uranium reactor which needs to keep neutron absorption outside the fuel as low as feasible. Some facilities that remove tritium also remove (or at least reduce the content of) O and O, which can – at least in principle – be used for .

India, which also has a large fleet of pressurized heavy water reactors (initially CANDU technology but since indigenized and further developed technology), also removes at least some of the tritium produced in the moderator/coolant of its reactors but due to the dual use nature of tritium and the Indian nuclear bomb program, less information about this is publicly available than for Canada.


Fission
Tritium is an uncommon product of the of uranium-235, plutonium-239, and uranium-233, (by ), with a production of about one atom per 10 fissions,

meaning it is produced in all reactors. The release or recovery of tritium needs to be considered in the operation of , especially in the reprocessing of nuclear fuel and storage of spent nuclear fuel. At some nuclear power plants it is discharged to the atmosphere.

Voloxidation is an optional additional step in nuclear reprocessing that removes volatile fission products (such as all isotopes of hydrogen) before an aqueous process begins. This would in principle enable economic recovery of the produced tritium, but even if the tritium is only disposed of and not used, it has the potential to reduce tritium contamination in the water used, reducing radioactivity released when the water is discharged since cannot be removed from "ordinary" water except by isotope separation.

Given the specific activity of tritium at , one is equivalent to roughly 2.8 mg.


Fukushima Daiichi
In June 2016 the Tritiated Water Task Force released a report

on the status of tritium in tritiated water at Fukushima Daiichi nuclear plant, as part of considering options for final disposal of the stored contaminated cooling water. This identified that the March 2016 holding of tritium on-site was 760  (equivalent to 2.1 g of tritium or 14 mL of pure tritiated water) in a total of 860,000 m of stored water. This report also identified the reducing concentration of tritium in the water extracted from the buildings etc. for storage, seeing a factor of ten decrease over the five years considered (2011–2016), 3.3 MBq/L to 0.3 MBq/L (after correction for the 5% annual decay of tritium).

According to a report by an expert panel considering the best approach to dealing with this issue, "Tritium could be separated theoretically, but there is no practical separation technology on an industrial scale. Accordingly, a controlled environmental release is said to be the best way to treat low-tritium-concentration water."

After a public information campaign sponsored by the Japanese government, the gradual release into the sea of the tritiated water began on 24 August 2023 and is the first of four releases through March 2024. The entire process will take "decades" to complete. China reacted with protest. The IAEA has endorsed the plan. The water released is diluted to reduce the tritium concentration to less than 1500 Bq/L, far below the limit recommended in drinking water by the WHO.


Helium-3
Tritium's helium-3 has a very large cross section (5330 barns) for reacting with thermal neutrons, expelling a proton; hence, it is rapidly converted back to tritium in .

+ n → +
This could allow tritium to be recycled as it decays, maintaining the desired inventory.


Cosmic rays
Tritium occurs naturally due to interacting with atmospheric gases. In the most important reaction for natural production, a fast neutron (which must have energy greater than 4.0 

) interacts with atmospheric :

+ n → +

Worldwide, the production of tritium from natural sources is about 4 megacuries (148 PBq) per year. The global equilibrium inventory of tritium created by natural sources remains approximately constant at 70 megacuries (2,590 PBq), as a balance between the fixed production rate and nuclear decay. These may be taken as 415 g and 7,250 g respectively.


Production history

USA
Tritium for American was produced in special heavy water reactors at the Savannah River Site until their closures in 1988. With the (START) after the end of the , the existing supplies were sufficient for the new, smaller number of nuclear weapons for some time.

of tritium was produced in the United States from 1955 to 1996. Since it continually decays into helium-3, the total amount remaining was about  at the time of the report,
     
and about as of 2023.27 years have passed since 1996, i.e. 2.25 half-lives, which reduce the 75kg of 1996 to 75/2^(2.25) ≈15.8 kg.

Tritium production was resumed with of rods containing (replacing the usual containing , , or ), at the reactors of the commercial Watts Bar Nuclear Plant from 2003 to 2005 followed by extraction of tritium from the rods at the Tritium Extraction Facility at the Savannah River Site beginning in November 2006.

Tritium leakage from the rods during reactor operations limits the number that can be used in any reactor without exceeding the maximum allowed tritium levels in the coolant.


Properties
Tritium has an of . Diatomic tritium ( or ) is a gas at standard temperature and pressure. Combined with , it forms ().

Compared to hydrogen having its natural composition on Earth, tritium has a higher (20.62 K vs. 13.99 K), a higher (25.04 K vs. 20.27 K), a higher critical temperature (40.59 K vs. 32.94 K) and a higher critical pressure (1.8317 MPa vs. 1.2858 MPa).

Tritium's specific activity is .

Tritium figures prominently in studies of due to its favorable reaction cross section and the large amount of energy (17.6 MeV) produced through its reaction with deuterium:

+ → +

All atomic nuclei have a positive charge from their , and therefore repel one another because like charges repel (Coulomb's law). However, if the atoms have a high enough temperature and pressure (for example, in the core of the Sun), then their random motions can overcome such repulsion, and they can come close enough for the strong nuclear force to take effect, fusing them into heavier atoms.

A tritium nucleus (triton), containing one proton and two neutrons, has the same charge as any hydrogen nucleus, and it experiences the same electrostatic repulsion when close to another nucleus. However, the neutrons in the triton increase the attractive strong nuclear force when close enough to another nucleus. As a result, tritium can fuse more easily with other light atoms than ordinary hydrogen can.

The same is true, albeit to a lesser extent, of deuterium. This is why ("failed" stars) cannot fuse normal hydrogen, but they do fuse a small minority of deuterium nuclei.

Like the other isotopes of , tritium is difficult to confine. Rubber, plastic, and some kinds of steel are all somewhat permeable. This has raised concerns that if tritium were used in large quantities, in particular for , it might contribute to radioactive contamination, though its short half-life should prevent significant long-term accumulation in the atmosphere.

The high levels of atmospheric nuclear weapons testing that took place prior to the enactment of the Partial Nuclear Test Ban Treaty proved to be unexpectedly useful to oceanographers. The high levels of tritium oxide introduced into upper layers of the oceans have been used in the years since then to measure the rate of mixing of the upper layers of the oceans with their lower levels.


Health risks
Since tritium is a low energy , it is not dangerous externally (its β particles cannot penetrate the skin), but it can be a radiation hazard if inhaled, ingested via food or water, or absorbed through the skin.

Organisms can take up HO, as they would HO. Plants convert HO into organically bound tritium (OBT), and are consumed by animals. HO is retained in humans for around 12 days, with a small portion of it remaining in the body as OBT. Tritium can be passed along the food chain as one organism feeds on another, though the metabolism of OBT is less understood than that of HO. Tritium can incorporate to and molecules within organisms which can lead to somatic and genetic impacts. These can emerge in later generations.

HO has a short biological half-life in the human body of 7 to 14 days, which both reduces the total effects of single-incident ingestion and precludes long-term of HO from the environment.

The biological half-life of tritiated water in the human body, which is a measure of body water turn-over, varies with the season. Studies on the biological half-life of occupational radiation workers for free water tritium in a coastal region of , India, show that the biological half-life in winter is twice that of the summer. If tritium exposure is suspected or known, drinking uncontaminated water will help replace the tritium from the body. Increasing sweating, urination or breathing can help the body expel water and thereby the tritium contained in it. However, care should be taken that neither nor a depletion of the body's results, as the health consequences of those things (particularly in the short term) can be more severe than those of tritium exposure.


Environmental contamination
Tritium has leaked from 48 of 65 nuclear sites in the US. In one case, leaking water contained of tritium per liter, which is 375 times the current EPA limit for drinking water, and 28 times the World Health Organization's recommended limit. Radioactive tritium leaks found at 48 US nuke sites. NBC News (21 June 2011). Retrieved on 16 October 2014. This is equivalent to or roughly 0.8 parts per trillion.

The US Nuclear Regulatory Commission states that in normal operation in 2003, 56 pressurized water reactors released of tritium (maximum: ; minimum: ; average: ) and 24 boiling water reactors released (maximum: ; minimum: 0 Ci; average: ), in liquid effluents. NRC: Frequently Asked Questions About Liquid Radioactive Releases "What are normal amounts of tritium released from nuclear power plants?" of tritium weigh about .


Regulatory limits
The legal limits for tritium in vary widely from country to country. Some figures are given below:
>
+ Tritium drinking water limits by country

!valign="bottom"

Country !valign="bottom"Tritium limit
(Bq/L) !valign="bottom"
Equivalent dose
(/year)
Australia76,1031,000
Japan60,000
Finland30,000
World Health Organization10,000
Switzerland10,000
Russia7,700
Canada (Ontario)7,000
United States740
Norway100

     
Germany100

     

The United States limit results in a dose of 4.0 millirems (or 40 micro in ) per year per EPA regulation 40CFR141, and is based on outdated dose calculation standards of National Bureau of Standards Handbook 69 circa 1963. Four millirem per year is about 1.3% of the average natural background radiation (~3 mSv). Updated dose calculation standards based on International Commission on Radiological Protection Report 30 and used in the NRC Regulation 10CFR20 results in a dose of 0.9 millirem (9 μSv) per year at 740 Bq/L (20 nCi/L).


Use

Radiometric assays in biology and medicine
Tritiation of drug candidates allows detailed analysis of their absorption and . Tritium has also been used for biological radiometric assays, in a process akin to radiocarbon dating. For example, 3H was traced through the bodies of rats.


Self-powered lighting
The beta particles from small amounts of tritium cause chemicals called to glow. This radioluminescence is used in self-powered lighting devices called betalights, which are used for night illumination of firearm sights, watches, , map lights, navigational compasses (such as current-use M-1950 U.S. military compasses), knives and a variety of other devices. , commercial demand for tritium is per year and the cost is

or more.


Nuclear weapons
Tritium is an important component in nuclear weapons; it is used to enhance the efficiency and yield of and the fission stages of in a process known as "boosting" as well as in external neutron initiators for such weapons.


Neutron initiator
These are devices incorporated in which produce a pulse of neutrons when the bomb is detonated to initiate the in the fissionable core (pit) of the bomb, after it is compressed to a by explosives. Actuated by an ultrafast switch like a , a small particle accelerator drives of tritium and deuterium to energies above the 15  or so needed for deuterium-tritium fusion and directs them into a metal target where the tritium and deuterium are as . High-energy from the resulting fusion radiate in all directions. Some of these strike plutonium or uranium nuclei in the primary's pit, initiating a nuclear chain reaction. The quantity of neutrons produced is large in absolute numbers, allowing the pit to quickly achieve neutron levels that would otherwise need many more generations of chain reaction, though still small compared to the total number of nuclei in the pit.


Boosting
Before detonation, a few grams of tritium–deuterium gas are injected into the hollow "pit" of fissile material. The early stages of the fission chain reaction supply enough heat and compression to start deuterium–tritium fusion; then both fission and fusion proceed in parallel, the fission assisting the fusion by continuing heating and compression, and the fusion assisting the fission with highly energetic (14.1 ) neutrons. As the fission fuel depletes and also explodes outward, it falls below the density needed to stay critical by itself, but the fusion neutrons make the fission process progress faster and continue longer than it would without boosting. Increased yield comes overwhelmingly from the increased fission. The energy from the fusion itself is much smaller because the amount of fusion fuel is much smaller. Effects of boosting include:
  • increased yield (for the same amount of fission fuel, compared to unboosted)
  • the possibility of by varying the amount of fusion fuel
  • allowing the bomb to require a smaller amount of the very expensive fissile material
  • eliminating the risk of predetonation by nearby nuclear explosions
  • not so stringent requirements on the implosion setup, allowing for a smaller and lighter amount of high explosives to be used

The tritium in a is continually undergoing radioactive decay, becoming unavailable for fusion. Also, its , helium-3, absorbs neutrons. This can offset or reverse the intended effect of the tritium, which was to generate many free neutrons, if too much helium-3 has accumulated. Therefore, boosted bombs need fresh tritium periodically. The estimated quantity needed is per warhead. To maintain constant levels of tritium, about per warhead per year must be supplied to the bomb.

One mole of deuterium-tritium gas contains about of tritium and of deuterium. In comparison, the 20 moles of plutonium in a nuclear bomb consists of about of plutonium-239.


Tritium in hydrogen bomb secondaries
Since tritium undergoes radioactive decay, and is also difficult to confine physically, the much larger secondary charge of heavy hydrogen isotopes needed in a true uses solid lithium deuteride as its source of deuterium and tritium, producing the tritium in situ during secondary ignition.

During the detonation of the primary stage in a thermonuclear weapon (Teller–Ulam staging), the sparkplug, a cylinder of U/Pu at the center of the fusion stage(s), begins to fission in a chain reaction, from excess neutrons channeled from the primary. The neutrons released from the fission of the sparkplug split lithium-6 into tritium and helium-4, while lithium-7 is split into helium-4, tritium, and one neutron. As these reactions occur, the fusion stage is compressed by photons from the primary and fission of the U or U/U jacket surrounding the fusion stage. Therefore, the fusion stage breeds its own tritium as the device detonates. In the extreme heat and pressure of the explosion, some of the tritium is then forced into fusion with deuterium, and that reaction releases even more neutrons.

Since this fusion process requires an extremely high temperature for ignition, and it produces fewer and less energetic neutrons (only fission and fusion are net neutron producers), lithium deuteride is not used in boosted bombs, but rather for multi-stage hydrogen bombs.


Controlled nuclear fusion
Tritium is an important fuel for controlled nuclear fusion in both magnetic confinement and inertial confinement fusion reactor designs. The National Ignition Facility (NIF) uses deuterium–tritium fuel, and the experimental fusion reactor will also do so. The deuterium–tritium reaction is favorable since it has the largest fusion cross section (about 5.0 barns) and it reaches this maximum cross section at the lowest energy (about 65  center-of-mass) of any potential fusion fuel. As tritium is very rare on earth, concepts for fusion reactors often include the breeding of tritium. During the operation of envisioned breeder fusion reactors, , often containing lithium as part of ceramic pebbles, are subjected to neutron fluxes to generate tritium to complete the fuel cycle.

The Tritium Systems Test Assembly (TSTA) was a facility at the Los Alamos National Laboratory dedicated to the development and demonstration of technologies required for fusion-relevant deuterium–tritium processing.


Electrical power source
Tritium can be used in a betavoltaic device to create an to generate .


Use in electron tubes
Tritium is used in various electron tubes, such as the Zellweger ZE22/3 glow tube. These devices contain a small amount of tritium to ionize the fill gas, typically a noble gas like or . This ionization ensures reliable and consistent operation by providing a steady current when a high voltage is applied, enhancing the device's performance and stability. The tritium is sealed within a glass envelope with two electrodes, one of which is coated with the radioactive material to create an ion path between the electrodes.


Use as an oceanic transient tracer
Aside from chlorofluorocarbons, tritium can act as a transient tracer and can "outline" the biological, chemical, and physical paths throughout the world's oceans because of its evolving distribution.

Tritium has thus been used as a tool to examine ocean circulation and ventilation and, for such purposes, is usually measured in tritium units, where 1 TU is defined as 1 tritium atom per 10 hydrogen atoms, equal to about 0.118 Bq/liter.

(2014). 9780080983004, Elsevier. .
As noted earlier, nuclear tests, mainly in the Northern Hemisphere at high latitudes, throughout the late 1950s and early 1960s introduced lots of tritium into the atmosphere, especially the . Before these nuclear tests, there were only about 3-4 kg of tritium on the Earth's surface; but these amounts rose by 2-3 orders of magnitude during the post-test period. Some sources reported natural background levels were exceeded by about 1,000 TU in 1963 and 1964 and the isotope is used in the northern hemisphere to estimate the age of groundwater and construct hydrogeologic simulation models.
(1993). 9780070397323, McGraw-Hill.
Estimated atmospheric levels at the height of weapons testing to approach 1,000 TU and pre-fallout levels of rainwater to be between 5 and 10 TU.

In 1963 Ireland recorded 2,000 TU in precipitation.Wunsch, Carl. (2015). Modern observational physical oceanography : understanding the global ocean. Princeton : Princeton University Press. p. 44 Figure 2.29. .


North Atlantic Ocean
While in the stratosphere (post-test period), the tritium interacted with and oxidized to water molecules and was present in much of the rapidly produced rainfall, making tritium a prognostic tool for studying the evolution and structure of the as well as the ventilation and formation of water masses in the North Atlantic.

Bomb-tritium data were used from the Transient Tracers in the Ocean (TTO) program in order to quantify the replenishment and overturning rates for deep water located in the North Atlantic.

Bomb-tritium also enters the deep ocean around the Antarctic.

Most of the bomb tritiated water (HHO) throughout the atmosphere can enter the ocean through the following processes:

  • precipitation
  • vapor exchange
  • river runoff
These processes make HHO a good tracer for time scales of up to a few decades.

Using the data from these processes for 1981, the 1-TU isosurface lies between 500 and 1,000 meters deep in the regions and then extends to 1,500–2,000 meters south of the due to recirculation and ventilation in the upper portion of the Atlantic Ocean. To the north, the isosurface deepens and reaches the floor of the which is directly related to the ventilation of the ocean floor over 10–20 year time-scales.

Also evident in the Atlantic Ocean is the tritium profile near between the late 1960s and late 1980s. There is a downward propagation of the tritium maximum from the surface (1960s) to 400 meters (1980s), which corresponds to a deepening rate of about 18 meters per year. There are also tritium increases at 1,500 m depth in the late 1970s and 2,500 m in the middle of the 1980s, both of which correspond to cooling events in the deep water and associated deep water ventilation.

From a study in 1991, the tritium profile was used as a tool for studying the mixing and spreading of newly formed North Atlantic Deep Water (NADW), corresponding to tritium increases to 4 TU. This NADW tends to spill over sills that divide the from the North Atlantic Ocean and then flows to the west and equatorward in deep boundary currents. This process was explained via the large-scale tritium distribution in the deep North Atlantic between 1981 and 1983. The sub-polar gyre tends to be freshened (ventilated) by the NADW and is directly related to the high tritium values (>1.5 TU). Also evident was the decrease in tritium in the deep western boundary current by a factor of 10 from the to the , which is indicative of loss to ocean interior due to turbulent mixing and recirculation.


Pacific and Indian oceans
In a 1998 study, tritium concentrations in surface seawater and atmospheric water vapor (10 meters above the surface) were sampled at the following locations: the , , the Bay of Bengal, , and the Strait of Malacca.

Results indicated that the tritium concentration in surface seawater was highest at the Fremantle Bay (about 0.40 Bq/liter), which could be accredited to the mixing of runoff of freshwater from nearby lands due to large amounts found in coastal waters. Typically, lower concentrations were found between 35 and 45° south, and near the . Results also indicated that (in general) tritium has decreased over the years (up to 1997) due to the physical decay of bomb tritium in the . As for water vapor, the tritium concentration was about one order of magnitude greater than surface seawater concentrations (ranging from 0.46 to 1.15 Bq/L). Therefore, the water vapor tritium is not affected by the surface seawater concentration; thus, the high tritium concentrations in the vapor were concluded to be a direct consequence of the downward movement of natural tritium from the stratosphere to the troposphere (therefore, the ocean air showed a dependence on latitudinal change).

In the North Pacific Ocean, the tritium (introduced as bomb tritium in the Northern Hemisphere) spread in three dimensions. There were subsurface maxima in the middle and low latitude regions, which is indicative of lateral mixing (advection) and processes along lines of constant potential density () in the upper ocean.

Some of these maxima even correlate well with extrema. In order to obtain the structure for ocean circulation, the tritium concentrations were mapped on 3 surfaces of constant potential density (23.90, 26.02, and 26.81). Results indicated that the tritium was well-mixed (at 6 to 7 TU) on the 26.81 isopycnal in the subarctic cyclonic gyre and there appeared to be a slow exchange of tritium (relative to shallower isopycnals) between this gyre and the anticyclonic gyre to the south; also, the tritium on the 23.90 and 26.02 surfaces appeared to be exchanged at a slower rate between the central gyre of the North Pacific and the equatorial regions.

The depth penetration of bomb tritium can be separated into three distinct layers:

Layer 1
Layer 1 is the shallowest layer and includes the deepest, ventilated layer in winter; it has received tritium via radioactive fallout and lost some due to advection and/or vertical diffusion and contains about 28% of the total amount of tritium.
Layer 2
Layer 2 is below the first layer but above the 26.81 and is no longer part of the mixed layer. Its two sources are diffusion downward from the mixed layer and lateral expansions outcropping strata (poleward); it contains about 58% of the total tritium.
Layer 3
Layer 3 is representative of waters that are deeper than the outcrop isopycnal and can only receive tritium via vertical diffusion; it contains the remaining 14% of the total tritium.


Mississippi River system
Trace amounts of radioactive materials from atomic weapons testing settled throughout the Mississippi River System. Tritium concentrations have been used to understand the of continental hydrologic systems such as lakes, streams, and rivers.

In a 2004 study, several rivers were taken into account during the examination of tritium concentrations (starting in the 1960s) throughout the Mississippi River Basin: (largest input to the Mississippi River flow), , and . The highest tritium concentrations were found in 1963 across locations throughout these rivers. The peak correlates with implementation of the US & Soviet atmospheric test ban treaty in 1962. The overall highest concentrations occurred in the Missouri River (1963) and were greater than 1,200 TU while the lowest concentrations were found in the Arkansas River (never greater than 850 TU and less than 10 TU in the mid-1980s).

As for the mass flux of tritium through the main stem of the Mississippi River into the Gulf of Mexico, data indicated that approximately 780 grams of tritium has flowed out of the River and into the Gulf between 1961 and 1997, an average of 21.7 grams/yr and 7.7 PBq/yr. Current fluxes through the Mississippi River are 1 to 2 grams per year as opposed to the pre-bomb period fluxes of roughly 0.4 grams per year.


See also


Footnotes

External links

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