General | |
---|---|
Name, symbol | tritium,3H |
Neutrons | 2 |
Protons | 1 |
Nuclide data | |
Natural abundance | trace |
Half-life | 12.32 years |
Decay products | 3He |
Isotope mass | 3.0160492 u |
Spin | 1⁄2 |
Excess energy | 14,949.794± 0.001 keV |
Binding energy | 8,481.821± 0.004 keV |
Decay modes | |
Decay mode | Decay energy (MeV) |
Beta emission | 0.018590 |
Tritium (/ˈtrɪtiəm/ or /ˈtrɪʃiəm/; symbol
T
or 3H
, also known as hydrogen-3) is a radioactive isotope of hydrogen. The nucleus of tritium (sometimes called a triton) contains one proton and two neutrons, whereas the nucleus of protium (by far the most abundant hydrogen isotope) contains one proton and no neutrons. Naturally occurring tritium is extremely rare on Earth, where trace amounts are formed by the interaction of the atmosphere with cosmic rays. It can be produced by irradiating lithium metal or lithium-bearing ceramic pebbles in a nuclear reactor. Tritium is used as a radioactive tracer, in radioluminescent light sources for watches and instruments, and, along with deuterium, as a fuel for nuclear fusion reactions with applications in energy generation and weapons. The name of this isotope is derived from Greek, Modern τρίτος (trítos), meaning 'third'.
Decay
While tritium has several different experimentally determined values of its half-life, the National Institute of Standards and Technology lists 4,500 ± 8 days (12.32 ± 0.02 years). It decays into helium-3 by beta decay as in this nuclear equation:
and it releases 18.6 keV of energy in the process. The electron's kinetic energy varies, with an average of 5.7 keV, while the remaining energy is carried off by the nearly undetectable electron antineutrino. Beta particles
from tritium can penetrate only about 6.0 mm of air, and they are
incapable of passing through the dead outermost layer of human skin. The unusually low energy released in the tritium beta decay makes the decay (along with that of rhenium-187) appropriate for absolute neutrino mass measurements in the laboratory (the most recent experiment being KATRIN).
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 produced in nuclear reactors by neutron activation of lithium-6. This is possible with neutrons of any energy, and is an exothermic reaction yielding 4.8 MeV. In comparison, the fusion of deuterium with tritium releases about 17.6 MeV of energy. For applications in proposed fusion energy reactors, such as ITER, pebbles consisting of lithium bearing ceramics including Li2TiO3 and Li4SiO4, are being developed for tritium breeding within a helium cooled pebble bed (HCPB), also known as a breeder blanket.
High-energy neutrons can also produce tritium from lithium-7 in an endothermic (net heat consuming) reaction, consuming 2.466 MeV. This was discovered when the 1954 Castle Bravo nuclear test produced an unexpectedly high yield.
Boron
High-energy neutrons irradiating boron-10 will also occasionally produce tritium:
A more common result of boron-10 neutron capture is 7Li
and a single alpha particle.
and a single alpha particle.
Deuterium
Tritium is also produced in heavy water-moderated reactors whenever a deuterium nucleus captures a neutron. This reaction has a quite small absorption cross section, making heavy water 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" processes up to 2,500 tonnes (2,500 long
tons; 2,800 short tons) of heavy water a year, and it separates out
about 2.5 kg (5.5 lb) of tritium, making it available for other uses.
Deuterium's absorption cross section for thermal neutrons is about 0.52 millibarns, whereas that of oxygen-16 (16
8O
) is about 0.19 millibarns and that of oxygen-17 (17
8O
) is about 240 millibarns.
8O
) is about 0.19 millibarns and that of oxygen-17 (17
8O
) is about 240 millibarns.
Fission
Tritium is an uncommon product of the nuclear fission of uranium-235, plutonium-239, and uranium-233, with a production of about one atom per each 10,000 fissions.
The release or recovery of tritium needs to be considered in the operation of nuclear reactors, especially in the reprocessing of nuclear fuels and in the storage of spent nuclear fuel.
The production of tritium is not a goal, but rather a side-effect. It
is discharged to the atmosphere in small quantities by some nuclear
power plants.
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 this water. This
identified that the March 2016 holding of tritium on-site was
760 TBq (equivalent to 2.1 g of tritium or 14 mL of tritiated water) in a total of 860000 m3
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.
Helium-3
Tritium's decay product helium-3 has a very large cross section for reacting with thermal neutrons, expelling a proton, hence it is rapidly converted back to tritium in nuclear reactors.
Cosmic rays
Tritium occurs naturally due to cosmic rays interacting with atmospheric gases. In the most important reaction for natural production, a fast neutron (which must have energy greater than 4.0 MeV) interacts with atmospheric nitrogen:
Worldwide, the production of tritium from natural sources is 148 petabecquerels
per year. The global equilibrium inventory of tritium created by
natural sources remains approximately constant at 2,590 petabecquerels.
This is due to a fixed production rate and losses proportional to the
inventory.
Production history
According to a 1996 report from Institute for Energy and Environmental Research on the US Department of Energy, only 225 kg (496 lb) of tritium had been produced in the United States from 1955 to 1996. Since it continually decays into helium-3, the total amount remaining was about 75 kg (165 lb) at the time of the report.
Tritium for American nuclear weapons was produced in special heavy water reactors at the Savannah River Site until their closures in 1988. With the Strategic Arms Reduction Treaty (START) after the end of the Cold War, the existing supplies were sufficient for the new, smaller number of nuclear weapons for some time.
The production of tritium was resumed with irradiation of rods containing lithium (replacing the usual control rods containing boron, cadmium, or hafnium), at the reactors of the commercial Watts Bar Nuclear Generating Station
from 2003–2005 followed by extraction of tritium from the rods at the
new 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 atomic mass of 3.0160492 u. Diatomic tritium (
T
2 or 3H
2) is a gas at standard temperature and pressure. Combined with oxygen, it forms a liquid called tritiated water (
T
2
O
).
T
2 or 3H
2) is a gas at standard temperature and pressure. Combined with oxygen, it forms a liquid called tritiated water (
T
2
O
).
Tritium figures prominently in studies of nuclear fusion because of its favorable reaction cross section and the large amount of energy (17.6 MeV) produced through its reaction with deuterium:
All atomic nuclei contain protons as their only electrically charged
particles. They therefore repel one another because like charges repel.
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 electrical repulsion (called the Coulomb force), and they can come close enough for the strong nuclear force to take effect, fusing them into heavier atoms.
The tritium nucleus, containing one proton and two neutrons,
has the same charge as the nucleus of ordinary hydrogen, and it
experiences the same electrostatic repulsive force when brought close to
another atomic nucleus. However, the neutrons in the tritium nucleus
increase the attractive strong nuclear force when brought close enough
to another atomic nucleus. As a result, tritium can more easily fuse
with other light atoms, compared with the ability of ordinary hydrogen
to do so.
The same is true, albeit to a lesser extent, of deuterium. This is why brown dwarfs (so-called failed stars) cannot utilize ordinary hydrogen, but they do fuse the small minority of deuterium nuclei.
Like the other isotopes of hydrogen,
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 fusion reactors, it may contribute to radioactive contamination, although 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 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
Tritium is an isotope of hydrogen, which allows it to readily bind to hydroxyl radicals, forming tritiated water (HTO), and to carbon atoms. Since tritium is a low energy beta emitter, it is not dangerous externally (its beta particles are unable to penetrate the skin), but it can be a radiation hazard when inhaled, ingested via food or water, or absorbed through the skin. HTO 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 bioaccumulation of HTO 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 the coastal region of Karnataka, India, show that the
biological half life in the winter season is twice that of the summer
season.
Environmental contamination
Tritium
has leaked from 48 of 65 nuclear sites in the US. In one case, leaking
water contained 7.5 microcuries (280 kBq) of tritium per litre, which is
375 times the EPA limit for drinking water.
The US Nuclear Regulatory Commission states that in normal operation in 2003, 56 pressurized water reactors released 40,600 curies (1.50 PBq) of tritium (maximum: 2,080 Ci; minimum: 0.1 Ci; average: 725 Ci) and 24 boiling water reactors released 665 curies (24.6 TBq) (maximum: 174 Ci; minimum: 0 Ci; average: 27.7 Ci), in liquid effluents.
According to the U.S. Environmental Protection Agency, self-illuminating exit signs improperly disposed in municipal landfills have been recently found out to contaminate waterways.
Regulatory limits
The legal limits for tritium in drinking water vary from country to country. Some figures are given below:
Country | Tritium limit (Bq/l) |
---|---|
Australia | 76103 |
Japan | 60000 |
Finland | 30000 |
WHO | 10000 |
Switzerland | 10000 |
Russia | 7700 |
Ontario (Canada) | 7000 |
United States | 740 |
The American limit is calculated to yield a dose of 4.0 millirems (or 40 microsieverts in SI units) per year. This is about 1.3% of the natural background radiation (roughly 3,000 μSv).
Use
Self-powered lighting
The beta particles emitted by the radioactive decay of small amounts of tritium cause chemicals called phosphors to glow. This radioluminescence is used in self-powered lighting devices called betalights, which are used for night illumination of firearm sights, watches, exit signs, map lights, knives and a variety of other devices. Tritium has replaced radioluminescent paint containing radium in this application, which can cause bone cancer and has been banned in most countries for decades. As of 2000, commercial demand for tritium is 400 grams per year and the cost is approximately US$30,000 per gram.
Nuclear weapons
Tritium is an important component in nuclear weapons. It is used to enhance the efficiency and yield of fission bombs and the fission stages of hydrogen bombs in a process known as "boosting" as well as in external neutron initiators for such weapons.
Neutron initiator
These are devices incorporated in nuclear weapons which produce a pulse of neutrons when the bomb is detonated to initiate the fission reaction in the fissionable core (pit) of the bomb, after it is compressed to a critical mass by explosives. Actuated by an ultrafast switch like a krytron, a small particle accelerator drives ions of tritium and deuterium to energies above the 15 keV or so needed for deuterium-tritium fusion and directs them into a metal target where the tritium and deuterium are adsorbed as hydrides. High-energy fusion neutrons
from the resulting fusion radiate in all directions. Some of these
strike plutonium or uranium nuclei in the primary's pit, initiating 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 plutonium or uranium. 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 MeV)
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 increase in fission. The energy released by the
fusion itself is much smaller because the amount of fusion fuel is so
much smaller. The effects of boosting include:
- increased yield (for the same amount of fission fuel, compared to detonation without boosting)
- the possibility of variable yield by varying the amount of fusion fuel
- allowing the bomb to require a smaller amount of the very expensive fissile material – and also 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 warhead is continually undergoing radioactive decay, hence becoming unavailable for fusion. Furthermore its decay product,
helium-3, absorbs neutrons if exposed to the ones emitted by nuclear
fission. This potentially offsets or reverses the intended effect of the
tritium, which was to generate many free neutrons, if too much helium-3
has accumulated from the decay of tritium. Therefore, it is necessary
to replenish tritium in boosted bombs periodically. The estimated
quantity needed is 4 grams per warhead. To maintain constant levels of tritium, about 0.20 grams per warhead per year must be supplied to the bomb.
One mole
of deuterium-tritium gas would contain about 3.0 grams of tritium and
2.0 grams of deuterium. In comparison, the 20 moles of plutonium in a
nuclear bomb consists of about 4.5 kilograms 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 hydrogen bomb 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 fission bomb stage in a thermonuclear weapon (Teller-Ullam staging), the sparkplug, a cylinder of U-235/Pu-239
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-238 or
U-238/U-235 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, deuterium-tritium fusion, and 7
3Li
splitting are net neutron producers), lithium deuteride is not used in boosted bombs, but rather for multi-stage hydrogen bombs.
3Li
splitting 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 experimental fusion reactor ITER and the National Ignition Facility (NIF) will use deuterium-tritium fuel. 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 keV center-of-mass) of any potential fusion fuel.
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.
Analytical chemistry
Tritium is sometimes used as a radiolabel.
It has the advantage that almost all organic chemicals contain
hydrogen, making it easy to find a place to put tritium on the molecule
under investigation. It has the disadvantage of producing a
comparatively weak signal.
Electrical power source
Use as an oceanic transient tracer
Aside from chlorofluorocarbons,
tritium can act as a transient tracer and has the ability to "outline"
the biological, chemical, and physical paths throughout the world 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 the ratio of 1 tritium atom to 1018 hydrogen atoms, approximately equal to 0.118 Bq/liter.
As noted earlier, nuclear weapons testing, primarily in the
high-latitude regions of the Northern Hemisphere, throughout the late
1950s and early 1960s introduced large amounts of tritium into the
atmosphere, especially the stratosphere.
Before these nuclear tests, there were only about 3 to 4 kilograms of
tritium on the Earth's surface; but these amounts rose by 2 or 3 orders
of magnitude during the post-test period.
Some sources reported natural background levels were exceeded by
approximately 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.
Recent scientific sources have 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 Valentia Island Ireland recorded 2,000 TU in precipitation.
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 hydrologic cycle as well as the ventilation and formation of water masses in the North Atlantic Ocean.
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 (HTO) throughout the atmosphere can
enter the ocean through the following processes: a) precipitation, b)
vapor exchange, and c) river runoff – these processes make HTO a great
tracer for time-scales 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 subtropical regions and then extends to 1,500–2,000 meters south of the Gulf Stream 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 abyssal plain which is directly related to the ventilation of the ocean floor over 10 to 20 year time-scales.
Also evident in the Atlantic Ocean is the tritium profile near Bermuda
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 approximately 18 meters per
year.
There are also tritium increases at 1,500 meters depth in the late
1970s and 2,500 meters 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 Norwegian Sea
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 Labrador Sea to the Tropics, 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 Sulu Sea, the Fremantle Bay, the Bay of Bengal, the Penang Bay, and the Strait of Malacca.
Results indicated that the tritium concentration in surface seawater
was highest at the Fremantle Bay (approximately 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 degrees south latitude and near the equator.
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 Indian Ocean.
As for water vapor, the tritium concentration was approximately one
order of magnitude greater than surface seawater concentrations (ranging
from 0.46 to 1.15 Bq/liter).
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 diffusion processes along lines of constant potential density (isopycnals) in the upper ocean. Some of these maxima even correlate well with salinity 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 3
distinct layers. 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 approximately 28% of the total amount of tritium.
Layer 2 is below the first layer but above the 26.81 isopycnal and is
no longer part of the mixed layer. Its 2 sources are diffusion downward
from the mixed layer and lateral expansions outcropping strata
(poleward); it contains about 58% of the total tritium.
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
The impacts of the nuclear fallout were felt in the United States throughout the Mississippi River System. Tritium concentrations can be used to understand the residence times
of continental hydrologic systems (as opposed to the usual oceanic
hydrologic systems) which include surface waters such as lakes, streams,
and rivers.
Studying these systems can also provide societies and municipals with
information for agricultural purposes and overall river water quality.
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: Ohio River (largest input to the Mississippi River flow), Missouri River, and Arkansas River.
The largest tritium concentrations were found in 1963 at all the
sampled locations throughout these rivers and correlate well with the
peak concentrations in precipitation due to the nuclear bomb tests 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).
Several processes can be identified using the tritium data from
the rivers: direct runoff and outflow of water from groundwater
reservoirs.
Using these processes, it becomes possible to model the response of the
river basins to the transient tritium tracer. Two of the most common
models are the following:
- Piston-flow approach – tritium signal appears immediately; and
- Well-mixed reservoir approach – outflow concentration depends upon the residence time of the basin water
Unfortunately, both models fail to reproduce the tritium in river
waters; thus, a two-member mixing model was developed that consists of 2
components: a prompt-flow component (recent precipitation – "piston")
and a component where waters reside in the basin for longer than 1 year
("well-mixed reservoir").
Therefore, the basin tritium concentration becomes a function of the
residence times within the basin, sinks (radioactive decay) or sources
of tritium, and the input function.
For the Ohio River, the tritium data indicated that about 40% of
the flow was composed of precipitation with residence times of less than
1 year (in the Ohio basin) and older waters consisted of residence
times of about 10 years.
Thus, the short residence times (less than 1 year) corresponded to the
"prompt-flow" component of the two-member mixing model. As for the
Missouri River, results indicated that residence times were
approximately 4 years with the prompt-flow component being around 10%
(these results are due to the series of dams in the area of the Missouri
River).
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 7.7 PBq/yr. And current fluxes through the Mississippi
River are about 1 to 2 grams per year as opposed to the pre-bomb period
fluxes of roughly 0.4 grams per year.
History
Tritium was first produced in 1934 from deuterium, another isotope of hydrogen, by Ernest Rutherford, Mark Oliphant, and Paul Harteck. However, their experiment could not isolate tritium, which was later accomplished by Luis Alvarez and Robert Cornog, who also realized tritium's radioactivity. Willard F. Libby recognized that tritium could be used for radiometric dating of water and wine.