How fire can be tamed
Graham R.L. Cowan
105, 1144 Division St., Cobourg, Ontario K9A 4J9, Canada
E-mail:
Abstract: Combustion dies at the interface between breathable air and
macroscopic pieces of certain involatile fuels. If fed only them, in a compressed
oxygen chamber, it makes an almost sun like flame that cannot run wild. If upon
dilution to manageable coolness the ash drops to the chamber bottom, and from
there can be removed without the diluent, true harness brokenness is possible.
Excess oxygen can be the diluent without thereby being wasted. It can rid itself
of the diluted flame’s heat, and spare many trees from becoming newsprint
bearing motor fuel mishap reports, by working in a thermodynamic cycle.
Some ashes, especially boria, both precipitate well from the diluted flame and
travel well. By visiting faraway solar or fission power stations, and returning to
the chamber as regenerated fuel, they can make combustion both docile, and
subsidiary to docile primary energies.
1 Introduction
Where fuel combustion seems most certain to continue and hugely increase, tame or not,
is in car motors. Taming it there can be considered to have six parts:
1 Liven up the oxygen (LUTO): equip cars with extractors of oxygen from air.
(These normally deny a little oxygen to air-breathing bystanders so as to provide it,
purified, to something that needs it so. On occasion they must cut that thing
entirely off in the bystanders’ favour. Accordingly, and to save space, they will be
called ‘oxygen deniers’ or ‘O-deniers’ from here on.)
Int. J. Nuclear Hydrogen Production and Applications, Vol. 1, No. 3, 2008 235
Copyright © 2008 Inderscience Enterprises Ltd.
2 Burners, learn to burn eclectically (BLeBE): choose a fuel whose ash can readily
be let out of a chamber full of hot compressed oxygen without letting much of the
oxygen come along. The fuel’s combustion must propagate in compressed oxygen
but die in air at breathable temperature and pressure.
3 Star-pyrolyse ash to fuel and oxygen (SPAFO): develop nuclear or solar power
stations to import the ash and convert it back to oxygen and fuel, the latter in small
uniform pellets shaped for feedability into pressure chambers.
4 Strongly confine oxygen in oxide (SCOO): make the inner surfaces of the oxygen
chamber of materials that hot, compressed, nearly pure oxygen cannot attack.
Include yielding surfaces so that when the fuel of part two burns within it, the
oxygen can expand and do work.
5 Let engines eat pellets (LEEP): equip cars with bins for the fuel pellets of part 3
and ways for the internal combustion engines of part 4 to take them from the bins.
6 Return ash to sender (RATS): Equip cars with bins in which ash can stay until
refuelling time, so that it then can be offloaded in exchange for fuel, and begin its
journey to the power stations (part 3).
A linear heap of one-carat (0.0002-kg) diamonds probably would satisfy the dying-in-air
condition of part 2. Strong heating at one end would cause the diamonds there to burn,
but the fire would not travel along the heap. Raising the pressure and, as part one implies,
making the oxygen less dilute could change this. But diamond ash is gaseous, and this
makes part two’s other requirement, that departing ash not take extra oxygen with it, hard
to meet.
Also, one variety of diamond ash is carbon monoxide, a gas that kills stealthily when
inhaled. Diamond fires, and carbon-oxidising fires in general, are not tame.
The earth’s atmosphere normally contains enough of the other diamond ash – carbon
dioxide – that the power stations of part three could import all the ash they would need
merely by letting it come to them in the wind. Part six would be unnecessary: all the cars,
all the power stations, and all of us would be in a single ash bin, the same one that now
contains just us and the cars. However, a car motor that burns diamonds in oxygen has
another difficulty: at present-day levels of efficiency, about half its power would go to the
oxygen denier.
A much smaller share would be taken if the heat engine could get the same heat using
much less oxygen. This turns out to be a real option, as potential fuels that are more
suitable than carbon in other ways typically also work their oxygen much harder.
2 Oxygen denier readiness
Although today’s oxygen deniers leave room for improvement, they are good enough to
go on with. A typical one is said to produce 34.5 kg/h of oxygen and mass 1590 kg.
Air sieve materials that let argon pass have been developed, but the portable oxygen
deniers now in commercial service use materials that sift out oxygen and argon alike.
Their normal product is a mixture with an oxygen mole fraction of 0.945, argon in the
same proportion to oxygen as in air, balance nitrogen (Santos et al., 2006).
236 G.R.L. Cowan
The theoretical work done by a single-stage compressor in feeding air through them has
been assessed in terms of megajoules per cubic metre of product at standard temperature
and pressure (STP). Plots of that work versus the production rate show it increasing
slowly for a while, then more quickly. For a commercial device using three different sieve
materials – Oxysiv 5, Oxysiv 7, MS S 624 – the knees in their plots appear, for the first
and last, respectively at 1.60 MJ/(STP m3) and 1.20 MJ/(STP m3). For Oxysiv 7, the greatest
work requirement is 1.02 MJ/(STP m3) (‘TE’ curves, Santos et al., 2006, Figure 4).
If Oxysiv 7 is used and a car motor turns a compressor that indeed has just one stage,
but is only 60% efficient, the car motor must provide 1.70 MJ/(STP m3) of shaft work.
That is 0.38 kilowatt-hours per kilogram of oxygen.
2.1 The fate of the argon . . .
At its simplest, a tame fire chamber would only let gas in, not out. It would admit no gas
but oxygen, and as much oxygen as came in would be incorporated into non-gaseous ash
and exit in that form.
Revised to use an oxygen denier like those available today, it would admit gases,
principally argon, that fire cannot condense. Argon would build up and the pressure
would increase. This would snuff the fire in one of a number of ways: increasing the
chamber pressure until no more oxygen could be injected, or until the chamber burst, for
instance. The fuel will not burn in air.
2.2 . . . And the resulting waste of oxygen
At the cost of increasing the oxygen denier’s energy demand by about 10%,1 this problem
can be solved. The extra energy would be needed to bring in that much more oxygen.
Along with argon, it will be allowed to flow back out of a small gas exit port. Argon’s
accumulation will thus be limited, and will not prevent continuous combustion.
The oxygen denier that takes 0.38 shaft kWh per produced kgO2 will therefore need
0.42 shaft kWh per kilogram of oxygen that the fire actually uses.
NIST data imply that a fire whose minus-delta-’G’ at 298.15 K is 1 kWh must, if
zirconium-fuelled, consume 0.111 kg of oxygen. Most other fuels take more: carbon
takes 0.292 kgO2/kWh, iron, if being oxidised to the (II, III) oxide magnetite, takes
0.226 kgO2/kWh (Linstrom and Mallard, 2005).
Multiplying these oxygen requirements by 0.42 kWh/kgO2 yields the fractions of the
fire’s energy the O-denier would take: for zirconium 0.0466, for carbon 0.123, and for
iron 0.0952. But since the O-denier runs on mechanical work, these fractions need to be
divided by a typical heat engine efficiency, say 0.3, and for zirconium, carbon, and iron
that gives 0.155, 0.409, and 0.317.
2.3 Capping the oxygen denier’s fractional take . . .
If there is a type of mechanical linkage that can divide the power from a turning shaft in
a fixed proportion between two loads, it could ensure that an O-denier that is expected to
need 0.317 of the power of the motor it feeds can never take more than 0.32.
The energy cost of extracting oxygen from air rises as the oxygen fraction diminishes,
so with such a power-fraction-limiting linkage, an oxygen denier might fall behind the
motor’s oxygen demand if its intake air began to contain less than 20% oxygen.
How fire can be tamed 237
2.4 . . . means a motor can starve for oxygen . . .
The motor would begin to lose oxygen pressure, and therefore power. The O-denier, able
to take no more than the fixed fraction of the now reduced power, would still not be able
to keep up. Soon it and the motor would stop.
2.5 . . . in the midst of plenty
This turns out to be just what they ought to do. People in a freezing house may someday
seek warmth in the garage by using there, as a furnace, an air-breathing car that oxidises
some carbon-free fuel. If the car has an oxygen denier that cannot, as it deoxygenates the
garage’s air, take more power to compensate, it will soon live up to its name by cutting
off the motor.
It will do this even though, with a less stingy allocation of the motor’s output, they
both might still have been running hours later, long after hypoxia, unheralded by any rise
in carbon dioxide levels, had stealthily and permanently shut down the people.
Portable oxygen deniers’ energy needs can in theory still decline by an order of
magnitude. If reductions continue incrementally, designers who pair them with heat
engines will be obliged incrementally to ratchet down, also, the fraction of the engines’
output they can take, keeping it barely over the minimum needed in fresh air.
Calling them oxygen deniers may make this critical denial function harder to overlook.
2.6 The inert hordes dodged a bullet
The necessity of thinking about hypoxia arises not just with tame fires but with the
encompassing class of carbon-free fuel-air reactions.
After hydrogen cars were impressively demonstrated in the mid to late 1970s, many
hoped or believed they were within 5–10 years of catching on. Had this been true, perhaps
by the late 1980s all cars would have been safe for prolonged running indoors, but that
safety is not intrinsic to hydrogen-air flames nor to fuel cell cathodes.
2.7 Internal iron combustion power
If a truck has a 1590-kg oxygen denier that provides 34.5 kg of oxygen per hour, and of
that, the fire in its heat engine combines 31.4 kg per hour with iron to form magnetite, it
will go:
238 G.R.L. Cowan
although perhaps not very quickly. Using 0.3 for heat engine efficiency, the above yields
for carbon 19 kW (26 hp), for iron 28 kW (38 hp), and for zirconium 72 kW (96 hp).
Dividing the fire’s oxygen consumption rate by the net power yields oxygen consumption
per net shaft kWh: carbon takes 1.65 kgO2/kWh, iron takes 1.12 kgO2/kWh, and zirconium
takes 0.44 kgO2/kWh.
Net power_(31.4 kg O2 per hour) *
(heat engine efficiency/mass of oxygen required per unit energy yielded by fire
_ (0.42 kWh per kg O2 ))
3 Burners, learn to burn eclectically (BLeBE)
The fuel chosen should burn readily enough in purified compressed oxygen, but be
non-ignitable in breathable air. If pulverisation would make it ignitable in air whereas
in palpably large pieces it is not, then in a fire-taming effort one would not pulverise it.
The side effects of making it inhalable and hard to clean up when spilled, would also be
avoided. Similarly, one would not have it generate another fuel, one that burns readily or
explosively in air, by taking oxygen from that other fuel’s ash.
Aluminium is the best-known fireproof fuel, but there are others. They include
beryllium – toxic and very expensive – and boron and silicon. They include heavier
elements, such as the above-mentioned zirconium, that clothe themselves in oxide films
that strongly impede ignition. If a net shaft kWh from a zirconium-burning vehicle motor
requires 0.44 kg oxygen, which over time averages roughly half in the ash reservoir, half
in the atmosphere or in transit back to it, then that kWh also requires 1.23 kg zirconium,
which is always on board.
With boron, aluminium, and silicon the always-on-board masses are, respectively,
0.276, 0.483 and 0.485 kg, and the combining oxygen masses are 0.613, 0.430 and 0.552
kg, per net shaft kWh. This again is on the basis of 0.3 heat engine efficiency and an
oxygen denier that requires 0.42 kWh per combining kilogram of oxygen. Unless for some
heavy element there is a compelling reason to accept the extra mass, tame combustion
should be fed one of these three.
The net-power calculation of the previous section predicts 51 kW for boron, 73 kW
for aluminium, and 57 kW for silicon. The truck mentioned there could keep up with
traffic if it were burning any of these.
3.1 Ability of ash to precipitate from diluteness in hot oxygen
An ash that fails to do this, and is produced in a flame much hotter than a solid pressure
envelope can bear, will not lend itself to that flame’s dilution down to bearable
temperature with excess oxygen, for letting the ash out will tend to entail also letting out,
and wasting, the oxygen.
If, however, cooling due to dilution causes the ash to condense and fall out, a quantity
of oxygen can repeatedly do three things – dilute ash, drop it, and rid itself of the heat the
ash gave it by acting as heat engine working fluid – before in its turn being incorporated
into ash and falling to the vessel’s bottom.
Among combustibles that will not burn in air, few present any difficulty for the
ash-fall part of this scheme; maybe only osmium, since its tetroxide’s normal boiling
point is 403 K. If there are osmium-burning-car enthusiasts, their dream will not be
advanced by the taming of fire.
Of elemental boron, aluminium, and silicon, none is screened out, for their ashes
– boria, corundum (aka alumina), and silica – all have normal boiling points well above
2000 K. By the time their flames in oxygen have diluted themselves below this temperature,
they have become smoke plumes, upwellings of hot oxygen in which involatile ash particles
fall slowly.
How fire can be tamed 239
3.2 Selective removability of precipitated corundum
If the purpose the smoke is to serve is expanding and pushing a piston in a cylinder, this
typically needs to be repeatable with the same piston and cylinder about 100 million
times: thousands of times per minute for thousands of hours. This will not happen with
corundum-bearing oxygen, as corundum is abrasive. In an environment of hot dusty
oxygen that is just beginning to do its work of expansion in an efficient automotive heat
engine, at the temperature of the surface upon which the oxygen presses, corundum is
harder than any other material that would be stable.
That surface could well be made of corundum. Strong confinement of oxygen in
oxide (SCOO) calls for a strong oxide. Corundum is a strong oxide. But if they are not
to scratch it, ash particles in the oxygen must be made of something softer.
Aluminium-burning rocket motors embody another solution to this problem – accept
a short lifetime. But there may be a way an aluminium burner can live a long life, despite
expelling corundum dust throughout it: let aluminium fill its combustion chamber, as
liquid, and burn oxygen in an inverse flame in mid-metal.
Liquid aluminium has a history of being fairly successfully managed, including
travelling hundreds of kilometres on public highways as 5-m3 crucibles-full. At departure
from a foundry such a load is at 1150–1200 K. Ideally it has not yet cooled below 1050 K,
more than 100 K above its freezing temperature, when it arrives at a casting site.
It seems reasonable that compressed oxygen injected from non-oxidisable nozzles
deeply submerged in pressurised liquid aluminium would be consumed near the nozzles,
none of it reaching the upper surface, and that the combustion products would initially
rise through the liquid as bubbles, but quickly lose heat to it and collapse. Farther up, the
flame would be one of hot liquid metal carrying corundum particles up through cooler
liquid metal.
Compared to a corundum-bearing updraft of oxygen, this other convecting fluid
offers the advantage that a material exists – aluminium diboride – that promises to resist
both it (through being saturated with it) and its corundum particles (through possibly
superior hardness). Although combustion would be internal to the liquid metal, it would
be external to aluminium diboride heat exchanger tubes placed in the updraft’s way, so
the system would be an external combustion engine. The working fluid in the tubes could
not be oxygen, but it would not have to be.
At the chamber bottom, where the liquid aluminium would be relatively cool, there
could be a drain with a screw impeller in it, both also made of aluminium diboride, in
order to let the precipitated corundum particles and the liquid metal entrained by them
exit as a sludge or paste. The drain would give onto a chamber where aliquots of the
sludge would fall onto a draining surface. As much liquid metal as might readily drain
out of them would do so, and be returned to the upper chamber. The aliquots would then
be cooled and put in an ash ingot bin.
This would amount to somewhat unselective ash removal because some liquid
aluminium between particles would get frozen into the ingots. Per net shaft kWh, more
than the previously noted 0.483 kg of aluminium would move from fuel bin to ash bin.
By helping to hold the ash ingots together, the unburned metal would aid in returning ash
to sender (RATS).
240 G.R.L. Cowan
3.3 Selective removability of precipitated boria and silica
Boron melts above 2000 K and silicon at 1687 K. Neither, when burned with pure oxygen,
can usefully be present in excess to dilute the flame, for neither shares aluminium’s
ability to remain fluid when cooled to temperatures well below the maximum a heat
engine’s solid parts can long endure. Because of this, they cannot coolly surround a flame
that starts out much hotter than that maximum and through turbulent mixing form a
diluted flame whose temperature is just right. Of the flame’s two reagents, only the
oxygen can do this. The result is a smoke of boria in oxygen or silica in oxygen.
Either smoke’s expansion would be less rough on a heat engine than that of
corundum-laden oxygen. Silica, whose crystals melt at 1983 K, is, like every
non-corundum ash that might be so suspended, less abrasive than corundum. If it
originally was vapour and has become a suspended condensate through being diluted and
cooled by the oxygen around it, boria exists as droplets, which supercool. When they land
on a surface that is hotter than about 0.8 of boria crystals’ 723-K melting point, they coat
it. Water droplet impact in engines powered by wet steam can be destructive, but boria
droplets are very different. A film formed by earlier-arriving boria droplets can so cover
a surface that latecomers cannot abrade it at all.
On oxygen-boron combustion chamber walls warm enough for accreting boria
droplets to merge into a film, the film will flow. Along with direct droplet precipitation,
this flow can create a chamber-bottom boria lake. A dynamic equilibrium can be
established where boria comes to the lake’s surface and, at the same rate, removes itself,
plus as much oxygen as was soluble in the surface layers, through a lake-bottom drain.
This removal is selective because gaseous oxygen cannot get down there.
If in the drain the boria has a temperature of 873 K, somewhat cooler than liquid
aluminium, it is runny enough to drain at a useful rate. Unlike a paste of corundum and
liquid aluminium, it is entirely liquid and unabrasive. It needs no screw impeller to help
it along.
Its dynamic viscosity and density, represented below by ‘_’ and ‘_’, are 480 pascal
seconds and 1608 kg/m3 (Smith and McBroom, 1999). A 0.25-m-deep lake of it that is
held at a combustor bottom by its standard terrestrial weight of 9.80665 N/kg will have
a top-to-bottom hydrostatic pressure difference, represented below by ‘_p’, of 3942 Pa.
A laminar flow calculation that neglects end effects:
How fire can be tamed 241
predicts that boria will exit through a circular hole in the bottom at a rate of 0.0189 kg/s
if the hole’s length L and diameter D are both 0.0388 m, and its walls are at the same
873-K temperature as the liquid.
In preparation for return of ash to sender – RATS – the boria extruding below the
bottom of the drain could periodically be cut off. The now detached gob could be cooled
by air flow, and then, with a little more air flow, blown into its bin.
Raising the temperature by 200 K could speed the flow up about 18-fold. A spun lake,
held to its bed by centrifugal force rather than planetary gravity, could drain much faster
still. But the 0.0189-kg/s oozing, with an average flow speed of 0.0100 m/s, turns out to
be adequate for draining the small volumes per unit time that a car-scale combustor
would produce. According to the previously noted per-net-shaft-kWh boron and oxygen
Mass throughput _ π _ D∧4* (_p)/(128 _L)
masses, which sum to 0.889 kg, the net driveshaft power that could be co-produced is
76 kW.
For silica that mass sum is 1.037 kg, highest of the three fuel-ash pairs under
consideration. Since corundum is more abrasive than silica, conceivably an engine
powered by expansion of hot compressed silica-bearing oxygen could be internally
surfaced with corundum, and not be eviscerated by the silica particles. But wherever they
settled, they would tend to stay. They would not be able to merge and flow. If they did
merge, it would amount to sintering. Perhaps they would form tough artificial quartzite
or vitreous silica scale on heat engine surfaces. Along with the extra mass, this prospect
makes internal silicon combustion relatively uninteresting.
4 Central station deoxidation
Billions are determined to become motorists. One way or another, motor fuel production
rates will rise by many terawatts over the next few decades. They can be increased cleanly
by constructing nuclear or solar power stations that take in alumina or boria ingots
and remove the oxygen. Such stations could be rated in terms of aluminium terawatts,
TW(Al), or boron terawatts, TW(B).
If each station were to produce 0.1 TW(Al), it would make about three times as much
as all of today’s smelters. Since this is roughly a two-orders-of-magnitude increase in
individual plant scale, by the inverse-square-root-of-scale rule (Marchetti, 2006), product
unit cost would decline by one order of magnitude, from around US$0.30/kWh(Al) down
to about US$0.03/kWh(Al). In aid of this cost reduction, inert anodes might be put
into service (Welch, 1999), so that where now a significant fraction of the energy stored
in aluminium comes from oxidising carbon anodes, scaled-up plants would need only
electricity.
A 0.1-TW(B) power station might need only heat, provided heat of a certain intensity
was available. Boria follows the general rule for very stable oxides that mere direct
heating, however intense, will not cause macroscopic separation into fuel and oxygen.
Star pyrolysis of ash to fuel and oxygen (SPAFO) yields fuel and oxygen atoms. They
remain mixed, and will not refrain from reattaching to each other if one cools the vapour
down to a temperature where, if they would so refrain, separation might conveniently occur.
However, heat from a source significantly hotter than 2500 K can usefully act on
another oxide that is less stable, and – being an ore of iron – very much cheaper and more
abundant: magnetite (Ehrensberger et al., 1997; Mohai et al., 2007):
(l_x)/(1_4x) Fe3O4→ (1/2) O2 _ 3/(1_4x) Fe(1_x)O(liq)
For x_0, NIST data imply this process has enthalpy change _372.3 kJ/mol, plus another
39.2 kJ/mol that the oxygen would give back in being cooled from 2500 to 298.15 K.
Being liquid, the ferrous oxide tends to separate from the oxygen, so they can be cooled
without recombining.
Losing the 39.2 kJ would be reasonable for a solar power station that focussed a large
image of the sun down onto a high-altitude outdoor stream of magnetite, for then the
half-mole of oxygen could go directly into the upper air. If such a station annually turned
32.6 billion kg of magnetite into 1.9 billion kg of oxygen and 30.7 billion kg of ferrous
oxide, its annual average output could be expressed as 1 GW(FeO).
242 G.R.L. Cowan
Where summer is much sunnier than winter, ferrous oxide production rates in winter,
spring, summer, and fall might average respectively zero, 1, 2, and 1 GW(FeO). By
summer’s end, 7.7 billion kg of ferrous oxide, a gigawatt-season’s worth, could
accumulate, perhaps as an outdoor conical heap 300 m across the base. If a steady
year-round ferrous oxide gigawatt were taken, the iron by winter’s end would be in a slightly
larger magnetite pile. Other kinds of gigawatt-season energy reservoir – two billion
lead-acid car batteries, a cubic km of water raised 800 m – are larger or more costly
or both.
Boria, like corundum, can dissolve in molten salts. Converted to 300–400 MW of
electricity, the GW(FeO) could electrolyse it there year-round, but it may also be able to
react directly with ferrous oxide and nitrogen, in a way that corundum cannot:
How fire can be tamed 243
This condenses nitrogen without producing any other gas, but is exothermic and
spontaneous at room temperature and pressure.
Raising the nitrogen pressure to a few tens of MPa should make it go at 500 K. Some
compound of boria and ferrous oxide may be so stable as to sidetrack it, or it may still
be too slow. It should be tried. If boron nitride and magnetite are seen to be producible
quickly enough, and they can be separated, three more spontaneous reactions will lever
boron up to freedom:
The above would transform the problem of deoxidising boron into one of converting
magnetite and ferrous halides back into free halogens, ferrous oxide, and iron. This
highly exothermic reaction would free the halogens:
Iron could be produced by consuming more ferrous oxide.
Finally, the magnetite could become oxygen and ferrous oxide,
and the ferrous oxide could freeze, and if x_0, 29 moles of ferrous oxide would have
been oxidised to 29/3 moles of magnetite and then recovered. Magnetite’s above-noted
372.3-kJ/mol enthalpy of partial deoxidation, times 29/3, gives the delta H of this step:
3.98 MJ/mol if oxygen is let go while still hot, 3.60 MJ/mol if its heat is recovered.
The net result would be the dissociation of one mole of boria, delta H _1.25336 MJ.
Of 3.98 MJ, that is 31.5%, about the same as if electricity had been made, but boria can
be wirelessly gathered in, and boron wirelessly distributed.
The magnetite heating could occur in an annular curtain of falling particles bathed
in rising high-pressure helium. Each particle would begin its fall as a magnetite particle.
As it descended it would give up oxygen until it was a ferrous oxide particle. The oxygen
would be swept upwards by the helium.
The heat could be radiant heat from a central fountain of chunks of an actinide
element or a mixture of actinides. Fission in the chunks would melt and evaporate them
so that they would merge as they approached the apices of their free flights. Because their
vapour would always be much denser than the surrounding helium, each chunk’s expanded
remains, although flying upwards as the chunk had been, would still be decelerating and
soon would fall back. The structure would be a dense vapour fountain.
Continuing fission in the vapour slug a chunk had become, would raise its temperature.
The resulting expansion would reduce its opacity to neutrons, so the process would limit
itself. As it fell back, later-arriving chunks, still condensed, could pass through it.
Surrounding this fountain and reflecting neutrons to it, would be a region filled
with cool flowing helium. The high transparency of helium to thermal radiation would
allow it to fill the space between the fountain and the sheath of iron oxide particles while
remaining cooler than either. Its flow would continuously remove the dense vapour
fountain’s outer surface, the remains of the longest-serving chunks, and carry it downwards.
Compared to operation at normal atmospheric pressure, the high pressure would
serve two purposes. One is to enable the cool helium to promote chain fission by
converting fast neutrons that escape the fountain into cool thermal ones before they have
gone far, so that they have a good chance of diffusing back into it.
If nuclei of natural uranium are the only ones in the vapour, these returning
cool neutrons are more likely to cause fission than in the case where they are captured
while still fast, because they are more likely to avoid capture by nuclei of the 99.28%
non-fissionable majority, and instead be captured by the fissionable minority. If the
surrounding helium has to cool too many neutrons, and its temperature increases over
time, so does theirs, and their selectivity diminishes. Therefore, in raising its own
temperature, this reactor would reduce its moderator’s effectiveness, and in so doing,
would reduce its own power. This self-regulating tendency is one it would share with
existing nuclear power reactors.
The second purpose pressure would serve is to raise the temperature at which the
actinide would boil, and thereafter reduce the rate at which it would expand, so that it
could stay near the centre longer, reach a higher temperature, and shine more strongly on
the iron oxide.
The cascade of actinide vapour and the sheath of helium, neutron-heated nearest
the vapour but still cool farther out, would together descend through a ring of nozzles
that would douse them with fluoride particles. This would condense the actinide vapour,
making the heat earlier stored in it unusable for magnetite pyrolysis, so ideally, for
efficiency’s sake, each piece of vapour would shine away much more energy during its
time of high luminosity than it would then spend in this manner.
The fluoride particles might be 16 mole parts sodium fluoride, four parts potassium
fluoride, and five parts magnesium fluoride, a composition sometimes referred to as
244 G.R.L. Cowan
NaF-16KF-20MgF2. It melts at 1077 K (Misra and Whittenberger, 1987). The amount
thrown into the descending flame would be adjusted so as to end up above this
temperature, in the hope that the particles of actinide soot would end up inside its
droplets, and there give up some fission fragments to it (Lemort, 1997):
How fire can be tamed 245
Gravity and a small pressure difference, maybe 1 kPa, together would pull the droplets,
any unincorporated actinide soot grains, and the helium around them all down into a
lower chamber. There they would impinge straight down upon the centre of a broad pool
of liquid magnesium near its 923-K freezing point. Falling into this, the fluoride droplets
would freeze into beads. These beads and the actinide soot, some of it inside them and
isolated from the liquid, would fall through it and come to rest on a layer of older beads.
The beads and soot would contain fast-decaying fission fragments. An influx of
pieces of solid magnesium would be maintained, therefore, to keep the liquid magnesium
near its freezing point. They would sink through it alongside the beads and lie with them
on the bead layer, and be melted by decay heat there. As much magnesium as was being
added as solid would be removed from the surface as liquid and dropped through helium,
which would take away the heat, probably to a heat engine.
The oldest, least heat-producing beads and soot grains would be at the bottom of
the bead layer. Under them would be a deep foundation of solid NaF-16KF-20MgF2.
It would extend far enough down to provide a long-term backup heat sink. After
solid magnesium pieces have stopped being thrown in, and all present have melted, the
liquid magnesium warms to 1077 K and the beads immersed in it melt. They form a
liquid NaF-16KF-20MgF2 layer between the solid fluoride and the magnesium. The
actinide grains formerly trapped in them fall onto the solid fluoride. Their continuing but
diminishing heat production drives the liquid-solid interface downwards. Occasionally it
reaches pockets of magnesium and causes them to drain upwards. Eventually the inward
leakage of the outside world’s coolness overwhelms the fission fragments and the melt
front becomes a freeze front. It rises above the grains, trapping them.
Usually the beads would not be allowed to melt and a dredge could selectively dredge
the deepest-down, least heat-producing ones off the solid NaF-16KF-20MgF2 surface.
The liquid magnesium could be evaporated off them, and then they could be pulverised
under liquid xenon. NIST tables say natural air-derived xenon at 175 K is dense enough
under its own 173.25-kPa vapour pressure to float NaF-16KF-20MgF2 bead fragments
but not actinide soot grains (Lemmon et al., 2005).
An alternative fluoride composition, NaF-13MgF2-22CaF2, melts at 1027 K (Misra
and Whittenberger, 1987). That is 50 K lower than NaF-16KF-20MgF2, but still higher
than magnesium’s freezing point, so much the same actinide-soot-gathering and
bead-forming behaviour can be expected of it. However, its floatability in liquid natural
xenon, even at the latter’s triple point, is uncertain. A better bet for floating it would be
the large amounts of slightly denser xenon that can be extracted from existing commercial
reactors’ spent fuel.
The actinide soot would be taken out from under the liquid xenon and the fluoride
bead fragments skimmed off the top. The soot would be pressed into chunks. Flung again
up the fountain’s axis, they would again become bright aliquots of vapour. The fluoride
would be used to cool the fountain’s effluent again.
Helium in the gas lying over the liquid magnesium would be cooled, filtered, and
returned to its place surrounding the fountain and enabling it to shine. Some fission
fragments’ inability to pass through the helium filters, and others’ binding by the fluoride,
are what make requiring the fuel to boil itself reasonable: those fission fragments not
incorporated when it condenses are promptly trapped in a trap good enough to be their
final resting place.
5 Summary
Fuelling combustion only with pellets of aluminium or boron, small but not so small as
to be difficult to see and handle individually, can tame it. Compared to burners of oil in
air, internal boron combustion cars and external aluminium combustion ones would both
significantly advance safety, as spilled aluminium or boron pellets would not be able to
burn in the dilute, low-pressure oxygen we live on.
Non-combustion primary energies can supply aluminium and boron by extracting
them from their oxides. These would conveniently be available as tame combustors’
well-consolidated ash ingots, as the same use of purified oxygen that overcomes these
fuels’ ignition resistance also makes it easy to retain their ashes.
Cars would need machinery to make ingots and bins to hold them. They would need
oxygen deniers. These O-deniers would reduce the engines’ net efficiency by taking some
of their output, and they and the ash bins would make cars larger and heavier, other things
being equal, than oil burners.
5.1 Implications
The cars would advance environmental stewardship: ashes would not be emitted to the
atmosphere. Chemically unaltered air would carry waste heat away in a stream that would
probably be directed aft, and the oxygen denier would emit another relatively slow,
relatively narrow stream of slightly oxygen-depleted air, probably upwards.
The cars would advance ease of use. Letting the ashes of hydrocarbon motor fuels
simply blow away can be easier than dealing with ash ingots, but certain ways of dealing
with the fuels themselves, ways that would otherwise be convenient, would cause frequent
severe accidents. Like the severe but infrequent harm of post-crash fuel-fed fires, these
large risks can be reduced to zero, and the potential conveniences made actual, by a
switch to innocuous fuel that will not burn.
People who carry flasks of reserve fuel in their cars may appreciate the following
illustration. The low-fuel light has been on for some time. The car falters. Reaching into
the back seat without looking, one raises the reserve flask’s lid and scoops out a handful
of aluminium or boron pellets. The car falters again, and in haste one fumbles some of
the handful onto the cabin floor. The rest are successfully dropped into the in-cabin
refuelling port. They roll down its throat into the main fuel bin in the front bumper. No
further hesitation occurs; additional handfuls cause the low-fuel light to go out. The
dropped pellets can be let lie until one is at one’s destination, then gathered up and put
back in the reserve flask.
Compared to those of liquid hydrocarbon-burning cars, zero-local-emission cars’
stores of propulsion energy have been significantly less convenient to replenish and much
smaller. The bargain they have offered early adopters has not been cachet for a price, but
246 G.R.L. Cowan
cachet for two prices: pay more and tolerate more inconvenience. Early adopters of tame
combustion cars would also have to pay more, but convenience would become one of two
benefits rather than one of two costs.
Having two refuelling ports on a car, one inside the cabin and one outside, is one such
potential convenience. Another is the option of buying the car and its whole lifetime
supply of about 10 m3 of fuel at the same time. Neither geometry nor prudence would
forbid storing the fuel in one’s 200 m3 basement apartment, and refuelling at home.
The ash ingots would not be so compact. Home refuellers could accept the
inconvenience of packaging them and shipping them off to power stations, but fuel
retailers would soon see an opportunity in doing this for them. Since the aluminium or
boron pellets would be uniform, durable, and non-ignitable in air, a fuel bin wall
ventilated with holes too small for them to fit through would let a retailer blow them in
with an air hose. The ash ingots might need two hoses, one to vacuum and one to blow.
This and the fuel transfer could be done simultaneously. The whole three-hose process
could be quick.
5.2 Prediction
When developed, tame combustion cars will promptly take over the high end of the car
market and then push hydrocarbon-air combustion progressively down and out.
References
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from CO2 with iron oxides and high-temperature solar energy’, Industrial & Engineering
Chemistry Research, Vol. 36, pp.645–648.
Lemmon, E.W., McLinden, M.O. and Friend, D.G. (2005) ‘Thermophysical properties of
fluid systems’ in P.J. Linstrom and W.G. Mallard (Eds), NIST Chemistry WebBook, NIST
Standard Reference Database Number 69, National Institute of Standards and Technology,
Gaithersburg MD, 20899, June. Available at: http://webbook.nist.gov.
Lemort, F. (1997) ‘Étude de la Séparation Actinides-Lanthanides des Déchets Nucléaires par
un Procédé Pyrochimique Nouveau’, Commissariat à l’Energie Atomique France Rapport
CEA-R-5760, pp.173–174. Available at: http://www-ist.cea.fr/publicea/exl-doc/
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How fire can be tamed 247
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Notes
1 One of the things determining how many kilograms of oxygen an O-denier must supply per
kilogram a tame fire uses is the minimum allowed oxidiser fraction in the tame fire chamber,
represented below by t. Air’s 0.21 is by definition significantly less than t.
Supposing t_0.6, assuming nitrogen behaves as an inert gas, and setting the oxygen denier
product’s oxygen, argon, and nitrogen mole fractions xO2
, xAr, and xN2
respectively to 0.945,
0.042, and 0.013:
248 G.R.L. Cowan
yields a value near 1.096.
Nitrogen in the chamber does not behave exactly as an inert gas, however. Were it to show
complete non-inertness, every molecule combining with two oxygen molecules to form two
nitrogen dioxide molecules, it would make its volume and diluting effect zero by hiding itself
in the oxidiser. xN2
would disappear from the ratio expression:
For the same t and mole fractions, that is around 1.071.
A catalytic converter might be needed in the gas exit channel to deal with nitrogen dioxide.
It would have about 75 times less gas to scrub than its counterpart in an oil/air-burning car, so
a bed of alkali, although consumable, might serve well enough instead.
Keywords: alternative fuels; decarbonisation; energy carriers; energy storage;
fireproof fuels; fuel safety; hydrogen economy; hydrogen public acceptance;
hypoxia; ignition resistant fuels; nuclear production of motor fuels; solar
production of motor fuels; tame combustion; tame fire; zero emission vehicles.
Reference to this paper should be made as follows: Cowan, G.R.L. (2008) ‘How
fire can be tamed’, Int. J. Nuclear Hydrogen Production and Applications,
Vol. 1, No. 3, pp.235–248.
Biographical note: Graham Cowan obtained a programming diploma from the
Honeywell Institute in 1984. He is a researcher in clean vehicle propulsion. His
interests include solar and nuclear hydrogen production for use as motor fuel,
and direct nuclear propulsion of larger vehicles, including air-cooling of their
reactors without irradiation of the air, through the use of low-vapour-pressure
oxides as heat transfer media. He has published popular articles and a technical
conference paper on these same oxides’ potential to be manageable ashes in
combustion power systems.