Method to regenerate oxygen traps
10428433 · 2019-10-01
Assignee
- Universite Grenoble Alpes (Saint Martin d'Heres, FR)
- Centre National De La Recherche Scientifique (Paris, FR)
Inventors
Cpc classification
B01J20/3441
PERFORMING OPERATIONS; TRANSPORTING
C25B1/00
CHEMISTRY; METALLURGY
B01D53/02
PERFORMING OPERATIONS; TRANSPORTING
B01J20/06
PERFORMING OPERATIONS; TRANSPORTING
B01J20/3433
PERFORMING OPERATIONS; TRANSPORTING
B01D53/96
PERFORMING OPERATIONS; TRANSPORTING
International classification
C25B1/00
CHEMISTRY; METALLURGY
B01D53/96
PERFORMING OPERATIONS; TRANSPORTING
Abstract
A method is described to regenerate an oxygen trap, comprising at least the following steps: circulating a current in the trap material (2) to reduce this material; measuring the value I.sub.m of the current and estimating its derivative dI.sub.m/dt in relation to time; estimating the length () of material reduced by the current as a function of the value of the current and its derivative; stopping circulation of the current when the length of reduced material is at least equal to a threshold value (.sub.s).
Claims
1. A method to regenerate an oxygen trap using an electric current, comprising at least the following steps: a) circulating, by a circuit and a voltage source, an electric current in a material of the trap to reduce the material; b) measuring, by an ammeter, a value Im of said electric current and estimating a derivative dIm/dt of the measured current Im in relation to time; c) estimating, by a calculator, a length () of material reduced by said electric current, as a function of the value of said current (Im) and of said derivative (dIm/dt); d) stopping, by a switch, circulation of the current when the length of reduced material is at least equal to a threshold value (s).
2. The method according to claim 1 wherein the length of reduced material is a function of the ratio Im.sup.2/(dIm/dt) between the square of the measured current and its derivative when the derivative dIm/dt is not zero.
3. The method according to claim 1 further comprising measuring or estimating a contribution, to the measured current, made by electrochemical reductions of pollutants in the environment of the trap, wherein the length () of reduced material is estimated in step c) as a function of the value of the measured current (Im), of the estimated derivative (dIm/dt), and of the measured or estimated contribution, to the measured current, made by the electrochemical reductions of pollutants.
4. The method according to claim 1 wherein a value is also measured of the current (Ip=I(dI/dt=0)) for a zero or near-zero derivative thereof, and wherein the length of reduced material is estimated as a function of the value of said current (Im), of its derivative (dIm/dt) and of the value of the current (Ip=I(dI/dt=0)) for a zero or near-zero derivative thereof.
5. The method according to claim 4 wherein the length of material is a function of the ratio Im(ImIp)/(dIm/dt) between the product of the electric current and the electric current corrected for the current value when the current is substantially constant, and the derivative of the current when the derivative dIm/dt is not zero.
6. The method according to claim 3 wherein the circulation of current is interrupted and the value of the current (Ip=I(dI/dt=0)) is measured for a zero or near-zero derivative thereof.
7. The method according to claim 6 wherein the interruption of the current and measurement of the value of the current (Ip=(dI/dt=0)), for a zero or near-zero derivative thereof, are performed at regular time intervals.
8. The method according to claim 1 wherein regenerating the oxygen trap takes place at a temperature between 600 C. and 900 C.
9. The method according to claim 1 wherein the trap material is a solid ZrYO or ZrScO solution, or a ThO.sub.2- and LaGaO.sub.3- structure with or without double substitutions of Y.sub.2O.sub.3 or Sc.sub.2O.sub.3 by CeO.sub.2 or Al.sub.2O.sub.3, or a 8(Y.sub.2O.sub.3).10(Al.sub.2O.sub.3) mixture.
10. A method to regenerate an oxygen trap using an electric current, comprising at least the following steps: a) circulating, by a circuit and a function generator, an electric current in a material of the trap to reduce the material; b) measuring, by an oscilloscope, a value Im of said electric current and estimating its derivative dIm/dt in relation to time; c) estimating, by a calculator, a length () of material reduced by said electric current, as a function of the value of said current (Im) and of its derivative (dIm/dt); d) stopping, by a switch, circulation of the current when the length of reduced material is at least equal to a threshold value (s), wherein, owing to said oscilloscope, a measurement or estimate is calculated of the contribution, to the measured current, made by electrochemical reductions of pollutants in the environment of the trap, and the length () of reduced material is estimated in step c) as a function of the value of the measured current (Im), of the derivative (dIm/dt), and of the contribution, to the measured current made by the electrochemical reductions of pollutants.
11. The method according to claim 1 wherein the instant (maximum) value is estimated of the current when it is interrupted.
12. The method according to claim 1 wherein a contribution to the measured current by electrochemical reductions of environment pollutants is estimated via fast-scan voltammetry, square-wave potential technique or low frequency complex impedance spectroscopy.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
(1)
(2)
(3)
(4)
(5)
(6)
(7)
(8)
DETAILED DESCRIPTION OF PARTICULAR EMBODIMENTS
(9)
(10) For example, it is a sample of 8 mole % yttrium-stabilized zirconium (YSZ), stable under a reducing atmosphere.
(11) Trap performance was not proven on this solid solution. The endurance thereof was previously tested by performing about ten reduction and re-oxidation cycles. It was also shown that this is possible under a hydrogen atmosphere.
(12) As a variant it is possible, as getter material, to use any solid solution of ZrYO or ZrScO type, with or without double substitutions (of Y.sub.2O.sub.3 or Sc.sub.2O.sub.3, either by CeO.sub.2 or by AlO.sub.3) but also all structures such as ThO.sub.2 and LaGaO.sub.3.sup. similar to ZrO.sub.2.sup. bases, with or without double substitutions (of Y.sub.2O.sub.3 or Sc.sub.2O.sub.3, either by CeO.sub.2 or by Al.sub.2O.sub.3). Mention can also be made of 8(Y.sub.2O.sub.3)10 (Al.sub.2O.sub.3) mixtures.
(13) As an example, a zirconium solution can be used such as Zr.sub.1-xY.sub.xO.sub.2-x/2 or Zr.sub.1-xSc.sub.xO.sub.2-x/2 with x between 0.03 and 0.11. A double substitution solid solution such as ZrO.sub.2(0.86)Y.sub.2O.sub.3(0.1)CeO.sub.2(0.04) or ZrO.sub.2(0.9)Y.sub.2O.sub.3(0.09)CeO.sub.2(0.01) can also be used.
(14) The inventors have been able to determine that the behaviour of a getter follows dynamics which appear to be exclusively or chiefly related to the re-oxidation process of materials and not to inertia of the gas as described in the work conducted under argon in particular by J. Foultier et al., Vacuum, 25, 1975, 307.
(15) An oxygen getter operating under a hydrogen atmosphere is able to capture a large amount of pollutant (in particular during pollution peaks) within a very short time, due to the very high diffusivity of pollutants in hydrogen. CFD code numerical simulation and the study of dimensionless numbers (Pe, Sc, Sh) prove that the purge rate has little influence on trap performance, since hydrogen has very good thermal diffusivity and a very high binary diffusion coefficient.
(16) Regeneration tests were conducted by the inventors, evidencing an unusual behaviour of ceramic that has never been reported in the literature.
(17) Modeling thereof is proposed below that is easy and robust and allows an explanation of this behaviour.
(18) With this modeling it is possible to control the state of reduction by measuring the current as a function of time.
(19) In the partly oxidized getter sample (the material of which is ytrrium-stabilized zirconium as indicated above) illustrated in
(20) Let V.sub.T (en m.sup.3) be the volume of the sample and S its cross-section (in m.sup.2).
(21) As illustrated in
(22) Through previous electrochemical characterization (e.g. by high frequency complex impedance spectroscopy) it is possible to determine an effective ionic conductivity .sub.ion.sup.eff, which is dependent on the morphology (porosity) of the sample.
(23) An exchange current K.sub.0 (in A/m.sup.2) can be inferred therefrom; these values are also dependent on the morphology of the sample, in particular its active surface area, and it was also ascertained that K.sub.0 is dependent on temperature range (20 C.) and the range of applied potential (0.5V).
(24) Finally, on the basis of the type of solid solution and the porosity thereof it is possible to estimate the concentration C.sub.1 (in mol/m.sup.3) of reducible oxygen contained in the material. This concentration is given by:
(25)
(26) with i: 1 or 2
(27) It relates to the number of moles of exchangeable oxygen in the regenerative length. X.sub.1 represents the number of oxygen atoms which can be exchanged with the external gas surrounding the getter. X.sub.2 represents the oxygens involved in internal exchanges but their physicochemical nature is unknown, and C.sub.2 is their concentration.
(28) Let Ohm's law expressed from this analysis be:
(29)
where E.sub.ion is the non-measurable difference in ionic potential.
(30) The following linearized electrochemical overvoltage law is proposed for X.sub.20 and 0X.sub.1C.sub.1V.sub.T (these two inequalities are in fact always verified since they correspond to the mass balance in the ceramic):
(31)
(32) In this equality I.sub.f(t) represents the charge transfer occurring within the bar or sample during polarisation, I.sub.f,1(t) is charge transfer related to re-oxidation of the bar, I.sub.f,2(t) represents oxygen exchanges within the bar.
(33) Under strong pollution it was found that it is possible to observe a current (I.sub.p) related to electrochemical reduction of the pollutants. It is not possible to relate this current to an overvoltage law but nevertheless an expression of current density representative thereof is used:
I.sub.T=I.sub.f+I.sub.p(2b)
(34) For X.sub.2=0, the expression (2a) is reduced to:
(35)
(36) The mass and charge balance is then expressed by the evolution rule of X.sub.1 and X.sub.2; for X.sub.20:
(37)
(38) And for 0X.sub.1C.sub.1V.sub.T
(39)
with F being Faraday's constant (C/mol).
(40) The operator (or automaton) has knowledge of I.sub.m (measured current) and E (the potential applied to the terminals of the sample). These values can be stored in memory.
(41) If it is written:
I.sub.m=(I.sub.f+I.sub.p)S(4a)
(42) Assuming that the time constant of the pollution-related current is lower than the constant which corresponds to internal regeneration of the ceramic:
(43)
(44) To determine the level of re-oxidation, it is sought to know X.sub.1 (amount of oxygen available for re-oxidation).
(45) The front position is expressed by:
(V.sub.TX.sub.1/C.sub.1)/S
(46) By analysis of equations (2a) and (3a), it is shown by combining equations (2c) and (3b) that for dI.sub.m/dt0 (the case dI.sub.m/dt<0 corresponds solely to internal exchanges without reduction or regeneration) the front position of can be written:
(47)
(48) L.sub.Regenerative represents the length that it is possible to regenerate (L.sub.Regenerative can be taken to be slightly shorter than the length of the bar to take into account electrode dimensions). The second and third parts of the 2.sup.nd member (which are the terms in 1/C1S2F and E/K.sub.0) of the above expression give the reduced length.
(49) Therefore can have a value higher than L.sub.Regenerative on account of the pollution-related current I.sub.p which can be determined by a current at
(50)
and/or by measuring the maximum value of the current at the time of interruption, or by any other electrochemical method allowing determination of pollutant concentration and to infer I.sub.p therefrom. This latter term is the contribution to the signal made by exchanges related to electrochemical reduction of pollutants in the environment.
(51) By means of electrochemical measurements e.g. voltamperometry or complex electrochemical impedance, it is possible to determine
(52)
but with variable accuracy depending on operating temperature (10% at 900 C. and 20% at 800 C.). Through geometric measurement and coulometry, at the time of total regeneration, and irrespective of temperature, it is possible to determine
(53)
to within 5%.
(54) With this fine-tuned knowledge of the system under polarization, it is easy to stop regeneration when reaches a set value .sub.s: for as long as calculated using the above formula or a similar formula remains below this threshold .sub.s, regeneration is continued. It is halted when , estimated or calculated using the above formula or similar formula, becomes equal to or higher than this threshold value .sub.s.
(55) In addition pollution may evolve; to give consideration thereto it is possible, by merely interrupting the regeneration current, to measure or record I.sub.p for example at regular time intervals e.g. every 5 or 10 seconds.
(56) As indicated above, the parameters S and .sub.ion.sup.eff K.sub.0, C.sub.1 can be determined or estimated. In addition, the percentage of uncertainty established on each of the parameters allows dimensioning of reducible length.
(57) The above formula shows that the front position is dependent on I.sup.2.sub.m/(dI.sub.m/dt); if the atmosphere is not pure, this position is dependent on I.sub.m(I.sub.mI.sub.p)/(dI.sub.m/dt).
(58) dI.sub.m/dt<0 corresponds to internal exchanges within the sample which are very rapid.
(59) The case dI.sub.m/dt=0 corresponds to the case in which the sample exchanges oxygen with the outside of the sample.
(60) dI.sub.m/dt>0 corresponds to the case in which oxygen is released into the atmosphere outside the sample (this is a regeneration situation since oxygen is released from the sample).
(61) Current measurements can be performed using an ammeter 6 arranged in series with the bar or sample 2.
(62) The current values can be transmitted to data processing means 16.
(63) These means 16 comprise a computer for example or micro-computer or calculator or an electrical circuit or a programmable or programmed electronic circuit or a microprocessor programmed to store in memory and process current data e.g. data supplied by the means 6, and data to implement a method according to the invention. In this manner the value of the regeneration front can be estimated or calculated.
(64) For example, a central unit 17 is programmed to apply a processing method of the invention. In particular the values of current I for dI/dt=0 or the maximum value (I.sub.instE=0) of the current at the time of interruption or regeneration can be measured or estimated. The values of dI.sub.m/dt can be estimated by numerical derivation (so-called naive method), for example for a time interval imposed by the operator (e.g. 5 to 100 seconds). As a variant, the means 17 apply another method e.g. fast-scan voltammetry or square-wave potential technique or low frequency complex impedance spectroscopy. These methods can be accompanied by a calibration step and the correlation which relates their results to Ip can be more or less complex.
(65) In addition the values of
(66)
may be previously measured and also stored in memory in the means 17.
(67) On the basis of these data, the means 17 can estimate or calculate the value of the regeneration front.
(68) These means 17 can also allow a comparison between this value of and a threshold value, and controlling of the switch 8 used to stop circulation of the regeneration current in the sample 2.
(69) On the monitor or visualizing means 19 it is possible for example to display the changes in measured current as a function of time and/or changes in .
(70)
(71)
(72)
(73) An example of a method which can be implemented according to the invention is schematically illustrated in
(74) At a first step (S1), a certain number of initial parameters can be measured or calculated e.g. .sub.ion.sup.eff, K.sub.0, C.sub.1. It is possible to infer
(75)
therefrom.
(76) Measurements of I are then performed (step 2) in particular for I.sub.p=I(dI/dt=0) or for IpI.sub.instE=0.
(77) From these measured values it is possible to estimate or calculate value (step S3).
(78) As a function of the result of comparison between this value and a threshold value .sub.s, it can be decided to stop or continue regeneration (step S4). In the latter case measurements of I are continued (step S2).
(79) Regeneration according to the invention can be carried out automatically after a certain time of use of the getter. Regeneration can be triggered by the means 17 programmed for this purpose e.g. on the basis of a clock signal. As a variant, a potential application test is applied e.g. for a time of 5 to 10 seconds and current I.sub.m is measured; also, a current I.sub.E is estimated as a function of the applied potential and of estimated regenerated length (application of Ohm's law); if the estimated current I.sub.E is higher than the measured current I.sub.m, regeneration is triggered.
(80)
(81) The device in
(82) Here the enclosure 102 and the block 112 both have a general cylindrical shape, the block being held in position in this enclosure via bottleneck regions 114 for example formed in the enclosure.
(83) The block 112 is inserted in an electric circuit comprising a generator of direct or rectified current 115 the terminals of which are electrically connected to opposite ends of the block, for example via metal conductors, 116a, 116b simply placed in contact with the solid electrolyte. In the experimental enclosure in
(84) An oven 116 surrounds the enclosure 102, at least the part thereof in which the block 112 is positioned, this oven being able to bring the solid solution to the temperature at which it has notable ionic and electronic conductivities, for example in the order of 600 C. to 800 C., when the block is formed of the solid solution containing zirconium, yttrium and cerium oxides, in particular in the above-indicated proportions.
(85) The apparatus also comprises means, particularly comprising a connector 120 and valve 122 to emit an inert gas or hydrogen inside the enclosure and means to evacuate this gas which particularly comprise a connector 124 and valve 126, these latter inlet and evacuation means preferably being arranged such that the input gas is caused to circulate in the opposite direction to the direction normally taken in a prior step by the gas to be purified.
(86) The apparatus thus prepared operates as follows.
(87) At a first stage the solid solution of the block 112 is converted to its reduced form, in particular by passing an electric current through the block in a direction which results from the indication of the + and polarities respectively associated with the conductors 116a and 116b. This step is performed by estimating the length of regeneration according to the present invention.
(88) During this operation, the valves 106 and 110 are closed whilst valves 122 and 126 are open and allow a gas to pass through the porous block such as nitrogen or a neutral gas but also hydrogen which entrains the oxygen released by the electrochemical reduction operation.
(89) This reduction operation can be accompanied by blackening of the porous mass.
(90) On completion of this operation, the supply to the electric circuit is interrupted.
(91) The oxygen trap is then able to function in particular under the following conditions.
(92) Valves 122 and 126 are closed and valves 106 and 110 are open, the latter allowing the gas to be purified to enter the enclosure via the connector 104, to pass in contact with the porous block 112 and to be evacuated via connector 110.
(93) The traces of oxygen contained in the gas to be purified are then energetically fixed by the solid solution of the block 112.
(94) According to document FR 2230402, observation of colouring of the block allows the moment to be estimated on and after which its adsorption capacity is exhausted, since it only returns to white when it has been fully re-oxidized. However this is not achievable when the process is in progress on account of temperature; it is this problem that is solved by the present invention.
(95) By monitoring the current I.sub.m as proposed herein, it is possible to observe the level of reduction or re-oxidation as shown in
(96) Oxygen adsorption is rapid irrespective of the degree of oxidation of the solid solution, and in particular the rate of oxygen adsorption is not substantially affected by this degree of oxidation for as long as it remains lower than its value in natural solid solutions.
(97) When this maximum degree of oxidation is reached, the solid solution is regenerated by converting it to its reduced form under the conditions of the present invention indicated above.
(98) The trap just described is therefore capable of operating discontinuously.
(99)
(100) The apparatus in
(101) Advantageously, the parts 131a, 131b of the block 112a are porous and separated by a compact or solid central portion 131c, the separation between the two compartments 128, 130 being obtained via a partition 132 in which a central opening is provided allowing passage into the block 112a, in the central portion thereof, a seal for example in enamel providing imperviousness between the central portion 131c and the edges of the opening in the partition 132.
(102) The block 112a is inserted in an electric circuit comprising a current generator 115a having its positive terminal connected to end 136 and negative terminal connected to end 138 of the block 112a, in compartments 128 and 130 respectively.
(103) The entry of the gas to be purified is through the connector 104a into compartment 130, the purified gas being evacuated through connector 108a, whilst an inert gas is caused to enter compartment 128 via connector 120a and evacuated outside compartment 128 via connector 122a.
(104) The traces of oxygen contained in the gas entering compartment 130 are therefore retained in the corresponding part of block 112a, in the form of ions which migrate in the bulk of the porous block in particular in the general direction indicated by arrow 140 when the generator is powered, these oxygen ions being converted to gaseous oxygen atoms in the vicinity of end 136 of the block 112a in contact with the conductor 116a to which the electrons are transferred.
(105) A neutral or reducing gas such as purge hydrogen, caused to enter compartment 128 via connector 120a, entrains the gaseous oxygen or formed vapour towards the evacuation connector 122a.
(106) The invention therefore particularly allows the applying of continuous mode purification.
(107) It also, at any time, provides an indication of the re-oxidation level and hence allows best control over the system whether functioning in discontinuous or continuous mode.
(108) The invention has been described with a solid cylindrical bar 2, but other shapes of samples can be used.
(109) More generally, the material of the trap 2 is of elongate shape e.g. cylindrical or parallelepiped.
(110) As a variant, it may be in the form of a pellet (
(111) Irrespective of shape, the sample may be composed of a material which may be porous or dense.
(112) The gas to be purified with the getter may be hydrogen or any other neutral gas e.g. of the type used in the field of microelectronics such as argon, helium or nitrogen.
(113) Examples of application of the invention are the following: purification of pollutants such as CO.sub.2, H.sub.2O, CO and NO in a neutral carrier gas or hydrogen; purification of He or H.sub.2 for analysis by gas phase chromatography (GPC); purification of H.sub.2 for on-hydride hydrogen storage; purification of H.sub.2 for use in fuel cells; purification of H.sub.2 for microelectronic processes; purification of neutral gases such as argon or nitrogen for any industrial use.