WO2014099591A1 - Apparatus and method of an improved flare in an andrussow process - Google Patents

Apparatus and method of an improved flare in an andrussow process Download PDF

Info

Publication number
WO2014099591A1
WO2014099591A1 PCT/US2013/074609 US2013074609W WO2014099591A1 WO 2014099591 A1 WO2014099591 A1 WO 2014099591A1 US 2013074609 W US2013074609 W US 2013074609W WO 2014099591 A1 WO2014099591 A1 WO 2014099591A1
Authority
WO
WIPO (PCT)
Prior art keywords
hydrogen
flare
stream
combustible gas
oxygen
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Ceased
Application number
PCT/US2013/074609
Other languages
French (fr)
Inventor
Stewart Forsyth
Aiguo Liu
Martin J. Renner
Brent J. STAHLMAN
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Invista Technologies SARL Switzerland
Invista Technologies SARL USA
Original Assignee
Invista Technologies SARL Switzerland
Invista Technologies SARL USA
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Invista Technologies SARL Switzerland, Invista Technologies SARL USA filed Critical Invista Technologies SARL Switzerland
Publication of WO2014099591A1 publication Critical patent/WO2014099591A1/en
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01CAMMONIA; CYANOGEN; COMPOUNDS THEREOF
    • C01C3/00Cyanogen; Compounds thereof
    • C01C3/02Preparation, separation or purification of hydrogen cyanide
    • C01C3/0208Preparation in gaseous phase
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01CAMMONIA; CYANOGEN; COMPOUNDS THEREOF
    • C01C3/00Cyanogen; Compounds thereof
    • C01C3/02Preparation, separation or purification of hydrogen cyanide
    • C01C3/0208Preparation in gaseous phase
    • C01C3/0212Preparation in gaseous phase from hydrocarbons and ammonia in the presence of oxygen, e.g. the Andrussow-process
    • C01C3/022Apparatus therefor
    • C01C3/0225Apparatus therefor characterised by the synthesis reactor
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/061Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating
    • F23G7/065Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating using gaseous or liquid fuel
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/08Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases using flares, e.g. in stacks
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines

Definitions

  • the present disclosure is directed to a reactor scheme for the Andrussow process for the production of hydrogen cyanide (HCN) from methane, ammonia, and oxygen.
  • HCN hydrogen cyanide
  • the Andrussow process can be used for gas phase production of hydrogen cyanide (HCN) from methane, ammonia, and oxygen over a platinum catalyst.
  • HCN hydrogen cyanide
  • Filtered ammonia, natural gas, and air are fed into a reactor and heated to about 800 °C to about 2,500 °C in the presence of a catalyst that includes at least platinum.
  • the methane can be supplied from natural gas, which can be further purified.
  • Hydrocarbons having at least two carbons can be present in natural gas.
  • Air can be used as a source of oxygen.
  • the reactor off-gas containing HCN and un-reacted ammonia can be quenched in a waste heat boiler to approximately 100 °C to 400 °C.
  • the quenched reactor off-gas, containing HCN can be sent through an ammonia absorption process to remove un-reacted ammonia, such as by contacting the reactor off-gas with ammonium phosphate solution, phosphoric acid, or sulfuric acid to remove the ammonia.
  • the product off-gas can be sent through an HCN absorber, where cold water can be added to entrain the HCN.
  • the HCN absorber can produce a gaseous waste stream that contains substantially hydrogen and by products. Due to the composition of the gaseous waste stream disposal can be an environmental concern, can be inefficient to flare off, or combinations thereof.
  • the present disclosure is directed to a solution to disposal of a gaseous waste stream from an HCN absorber in an Andrussow process.
  • the solution can include a system and method for producing hydrogen cyanide via the Andrussow process.
  • the system can include a reactor zone wherein oxygen, ammonia, and methane are allowed to react in the presence of a catalyst comprising platinum to provide at least hydrogen cyanide (HCN), hydrogen, and waste product.
  • HCN recovery zone can substantially remove the hydrogen cyanide from the hydrogen and the waste product.
  • a flare zone can burn a combustible gas mixture in hydrogen mode to produce at least carbon dioxide and water, the combustible gas mixture comprising at least a portion of the hydrogen and at least a portion of the gaseous waste product.
  • the combustible gas mixture can include natural gas.
  • a hydrocarbon mixture can provide the methane in the system.
  • the hydrocarbon mixture can comprise natural gas, biogas, substantially pure methane, or mixtures thereof.
  • the system can include a hydrogen recovery system, which can recycle, store, or utilize the recovered hydrogen downstream or upstream of the hydrogen recovery system.
  • the system can include an ammonia extraction zone wherein the ammonia is substantially removed from the HCN, hydrogen, and waste product.
  • a hydrogen cyanide recovery zone can provide a hydrogen cyanide product stream that can include a purity of at least about 98.5% hydrogen cyanide or provide the gaseous waste product stream such that less than about 1.5% HCN is present.
  • the combustible gaseous waste mixture, fed to the flare can comprise at least about 8 vol% hydrogen.
  • the flare exit velocity can be less than about 37.2 meters per second, such as less than about V max , wherein V max is defined by:
  • Vmax ( H2 - Ki)*K 2 , wherein
  • Ki constant, 6.0 volume% hydrogen
  • XH 2 volume % hydrogen, on a wet basis, as calculated by using the American Society for Testing and Materials (ASTM) Method D 1946-77.
  • the flare zone can be configured to operate at temperatures of greater than about
  • the flare can be unassisted or stabilized.
  • the flare zone can comprise at least a 3.0 inch diameter flare tip.
  • the flare zone further can be configured to flare a non-hydrogen combustible gas mixture burned in a non-hydrogen mode, such as a non-hydrogen combustible gas mixture of a heat content of at least about 200 BTU/scf.
  • the system can include at least one liquid separator, upstream of the flare, to remove at least a portion of liquid present in the combustible gas mixture or non-hydrogen combustible gas mixture.
  • a method for burning a waste product produced by an Andrussow process can include allowing oxygen, ammonia, and methane to react in the presence of a catalyst comprising platinum to give a product stream comprising at least hydrogen cyanide, hydrogen, and a waste product.
  • Hydrogen cyanide can be extracted from the product stream to produce an HCN product stream and a gaseous waste stream comprising at least a portion of the hydrogen and the waste product and the gaseous waste stream can be feed to a hydrogen mode flare.
  • the method can include extracting ammonia from the product stream, such as prior to extracting hydrogen cyanide. At least a portion of liquid can be separated from the gaseous waste stream prior to feeding the gaseous waste stream to the hydrogen mode flare. Hydrogen can be recovered from the gaseous waste stream. Such a gaseous waste stream with reduced hydrogen content can still be efficiently flared using the methods and apparatus described herein.
  • the method can include supplementing the flared components with hydrogen or hydrocarbons, such as methane.
  • the method can include flaring the extracted stream at a flare exit velocity of less than about 37.2 meters per second, such as V max .
  • the flare zone can operate at a temperature of greater than about 1650 °C.
  • the method can include assisting or stabilizing the flare.
  • FIG. 1 is a schematic block flow diagram of an HCN production via the
  • catalysts can be chosen from oxidation catalysts that are infusible (solid) at the working temperature of around 1000°C; he included platinum, iridium, rhodium, palladium, osmium, gold or silver as catalytically active metals either in pure form or as alloys.
  • certain base metals such as rare earth metals, thorium, uranium, and others, could also be used, such as in the form of infusible oxides or phosphates, and that catalysts could either be formed into nets (screens), or deposited on thermally-resistant solid supports such as silica or alumina.
  • platinum-containing catalysts have been selected due to their efficacy and to the heat resistance of the metal even in gauze or net form.
  • a platinum-rhodium alloy can be used as the catalyst, which can be in the form of a metal gauze or screen such as a woven or knitted gauze sheet, or can be disposed on a support structure.
  • the woven or knitted gauze sheet can form a mesh-like structure having a size from 20-80 mesh, e.g., having openings with a size from about 0.18 mm to about 0.85 mm.
  • a catalyst can comprise from about 85 wt% to about 95 wt% Pt and from about 5 wt% to about 15 wt% Rh, such as 85/5 Pt/Rh, 90/10, or 95/5 Pt/Rh.
  • a platinum-rhodium catalyst can also comprise small amounts of metal impurities, such as iron (Fe), palladium (Pd), iridium (Ir), ruthenium (Ru), and other metals. The impurity metals can be present in trace amounts, such as about 10 ppm or less.
  • a catalyst comprising a plurality of fine- mesh gauzes of Pt with 10% rhodium disposed in series is used at temperatures of about 800 to 2,500° C, 1,000 to 1,500° C, or about 980 to 1050° C.
  • the catalyst can be a commercially-available catalyst, such as a Pt-Rh catalyst gauze available from Johnson Matthey Pic, London, UK, or a Pt-Rh catalyst gauze available from Heraeus Precious Metals GmbH & Co., Hanau, Germany.
  • the composition of a gaseous waste stream from and Andrussow process can make disposal of the stream difficult.
  • the gaseous waste stream can be such that flaring is inefficient, harmful to the environment, outside the parameters of local or federal regulations, or combinations thereof.
  • the present disclosure is directed to an apparatus and method for the synthesis of HCN via an Andrussow process, in which an improved flare can dispose of the gaseous waste stream taking into consideration environmental concerns, efficiency concerns, or governmental regulations.
  • FIG. 1 is a schematic block flow diagram of an example process 10 for the production of hydrogen cyanide (HCN) via the Andrussow process, according to the present disclosure.
  • a HCN reaction zone 12 is supplied with an ammonia (NH 3 ) stream 2, a methane (CH 4 ) stream 4, and an air stream 6 (which includes oxygen gas (0 2 )).
  • Air can include air and other oxygen-containing gas mixtures, including oxygen-enriched air having oxygen concentrations above about 21 vol%. Examples herein can be particularly useful when an Andrussow process is adapted to employ a gaseous oxygen feed stream 6 that contains somewhat higher levels of oxygen than air.
  • such a gaseous oxygen feed stream 6 can contain at least about 25 vol% oxygen, at least about 30 vol% oxygen, at least about 40 vol% oxygen, at least about 50 vol% oxygen, at least about 60 vol% oxygen, at least about 70 vol% oxygen, at least about 80 vol% oxygen, at least about 90 vol% oxygen, at least about 95 vol% oxygen, at least about 98 vol% oxygen.
  • the process 10 can include an air Andrussow process, e.g., an air stream 6 that includes about 21 vol% oxygen, an air-enriched Andrussow process, e.g., an air stream 6 that includes greater than about 21 vol% oxygen but less than about 100 vol% oxygen, or an oxygen Andrussow process, e.g., an air stream 6 that includes about 100% oxygen.
  • the one or more reactors can include a HCN catalyst, such as platinum (Pt) or a platinum alloy, such as an alloy of platinum with rhodium (Rd) or palladium (Pd) containing at least about 85% platinum by weight.
  • Alloys used in the Andrussow process can include, but are not limited to, 10 wt% Rh - 90 wt% Pt, 8 wt% Rh - 92 wt% Pt, 5 wt% Pd - 5 wt% Rh - 90 wt% Pt, or 5 wt% Rh - 95 wt% Pt. Alloys containing up to about 5 wt% iridium (Ir) can be used.
  • the HCN catalyst can be designed to reduce by products, such as nitrous-oxide by products, and therefore can have an increase rhodium (Rh) content, or other materials, such as cobalt (Co).
  • the HCN catalyst can be contained in a packed bed, such as in a packed bed reactor, or be formed as a gauze, such as by weaving or knitting metal filaments into gauze-like structures. Such formed catalysts are well established in the art and can contain the catalytic materials described herein.
  • the HCN catalyst can be a commercially-available catalyst, such as a Pt-Rh catalyst gauze available from Johnson Matthey Pic, London, UK, or a Pt-Rh catalyst gauze available from Heraeus Precious Metals GmbH & Co., Hanau, GERMANY.
  • the resulting product stream 14 from the HCN reaction zone 12 can be fed into an ammonia recovery system 16 that is configured to recover unreacted N3 ⁇ 4.
  • Ammonia can be recovered by NH 3 absorption via providing one or more of phosphoric acid (H 3 P0 4 ), sulfuric acid (H 2 S0 4 ), or an ammonium phosphate solution to the product stream 14 that can absorb NH 3 from the product stream 14.
  • a phosphoric acid stream 18 within the ammonia recovery system 16 can absorb NH 3 .
  • Ammonia can be removed from the H 3 P0 4 /NH 3 solution using one or more strippers to separate the NH 3 from the H 3 P0 4 .
  • the NH 3 can be recycled back to the HCN reaction zone 12 via an NH 3 recycle stream 20.
  • the H 3 P0 4 and other waste can be purged as a wastewater stream 22, while an NH 3 -stripped HCN stream 24 can be fed to an HCN recovery system 26.
  • the HCN recovery system 26 can include one or more unit operations configured to separate and purify HCN from the HCN stream 24. As a result of the HCN recovery system 26, a purified HCN product stream 28 is produced.
  • the HCN recovery system 26 can also produce a waste gas 30 or a wastewater stream 32. Wastewater streams 22, 32 can be fed to waste water treatment 36 for further processing, such as recovery of ammonia or hydrogen cyanide.
  • the final wastewater stream 40 from the waste water treatment 36 can be further processed, stored, or disposed.
  • HCN recovery system 26 can include a gaseous waste stream 30.
  • Gaseous waste stream 30 can include hydrogen, carbon monoxide, nitrogen, carbon dioxide, hydrogen cyanide, or mixtures thereof.
  • gaseous waste stream 30 can include additional waste streams not illustrated.
  • a waste stream from reactor 12 or other operation can be combined with stream 30.
  • the composition of gas waste stream 30 can vary according to a number of factors, including composition of the feed streams 2, 4, 6, efficiency of the HCN reaction zone 12, efficiency of the ammonia recovery system 16, efficiency of the HCN recovery system 26, operating conditions, or combinations thereof.
  • gaseous waste stream 30 can feed a hydrogen recovery system 42.
  • the gaseous waste stream 30 can contain residual amounts of HCN, as well as significant hydrogen gas or a variety of gases including unreacted methane, carbon dioxide, carbon monoxide, water, nitrogen, and a variety of organonitriles.
  • Removal of HCN can be substantially complete, not only so that valuable HCN is not lost to the waste stream, but also for health and environmental concerns, and because significant amounts of HCN can complicate processing of the waste stream.
  • some pressure swing apparatus absorbents that can be used for hydrogen recovery can have operational limits of less than about 2.0% HCN, or less than about 1.5% HCN.
  • the gaseous waste stream can have less than about 2.0% HCN, or less than about 1.5% HCN, or less than about 1% HCN, or less than about 0.5% HCN, or less than about 0.2% HCN, or less than about 0.1% HCN.
  • the HCN content of the gaseous waste stream 30 can vary, for example, between about 0.5% to about 1.0%.
  • gaseous waste stream 30 can include 40-75 vol% H 2 , 15-35 vol% CO, 5-15 vol% N 2 , 1- 2 vol% C0 2 , 1-2 vol% CH 4 , or 0-1 vol% HCN.
  • the recovered hydrogen stream 50 can be stored for future processing or sale, sent to additional hydrogen processing units, recycled to a point upstream or downstream, used to supplement a flare 48 (as discussed further below), or combinations thereof.
  • Hydrogen recovery system 42 can regulate a level of hydrogen that is recovered from combined gaseous waste stream 20. For example, if combined gaseous stream 30 is hydrogen rich, such as greater than about 40 vol%, hydrogen recovery system 42 can recover a larger percentage of hydrogen. While the recovered hydrogen stream 50 need not be 100% pure, removal of at least the majority of the carbon dioxide, carbon monoxide, or nitriles from hydrogen can be desirable to avoid side products and contaminants when the recovered hydrogen is used, for example, for hydrogenation reactions.
  • the recovered hydrogen gas can be at least about 90% pure, or at least about 91 % pure, or at least about 92% pure, or at least about 93 % pure, or at least about 94% pure, or at least about 95 % pure, or at least about 96% pure, or at least about 97 % pure, or at least about 98% pure, or at least about 99% pure hydrogen.
  • hydrogen recovery system 42 can be optimized to provide a processed gaseous waste stream 52 to a processing unit downstream.
  • the hydrogen recovery system 42 can produce a processed gaseous waste stream including at least about 8 vol% hydrogen.
  • Gaseous waste stream 52 can include less than about 1.5% HCN.
  • a valve can be located downstream of hydrogen recovery system 42 but upstream of processed gaseous waste stream 52, such that gaseous waste stream 30 feeds directly and only to the hydrogen recovery system 42.
  • system 10 can include the flare 48 to burn off gaseous waste stream 30.
  • Flare 48 can be designed to thoroughly destroy gaseous waste. If the gaseous waste is dilute, stream 30 can be enriched with hydrocarbon fuel 56, such as natural gas, to increase a heating value of the resulting blend in order to ensure that the waste is thoroughly destroyed.
  • Hydrogen has a lower net heating value than many hydrocarbon fuels. For example, the net heating value of methane is about 913 BTU/scf. On the other hand, the net heating value of hydrogen is only about 275 BTU/scf.
  • a detector that can quantify components in the combustible gas mixture.
  • a valve can be operably linked to the detector, where the valve is configured to permit supplementing the combustible gas mixture 30 with a hydrogen-containing enrichment fuel, such as hydrogen or methane, when a set value of non-combustible components, corresponding to a lower threshold of heat content, are detected in the combustible gas mixture.
  • a hydrogen-containing enrichment fuel such as hydrogen or methane
  • the amount of hydrogen-containing enrichment fuel needed to thoroughly destroy the dilute gaseous waste material upon combustion also depends, in part, on the heating value of the dilute gaseous waste material flared.
  • the enrichment stream can contain a sufficient amount of hydrogen or hydrocarbons such that, when blended with the gaseous waste stream 30, the resulting blend can a sufficient heating value to thoroughly destroy the dilute gaseous waste material upon combustion in the flare 48.
  • a valve can be operably linked to the detector, where the valve is configured to permit supplementing the oxygen permitted to react when a hydrogen
  • the oxygen can be provided by air stream 6 or an oxygen supplement stream upstream of or connected to the HCN reactor 12.
  • inert gases are utilized to provide a heat transfer benefit during the reaction.
  • the presence of nitrogen in the reactor can aid in decreasing temperature spikes.
  • the present inventors have invented an HCN process capable of handling greater oxygen concentrations in a feed stream by using a flare, such as flare 48, to increase temperature control of the system. Further, greater oxygen concentrations in the feed stream can provide the benefit of reducing an amount of fuel, such as methane 4 required for the HCN reactor 12.
  • flare 48 can be designed to meet local environment or federal environmental velocity requirements of the flare.
  • a flare exit velocity can be less than about 37.2 meters per second. Flare exit velocity is the velocity of the flare at the tip of the flare device 48.
  • the flare velocity can be designed to be less than a V max , where V max is defined by
  • V max (XH2 - K *K 2 , wherein
  • V max maximum permitted flare exit velocity, meters per second
  • Ki constant, 6.0 volume% hydrogen
  • Xm volume % hydrogen, on a wet basis, as calculated by using the American Society for Testing and Materials (ASTM) Method D 1946-77.
  • the flare 48 can be designed to burn the combustible gaseous mixture at temperatures of greater than about 1000 °C, greater than about 1200 °C, of greater than about 1350 °C, of greater than about 1500 °C, of greater than about 1600 °C, or greater than about 1800 °C.
  • the flare burn temperature can include a temperature greater than a combustion temperature of one or more component of the combustible gaseous mixture.
  • the combustible gaseous mixture can include supplemental hydrocarbons, such as natural gas, or hydrogen, to increase the combustibility of the combustible gaseous mixture.
  • the flare 48 can include any flare suitable for destruction of the combustible gaseous mixture.
  • the flare 48 can include an unassisted flare or an assisted flare, or stabilized or non-stabilized flare.
  • An assisted flare includes an additional stream, such as steam assisted or air assisted, to provide for an increased flare exit velocity, increased combustible composition, more consistent combustible composition, or combinations thereof.
  • a stabilized flare can include an additional stream, such as hydrocarbon stabilized or air stabilized, to increase flare consistency, such as exit velocity, or temperature.
  • a flare nozzle of the flare 48 can be in compliance of any designed regulations, such as a flare tip or nozzle dimension.
  • the flare zone can include an at least a 3.0 inch diameter flare tip.
  • the flare zone further can be configured to operate with a non- hydrogen combustible gas mixture burned in a non-hydrogen mode.
  • the non-hydrogen combustible gas mixture can include a heat value of at least about 200 BTU/scf.
  • the flare 48 can switch between a hydrogen mode, such as burning a minimum percentage of hydrogen, or a non-hydrogen mode, such as zero vol% hydrogen, or combinations thereof. The flare 48 can provide the benefit of increased operational flexibility.
  • the system 10 can include a scrubber downstream or upstream of the hydrogen recovery system 42 to remove at least a portion of liquid, such as water, present in gaseous waste stream 30.
  • Removing liquid provided to the flare 48 can provide a steady flare, a more predictable heat capacity of the feed provided to the flare 48.
  • Combustible gaseous waste 30 can be fed to additional processes 54 of system 10, such as a boiler that can be utilized downstream to recycle heat energy.
  • a method for the production of hydrogen cyanide can include allowing oxygen, ammonia, and methane to react in the presence of the catalyst comprising platinum to give a product stream comprising at least hydrogen cyanide, hydrogen, and the waste product.
  • the method can further include extracting the hydrogen cyanide from the product stream to produce the HCN product stream (FIG. 1, element 28) and the gaseous waste stream (FIG. 1, element 30) comprising at least a portion of the hydrogen and the waste product and feeding the gaseous waste stream to a hydrogen mode flare (FIG. 1, element 48).
  • the gaseous waste stream can include more than one gaseous waste stream combined with the gaseous waste stream, such that at least a portion of the waste from the system is flared, for example in flare 48.
  • the method can include separating at least a portion of liquid in the gaseous waste stream, such as by a vapor-liquid separator, flash drum, knock-out drum, knockout pot, compressor suction drum, compressor inlet drum, demister, or combinations thereof.
  • the method includes extracting ammonia from the product stream, such as by an ammonia scrubber.
  • the method can also include recovering hydrogen from the gaseous waste stream or combined gaseous waste stream.
  • the hydrogen composition of the gaseous waste stream may be in excess of hydrogen mode flaring levels. In such instances, the excess hydrogen can be recovered and utilized elsewhere in a plant, stored for future use or sale, or combinations thereof.
  • the method can include regulating the flare, such that the flare exit velocity is less than about 37.2 meters per second. Regulating flare exit velocity can provide the benefit of a stable flare, increasing the destruction of the elements or compounds burned. Further, the method can include flaring the gaseous waste stream at a temperature of greater than about 1650 ° C.
  • Example 1 Comparison Air, Air Enriched, and Oxygen Andrussow Process Waste Gas Compositions
  • This Example illustrates that an Andrussow process that uses an enriched source of oxygen generally produces a waste stream with higher hydrogen content than one that employs air as an oxygen source.
  • the method can include regulating the flare, such that the flare exit velocity is less than about 37.2 meters per second. Regulating flare exit velocity can provide the benefit of a stable flare, increasing the destruction of the elements or compounds burned. Further, the method can include flaring the gaseous waste stream at a temperature of greater than about 1650 ° C.
  • a 4 inch internal diameter stainless steel reactor with ceramic insulation lining inside is used for pilot scale test. Forty sheets of 90 wt% Pt/10 wt% Rh 40 mesh gauze from Johnson Matthey (USA) are loaded as catalyst bed. Perforated alumina tile is used for catalyst sheet support. The total flow rate is set at 2532 SCFH (standard cubic foot per hour). Hydrogen cyanide is produced via multiple Andrussow processes. One process, the air Andrussow process, employs an oxygen-containing gas (air) that includes 21 vol% oxygen. A second process, the air- enriched Andrussow process, employs an oxygen-containing gas having greater than about 21 vol% oxygen and less than about 100 vol% oxygen. A third process, the oxygen Andrussow process, employs an oxygen-containing gas that is about 100 vol% oxygen.
  • Ammonia is separately removed from each of the product streams in a process involving absorption into an ammonium phosphate stream.
  • Hydrogen cyanide is then removed from the ammonia-depleted product stream in a process involving acidified water, thereby separately generating a hydrogen cyanide product and a gaseous waste stream for each of the processes.
  • an Andrussow process that employs an enriched oxygen stream as a source of the oxygen reactant generates significantly more hydrogen than an Andrussow process that employs air as a source of the oxygen reactant.
  • Example 2 Comparison BTU values for Air, Air Enriched and Oxygen Andrussow Process Waste Gas Compositions
  • This Example illustrates that an Andrussow process that uses an enriched source of oxygen generally produces a waste stream with higher heating value than one that employs air as an oxygen source.
  • Example 2 Three processes, as outlined in Example 1 , are used to produce HCN.
  • the heating value of the gaseous waste streams from the air, air enriched, and oxygen processes are shown below in Table 2.
  • an Andrussow process that employs an enriched oxygen stream as a source of the oxygen reactant generates a waste stream with a significantly lower heating value than an Andrussow process that employs air as a source of the oxygen reactant.
  • Method examples described herein can be machine or computer-implemented, at least in part. Some examples can include a computer-readable medium or machine-readable medium encoded with instructions operable to configure an electronic device to perform methods or method steps as described in the above examples.
  • An implementation of such methods or method steps can include code, such as microcode, assembly language code, a higher-level language code, or the like. Such code can include computer readable instructions for performing various methods. The code may form portions of computer program products. Further, in an example, the code can be tangibly stored on one or more volatile, non-transitory, or non- volatile tangible computer-readable media, such as during execution or at other times.
  • Examples of these tangible computer-readable media can include, but are not limited to, hard disks, removable magnetic disks, removable optical disks (e.g., compact disks and digital video disks), magnetic cassettes, memory cards or sticks, random access memories (RAMs), read only memories (ROMs), and the like.
  • a reactor zone wherein oxygen, ammonia, and methane are allowed to react in the presence of a catalyst comprising platinum or platinum alloy to provide a product stream comprising at least hydrogen cyanide (HCN), hydrogen, and waste product;
  • HCN hydrogen cyanide
  • an HCN recovery zone wherein the hydrogen cyanide is substantially removed from the product stream to generate a hydrogen cyanide product and a combustible gas mixture comprising the hydrogen and the waste product;
  • a flare zone wherein at least the combustible gas mixture is burned in a hydrogen mode to produce at least carbon dioxide and water.
  • hydrocarbon mixture comprises natural gas, biogas, substantially pure methane, or mixtures thereof.
  • V m a x (XH2 - K *K 2 , wherein
  • V m a maximum permitted flare exit velocity, meters per second
  • K ⁇ constant, 6.0 volume% hydrogen
  • K 2 constant, 3.9 meters per second per volume % hydrogen
  • XH2 volume % hydrogen, on a wet basis, as calculated by using the American Society for Testing and Materials (ASTM) Method D 1946-77.
  • valve operably linked to the detector, where the valve is configured to permit supplementing the combustible gas mixture with hydrogen or methane when a set value of non-combustible components, corresponding to a lower threshold of heat content, are detected in the combustible gas mixture.
  • a method for burning a waste product produced by an Andrussow process comprising:
  • Vmax (X H 2 - i)*K 2 , wherein
  • Vmax maximum permitted flare exit velocity, meters per second
  • XH2 volume % hydrogen, on a wet basis, as calculated by using the

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • General Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Inorganic Chemistry (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Catalysts (AREA)

Abstract

Systems and methods for producing hydrogen cyanide via an Andrussow process are described. The system can include a reactor zone wherein oxygen, ammonia, and methane are allowed to react in the presence of a catalyst comprising platinum to provide at least hydrogen cyanide (HCN), hydrogen, and waste product. An HCN recovery zone can substantially remove the hydrogen cyanide from the hydrogen and the waste product. A flare zone can burn at least a combustible gas mixture in a hydrogen mode to produce at least carbon dioxide and water, the combustible gas mixture comprising at least a portion of the hydrogen and at least a portion of the waste product.

Description

APPARATUS AND METHOD OF AN IMPROVED FLARE IN AN ANDRUSSOW
PROCESS
CROSS-REFERENCE TO RELATED APPLICATION
[0001] This application claims the benefit of priority to U.S. Provisional Patent
Application Serial No. 61/738,817 entitled "APPARATUS AND METHOD OF AN
IMPROVED FLARE IN AN ANDRUSSOW PROCESS," filed December 18, 2012, the disclosure of which is incorporated herein in its entirety by reference.
TECHNICAL FIELD
[0002] The present disclosure is directed to a reactor scheme for the Andrussow process for the production of hydrogen cyanide (HCN) from methane, ammonia, and oxygen.
BACKGROUND
[0003] The Andrussow process can be used for gas phase production of hydrogen cyanide (HCN) from methane, ammonia, and oxygen over a platinum catalyst. Filtered ammonia, natural gas, and air are fed into a reactor and heated to about 800 °C to about 2,500 °C in the presence of a catalyst that includes at least platinum. The methane can be supplied from natural gas, which can be further purified. Hydrocarbons having at least two carbons can be present in natural gas. Air can be used as a source of oxygen. The reactor off-gas containing HCN and un-reacted ammonia can be quenched in a waste heat boiler to approximately 100 °C to 400 °C. The quenched reactor off-gas, containing HCN, can be sent through an ammonia absorption process to remove un-reacted ammonia, such as by contacting the reactor off-gas with ammonium phosphate solution, phosphoric acid, or sulfuric acid to remove the ammonia. From the ammonia absorber, the product off-gas can be sent through an HCN absorber, where cold water can be added to entrain the HCN. The HCN absorber can produce a gaseous waste stream that contains substantially hydrogen and by products. Due to the composition of the gaseous waste stream disposal can be an environmental concern, can be inefficient to flare off, or combinations thereof.
[0004] Various aspects of HCN production are described in the following articles: Eric L.
Crump, U.S. Environmental Protection Agency, Office of Air Quality Planning and Standards, Economic Impact Analysis For the Proposed Cyanide Manufacturing NESHAP (May 2000), available online at http://nepis. epa.gov/Exe/ZyPDF. cgi?Dockey=P 100AHG1.PDF, is directed toward the manufacture, end uses, and economic impacts of HCN; N.V. Trusov, Effect of Sulfur Compounds and Higher Homologues of Methane on Hydrogen Cyanide Production by the Andrussow Method, Rus. J. of Applied Chemistry, Vol. 74, No. 10, pp. 1693-97 (2001), is directed toward the effects of unavoidable components of natural gas, such as sulfur and higher homologues of methane, on the production of HCN by the Andrussow process; Clean
Development Mechanism (CDM) Executive Board, United Nations Framework Convention on Climate Change (UNFCCC), Clean Development Mechanism Project Design Document Form (CDMPDD), Ver. 3, (Jul. 28, 2006), available online at
http://cdm.unfccc.int/Reference/PDDs_Forms/PDDs/PDD Jorm04 v03 2.pdf is directed toward the production of HCN by the Andrussow process; and Gary R. Maxwell et al., Assuring process safety in the transfer of hydrogen cyanide manufacturing technology, J. of Hazardous Materials, Vol. 142, pp. 677-84 (2007), is directed toward the safe production of HCN.
SUMMARY
[0005] The present disclosure is directed to a solution to disposal of a gaseous waste stream from an HCN absorber in an Andrussow process. The solution can include a system and method for producing hydrogen cyanide via the Andrussow process. The system can include a reactor zone wherein oxygen, ammonia, and methane are allowed to react in the presence of a catalyst comprising platinum to provide at least hydrogen cyanide (HCN), hydrogen, and waste product. An HCN recovery zone can substantially remove the hydrogen cyanide from the hydrogen and the waste product. A flare zone can burn a combustible gas mixture in hydrogen mode to produce at least carbon dioxide and water, the combustible gas mixture comprising at least a portion of the hydrogen and at least a portion of the gaseous waste product. The combustible gas mixture can include natural gas.
[0006] A hydrocarbon mixture can provide the methane in the system. The hydrocarbon mixture can comprise natural gas, biogas, substantially pure methane, or mixtures thereof. The system can include a hydrogen recovery system, which can recycle, store, or utilize the recovered hydrogen downstream or upstream of the hydrogen recovery system. The system can include an ammonia extraction zone wherein the ammonia is substantially removed from the HCN, hydrogen, and waste product.
[0007] A hydrogen cyanide recovery zone can provide a hydrogen cyanide product stream that can include a purity of at least about 98.5% hydrogen cyanide or provide the gaseous waste product stream such that less than about 1.5% HCN is present. The combustible gaseous waste mixture, fed to the flare, can comprise at least about 8 vol% hydrogen. The flare exit velocity can be less than about 37.2 meters per second, such as less than about Vmax, wherein Vmax is defined by:
Vmax = ( H2 - Ki)*K2, wherein
ma = maximum permitted flare exit velocity, meters per second
Ki = constant, 6.0 volume% hydrogen
K2 = constant, 3.9 meters per second per volume % hydrogen
XH2 = volume % hydrogen, on a wet basis, as calculated by using the American Society for Testing and Materials (ASTM) Method D 1946-77.
[0008] The flare zone can be configured to operate at temperatures of greater than about
1350 °C. The flare can be unassisted or stabilized. The flare zone can comprise at least a 3.0 inch diameter flare tip.
[0009] The flare zone further can be configured to flare a non-hydrogen combustible gas mixture burned in a non-hydrogen mode, such as a non-hydrogen combustible gas mixture of a heat content of at least about 200 BTU/scf. The system can include at least one liquid separator, upstream of the flare, to remove at least a portion of liquid present in the combustible gas mixture or non-hydrogen combustible gas mixture.
[0010] According to the present disclosure, a method for burning a waste product produced by an Andrussow process can include allowing oxygen, ammonia, and methane to react in the presence of a catalyst comprising platinum to give a product stream comprising at least hydrogen cyanide, hydrogen, and a waste product. Hydrogen cyanide can be extracted from the product stream to produce an HCN product stream and a gaseous waste stream comprising at least a portion of the hydrogen and the waste product and the gaseous waste stream can be feed to a hydrogen mode flare.
[0011] The method can include extracting ammonia from the product stream, such as prior to extracting hydrogen cyanide. At least a portion of liquid can be separated from the gaseous waste stream prior to feeding the gaseous waste stream to the hydrogen mode flare. Hydrogen can be recovered from the gaseous waste stream. Such a gaseous waste stream with reduced hydrogen content can still be efficiently flared using the methods and apparatus described herein. The method can include supplementing the flared components with hydrogen or hydrocarbons, such as methane.
[0012] The method can include flaring the extracted stream at a flare exit velocity of less than about 37.2 meters per second, such as Vmax. The flare zone can operate at a temperature of greater than about 1650 °C. The method can include assisting or stabilizing the flare.
[0013] These and other examples and features of the present systems and methods will be set forth in part in the following Detailed Description. This Summary is intended to provide an overview of the present subject matter, and is not intended to provide an exclusive or exhaustive explanation. The Detailed Description below is included to provide further information about the present systems and methods.
BRIEF DESCRIPTION OF THE FIGURES
[0014] FIG. 1 is a schematic block flow diagram of an HCN production via the
Andrussow process according to the present disclosure.
DETAILED DESCRIPTION
[0015] The synthesis of hydrogen cyanide by the Andrussow method (see, for example,
Ullmann's Encyclopedia of Industrial Chemistry, Volume 8, VCH Verlagsgesellschaft,
Weinheim, 1987, pp. 161-162) can be carried out in the vapor phase over a catalyst that comprises platinum or platinum alloys, or other metals. Catalysts suitable for carrying out the Andrussow process were discovered and described in the original Andrussow patent, published as U.S. Pat. No. 1,934,838, and elsewhere. In Andrussow's original work, he disclosed that catalysts can be chosen from oxidation catalysts that are infusible (solid) at the working temperature of around 1000°C; he included platinum, iridium, rhodium, palladium, osmium, gold or silver as catalytically active metals either in pure form or as alloys. He also noted that certain base metals, such as rare earth metals, thorium, uranium, and others, could also be used, such as in the form of infusible oxides or phosphates, and that catalysts could either be formed into nets (screens), or deposited on thermally-resistant solid supports such as silica or alumina. [0016] In subsequent development work, platinum-containing catalysts have been selected due to their efficacy and to the heat resistance of the metal even in gauze or net form. For example, a platinum-rhodium alloy can be used as the catalyst, which can be in the form of a metal gauze or screen such as a woven or knitted gauze sheet, or can be disposed on a support structure. In an example, the woven or knitted gauze sheet can form a mesh-like structure having a size from 20-80 mesh, e.g., having openings with a size from about 0.18 mm to about 0.85 mm. A catalyst can comprise from about 85 wt% to about 95 wt% Pt and from about 5 wt% to about 15 wt% Rh, such as 85/5 Pt/Rh, 90/10, or 95/5 Pt/Rh. A platinum-rhodium catalyst can also comprise small amounts of metal impurities, such as iron (Fe), palladium (Pd), iridium (Ir), ruthenium (Ru), and other metals. The impurity metals can be present in trace amounts, such as about 10 ppm or less.
[0017J A broad spectrum of possible embodiments of the Andrussow method is described in German Patent 549,055. In one example, a catalyst comprising a plurality of fine- mesh gauzes of Pt with 10% rhodium disposed in series is used at temperatures of about 800 to 2,500° C, 1,000 to 1,500° C, or about 980 to 1050° C. For example, the catalyst can be a commercially-available catalyst, such as a Pt-Rh catalyst gauze available from Johnson Matthey Pic, London, UK, or a Pt-Rh catalyst gauze available from Heraeus Precious Metals GmbH & Co., Hanau, Germany.
[0018] The composition of a gaseous waste stream from and Andrussow process can make disposal of the stream difficult. For example, the gaseous waste stream can be such that flaring is inefficient, harmful to the environment, outside the parameters of local or federal regulations, or combinations thereof. The present disclosure is directed to an apparatus and method for the synthesis of HCN via an Andrussow process, in which an improved flare can dispose of the gaseous waste stream taking into consideration environmental concerns, efficiency concerns, or governmental regulations.
[0019] FIG. 1 is a schematic block flow diagram of an example process 10 for the production of hydrogen cyanide (HCN) via the Andrussow process, according to the present disclosure. In the example process 10, a HCN reaction zone 12 is supplied with an ammonia (NH3) stream 2, a methane (CH4) stream 4, and an air stream 6 (which includes oxygen gas (02)). Air can include air and other oxygen-containing gas mixtures, including oxygen-enriched air having oxygen concentrations above about 21 vol%. Examples herein can be particularly useful when an Andrussow process is adapted to employ a gaseous oxygen feed stream 6 that contains somewhat higher levels of oxygen than air. For example, such a gaseous oxygen feed stream 6 can contain at least about 25 vol% oxygen, at least about 30 vol% oxygen, at least about 40 vol% oxygen, at least about 50 vol% oxygen, at least about 60 vol% oxygen, at least about 70 vol% oxygen, at least about 80 vol% oxygen, at least about 90 vol% oxygen, at least about 95 vol% oxygen, at least about 98 vol% oxygen. The process 10 can include an air Andrussow process, e.g., an air stream 6 that includes about 21 vol% oxygen, an air-enriched Andrussow process, e.g., an air stream 6 that includes greater than about 21 vol% oxygen but less than about 100 vol% oxygen, or an oxygen Andrussow process, e.g., an air stream 6 that includes about 100% oxygen.
[0020] The three feed streams 2, 4, 6, are mixed and reacted in one or more reactors to be converted to hydrogen cyanide and water in the presence of a catalyst according to Equation 1 :
2 NH3 + 2 CH4 + 3 02→2 HCN + 6 H20 [1]
[0021] The one or more reactors can include a HCN catalyst, such as platinum (Pt) or a platinum alloy, such as an alloy of platinum with rhodium (Rd) or palladium (Pd) containing at least about 85% platinum by weight. Alloys used in the Andrussow process can include, but are not limited to, 10 wt% Rh - 90 wt% Pt, 8 wt% Rh - 92 wt% Pt, 5 wt% Pd - 5 wt% Rh - 90 wt% Pt, or 5 wt% Rh - 95 wt% Pt. Alloys containing up to about 5 wt% iridium (Ir) can be used. In an example, the HCN catalyst can be designed to reduce by products, such as nitrous-oxide by products, and therefore can have an increase rhodium (Rh) content, or other materials, such as cobalt (Co). The HCN catalyst can be contained in a packed bed, such as in a packed bed reactor, or be formed as a gauze, such as by weaving or knitting metal filaments into gauze-like structures. Such formed catalysts are well established in the art and can contain the catalytic materials described herein.
[0022] The HCN catalyst can be a commercially-available catalyst, such as a Pt-Rh catalyst gauze available from Johnson Matthey Pic, London, UK, or a Pt-Rh catalyst gauze available from Heraeus Precious Metals GmbH & Co., Hanau, GERMANY.
[0023] The resulting product stream 14 from the HCN reaction zone 12 can be fed into an ammonia recovery system 16 that is configured to recover unreacted N¾. Ammonia can be recovered by NH3 absorption via providing one or more of phosphoric acid (H3P04), sulfuric acid (H2S04), or an ammonium phosphate solution to the product stream 14 that can absorb NH3 from the product stream 14. In the example shown in FIG. 1, a phosphoric acid stream 18 within the ammonia recovery system 16 can absorb NH3. Ammonia can be removed from the H3P04/NH3 solution using one or more strippers to separate the NH3 from the H3P04. The NH3 can be recycled back to the HCN reaction zone 12 via an NH3 recycle stream 20. The H3P04 and other waste can be purged as a wastewater stream 22, while an NH3-stripped HCN stream 24 can be fed to an HCN recovery system 26.
[0024] The HCN recovery system 26 can include one or more unit operations configured to separate and purify HCN from the HCN stream 24. As a result of the HCN recovery system 26, a purified HCN product stream 28 is produced. The HCN recovery system 26 can also produce a waste gas 30 or a wastewater stream 32. Wastewater streams 22, 32 can be fed to waste water treatment 36 for further processing, such as recovery of ammonia or hydrogen cyanide. The final wastewater stream 40 from the waste water treatment 36 can be further processed, stored, or disposed.
[0025] As illustrated in FIG. 1, HCN recovery system 26 can include a gaseous waste stream 30. Gaseous waste stream 30 can include hydrogen, carbon monoxide, nitrogen, carbon dioxide, hydrogen cyanide, or mixtures thereof. In an example, gaseous waste stream 30 can include additional waste streams not illustrated. For example, a waste stream from reactor 12 or other operation can be combined with stream 30. The composition of gas waste stream 30 can vary according to a number of factors, including composition of the feed streams 2, 4, 6, efficiency of the HCN reaction zone 12, efficiency of the ammonia recovery system 16, efficiency of the HCN recovery system 26, operating conditions, or combinations thereof.
[0026] In an example, gaseous waste stream 30 can feed a hydrogen recovery system 42.
In general, the gaseous waste stream 30 can contain residual amounts of HCN, as well as significant hydrogen gas or a variety of gases including unreacted methane, carbon dioxide, carbon monoxide, water, nitrogen, and a variety of organonitriles. Removal of HCN can be substantially complete, not only so that valuable HCN is not lost to the waste stream, but also for health and environmental concerns, and because significant amounts of HCN can complicate processing of the waste stream. For example, some pressure swing apparatus absorbents that can be used for hydrogen recovery can have operational limits of less than about 2.0% HCN, or less than about 1.5% HCN. Hence, the gaseous waste stream can have less than about 2.0% HCN, or less than about 1.5% HCN, or less than about 1% HCN, or less than about 0.5% HCN, or less than about 0.2% HCN, or less than about 0.1% HCN. In some situations, the HCN content of the gaseous waste stream 30 can vary, for example, between about 0.5% to about 1.0%. For example, gaseous waste stream 30 can include 40-75 vol% H2, 15-35 vol% CO, 5-15 vol% N2, 1- 2 vol% C02, 1-2 vol% CH4, or 0-1 vol% HCN.
[0027] The recovered hydrogen stream 50 can be stored for future processing or sale, sent to additional hydrogen processing units, recycled to a point upstream or downstream, used to supplement a flare 48 (as discussed further below), or combinations thereof. Hydrogen recovery system 42 can regulate a level of hydrogen that is recovered from combined gaseous waste stream 20. For example, if combined gaseous stream 30 is hydrogen rich, such as greater than about 40 vol%, hydrogen recovery system 42 can recover a larger percentage of hydrogen. While the recovered hydrogen stream 50 need not be 100% pure, removal of at least the majority of the carbon dioxide, carbon monoxide, or nitriles from hydrogen can be desirable to avoid side products and contaminants when the recovered hydrogen is used, for example, for hydrogenation reactions. For example, the recovered hydrogen gas can be at least about 90% pure, or at least about 91 % pure, or at least about 92% pure, or at least about 93 % pure, or at least about 94% pure, or at least about 95 % pure, or at least about 96% pure, or at least about 97 % pure, or at least about 98% pure, or at least about 99% pure hydrogen. Further, if a processing unit downstream, such as flare 48, is designed to operate at a range of hydrogen concentrations, hydrogen recovery system 42 can be optimized to provide a processed gaseous waste stream 52 to a processing unit downstream. In an example, the hydrogen recovery system 42 can produce a processed gaseous waste stream including at least about 8 vol% hydrogen. Gaseous waste stream 52 can include less than about 1.5% HCN. A valve can be located downstream of hydrogen recovery system 42 but upstream of processed gaseous waste stream 52, such that gaseous waste stream 30 feeds directly and only to the hydrogen recovery system 42.
[0028] In an example, system 10 can include the flare 48 to burn off gaseous waste stream 30. Flare 48 can be designed to thoroughly destroy gaseous waste. If the gaseous waste is dilute, stream 30 can be enriched with hydrocarbon fuel 56, such as natural gas, to increase a heating value of the resulting blend in order to ensure that the waste is thoroughly destroyed. Hydrogen has a lower net heating value than many hydrocarbon fuels. For example, the net heating value of methane is about 913 BTU/scf. On the other hand, the net heating value of hydrogen is only about 275 BTU/scf. In view of this disparity, one would not expect that a gaseous mixture containing a relatively low concentration of hydrogen would be sufficient to thoroughly destroy the dilute gaseous waste with which it is blended. However, unexpectedly, the present inventors discovered that a minimum amount of about at least 5 vol %, of about at least 7 vol%, of about at least 8 vol%, of about at least 10 vol % of hydrogen in the gaseous mixture flared was sufficient to ensure destruction of the gaseous waste.
[0029] In an example, a detector that can quantify components in the combustible gas mixture. A valve can be operably linked to the detector, where the valve is configured to permit supplementing the combustible gas mixture 30 with a hydrogen-containing enrichment fuel, such as hydrogen or methane, when a set value of non-combustible components, corresponding to a lower threshold of heat content, are detected in the combustible gas mixture. The amount of hydrogen-containing enrichment fuel needed to thoroughly destroy the dilute gaseous waste material upon combustion also depends, in part, on the heating value of the dilute gaseous waste material flared. The enrichment stream can contain a sufficient amount of hydrogen or hydrocarbons such that, when blended with the gaseous waste stream 30, the resulting blend can a sufficient heating value to thoroughly destroy the dilute gaseous waste material upon combustion in the flare 48.
[0030] In an example, a valve can be operably linked to the detector, where the valve is configured to permit supplementing the oxygen permitted to react when a hydrogen
concentration below a threshold value is detected in the combustible gas-mixture 30. An increase in the amount of oxygen 6 can result in an increase in hydrogen concentration in the combustible gas mixture 30. In an example, the oxygen can be provided by air stream 6 or an oxygen supplement stream upstream of or connected to the HCN reactor 12. Surprisingly, providing greater oxygen concentrations to the HCN reactor 12, and consequently lower inert gas concentrations (e.g., N2), can provide the benefit of more combustible gas waste 30 that can be utilized in flare 48. Typically, inert gases are utilized to provide a heat transfer benefit during the reaction. For example, the presence of nitrogen in the reactor can aid in decreasing temperature spikes. The present inventors have invented an HCN process capable of handling greater oxygen concentrations in a feed stream by using a flare, such as flare 48, to increase temperature control of the system. Further, greater oxygen concentrations in the feed stream can provide the benefit of reducing an amount of fuel, such as methane 4 required for the HCN reactor 12.
[0031] In an example flare 48 can be designed to meet local environment or federal environmental velocity requirements of the flare. For example, a flare exit velocity can be less than about 37.2 meters per second. Flare exit velocity is the velocity of the flare at the tip of the flare device 48. In another example, the flare velocity can be designed to be less than a Vmax, where Vmax is defined by
Vmax = (XH2 - K *K2, wherein
Vmax = maximum permitted flare exit velocity, meters per second
Ki = constant, 6.0 volume% hydrogen
K2 = constant, 3.9 meters per second per volume % hydrogen
Xm = volume % hydrogen, on a wet basis, as calculated by using the American Society for Testing and Materials (ASTM) Method D 1946-77. Increasing the amount of oxygen allowed to react in the HCN reactor 12 can provide the benefit of increasing the concentration of hydrogen in the waste stream 30, consequently increasing the flare velocity, as described above.
[0032] In an example, the flare 48 can be designed to burn the combustible gaseous mixture at temperatures of greater than about 1000 °C, greater than about 1200 °C, of greater than about 1350 °C, of greater than about 1500 °C, of greater than about 1600 °C, or greater than about 1800 °C. The flare burn temperature can include a temperature greater than a combustion temperature of one or more component of the combustible gaseous mixture. In an example, the combustible gaseous mixture can include supplemental hydrocarbons, such as natural gas, or hydrogen, to increase the combustibility of the combustible gaseous mixture.
[0033] The flare 48 can include any flare suitable for destruction of the combustible gaseous mixture. For example, the flare 48 can include an unassisted flare or an assisted flare, or stabilized or non-stabilized flare. An assisted flare includes an additional stream, such as steam assisted or air assisted, to provide for an increased flare exit velocity, increased combustible composition, more consistent combustible composition, or combinations thereof. A stabilized flare can include an additional stream, such as hydrocarbon stabilized or air stabilized, to increase flare consistency, such as exit velocity, or temperature. A flare nozzle of the flare 48 can be in compliance of any designed regulations, such as a flare tip or nozzle dimension. In an example, the flare zone can include an at least a 3.0 inch diameter flare tip.
[0034] In an example, the flare zone further can be configured to operate with a non- hydrogen combustible gas mixture burned in a non-hydrogen mode. The non-hydrogen combustible gas mixture can include a heat value of at least about 200 BTU/scf. The flare 48 can switch between a hydrogen mode, such as burning a minimum percentage of hydrogen, or a non-hydrogen mode, such as zero vol% hydrogen, or combinations thereof. The flare 48 can provide the benefit of increased operational flexibility.
[0035] In an example, the system 10 can include a scrubber downstream or upstream of the hydrogen recovery system 42 to remove at least a portion of liquid, such as water, present in gaseous waste stream 30. Removing liquid provided to the flare 48 can provide a steady flare, a more predictable heat capacity of the feed provided to the flare 48. Combustible gaseous waste 30 can be fed to additional processes 54 of system 10, such as a boiler that can be utilized downstream to recycle heat energy.
[0036] According to the present disclosure, a method for the production of hydrogen cyanide can include allowing oxygen, ammonia, and methane to react in the presence of the catalyst comprising platinum to give a product stream comprising at least hydrogen cyanide, hydrogen, and the waste product. The method can further include extracting the hydrogen cyanide from the product stream to produce the HCN product stream (FIG. 1, element 28) and the gaseous waste stream (FIG. 1, element 30) comprising at least a portion of the hydrogen and the waste product and feeding the gaseous waste stream to a hydrogen mode flare (FIG. 1, element 48). The gaseous waste stream can include more than one gaseous waste stream combined with the gaseous waste stream, such that at least a portion of the waste from the system is flared, for example in flare 48.
[0037] In an example, the method can include separating at least a portion of liquid in the gaseous waste stream, such as by a vapor-liquid separator, flash drum, knock-out drum, knockout pot, compressor suction drum, compressor inlet drum, demister, or combinations thereof.
[0038] In an example, the method includes extracting ammonia from the product stream, such as by an ammonia scrubber. The method can also include recovering hydrogen from the gaseous waste stream or combined gaseous waste stream. For example, the hydrogen composition of the gaseous waste stream may be in excess of hydrogen mode flaring levels. In such instances, the excess hydrogen can be recovered and utilized elsewhere in a plant, stored for future use or sale, or combinations thereof.
[0039] The method can include regulating the flare, such that the flare exit velocity is less than about 37.2 meters per second. Regulating flare exit velocity can provide the benefit of a stable flare, increasing the destruction of the elements or compounds burned. Further, the method can include flaring the gaseous waste stream at a temperature of greater than about 1650 ° C.
EXAMPLES
Example 1: Comparison Air, Air Enriched, and Oxygen Andrussow Process Waste Gas Compositions
[0040] This Example illustrates that an Andrussow process that uses an enriched source of oxygen generally produces a waste stream with higher hydrogen content than one that employs air as an oxygen source.
[0041] The method can include regulating the flare, such that the flare exit velocity is less than about 37.2 meters per second. Regulating flare exit velocity can provide the benefit of a stable flare, increasing the destruction of the elements or compounds burned. Further, the method can include flaring the gaseous waste stream at a temperature of greater than about 1650 ° C.
[0042] A 4 inch internal diameter stainless steel reactor with ceramic insulation lining inside is used for pilot scale test. Forty sheets of 90 wt% Pt/10 wt% Rh 40 mesh gauze from Johnson Matthey (USA) are loaded as catalyst bed. Perforated alumina tile is used for catalyst sheet support. The total flow rate is set at 2532 SCFH (standard cubic foot per hour). Hydrogen cyanide is produced via multiple Andrussow processes. One process, the air Andrussow process, employs an oxygen-containing gas (air) that includes 21 vol% oxygen. A second process, the air- enriched Andrussow process, employs an oxygen-containing gas having greater than about 21 vol% oxygen and less than about 100 vol% oxygen. A third process, the oxygen Andrussow process, employs an oxygen-containing gas that is about 100 vol% oxygen.
[0043] Ammonia is separately removed from each of the product streams in a process involving absorption into an ammonium phosphate stream. Hydrogen cyanide is then removed from the ammonia-depleted product stream in a process involving acidified water, thereby separately generating a hydrogen cyanide product and a gaseous waste stream for each of the processes.
[0044] The composition of the gaseous waste streams from the air, air enriched, and oxygen processes are shown below in Table 1.
Table 1
Figure imgf000014_0001
[0045] As illustrated, an Andrussow process that employs an enriched oxygen stream as a source of the oxygen reactant generates significantly more hydrogen than an Andrussow process that employs air as a source of the oxygen reactant. Example 2: Comparison BTU values for Air, Air Enriched and Oxygen Andrussow Process Waste Gas Compositions
[0046] This Example illustrates that an Andrussow process that uses an enriched source of oxygen generally produces a waste stream with higher heating value than one that employs air as an oxygen source.
[0047] Three processes, as outlined in Example 1 , are used to produce HCN. The heating value of the gaseous waste streams from the air, air enriched, and oxygen processes are shown below in Table 2.
Table 2
Figure imgf000015_0001
[0048] As illustrated, an Andrussow process that employs an enriched oxygen stream as a source of the oxygen reactant generates a waste stream with a significantly lower heating value than an Andrussow process that employs air as a source of the oxygen reactant.
[0049] The above Detailed Description is intended to be illustrative, and not restrictive.
For example, the above-described examples (or one or more elements thereof) can be used in combination with each other. Other examples can be used, such as by one of ordinary skill in the art upon reviewing the above description. Also, various features or elements can be grouped together to streamline the disclosure. This should not be interpreted as intending that an unclaimed disclosed feature is essential to any claim. Rather, inventive subject matter can lie in less than all features of a particular disclosed example. Thus, the following claims are hereby incorporated into the Detailed Description, with each claim standing on its own as a separate example. The scope of the invention should be determined with reference to the appended claims, along with the full scope of equivalents to which such claims are entitled.
[0050] In the event of inconsistent usages between this document and any documents so incorporated by reference, the usage in this document controls.
[0051] In this document, the terms "a" or "an" are used, as is common in patent documents, to include one or more than one, independent of any other instances or usages of "at least one" or "one or more." In this document, the term "or" is used to refer to a nonexclusive or, such that "A or B" includes "A but not B," "B but not A," and "A and B," unless otherwise indicated. In this document, the terms "including" and "in which" are used as the plain-English equivalents of the respective terms "comprising" and "wherein." Also, in the following claims, the terms "including" and "comprising" are open-ended, that is, a system, device, article, composition, formulation, or process that includes elements in addition to those listed after such a term in a claim are still deemed to fall within the scope of that claim. Moreover, in the following claims, the terms "first," "second," and "third," etc. are used merely as labels, and are not intended to impose numerical requirements on their objects.
[0052] Method examples described herein can be machine or computer-implemented, at least in part. Some examples can include a computer-readable medium or machine-readable medium encoded with instructions operable to configure an electronic device to perform methods or method steps as described in the above examples. An implementation of such methods or method steps can include code, such as microcode, assembly language code, a higher-level language code, or the like. Such code can include computer readable instructions for performing various methods. The code may form portions of computer program products. Further, in an example, the code can be tangibly stored on one or more volatile, non-transitory, or non- volatile tangible computer-readable media, such as during execution or at other times. Examples of these tangible computer-readable media can include, but are not limited to, hard disks, removable magnetic disks, removable optical disks (e.g., compact disks and digital video disks), magnetic cassettes, memory cards or sticks, random access memories (RAMs), read only memories (ROMs), and the like.
[0053] The Abstract is provided to comply with 37 C.F.R. § 1.72(b), to allow the reader to quickly ascertain the nature of the technical disclosure. It is submitted with the understanding that it will not be used to interpret or limit the scope or meaning of the claims.
[0054] Although the invention has been described with reference to exemplary examples, workers skilled in the art will recognize that changes may be made in form and detail without departing from the spirit and scope of the invention.
[0055] The invention has been described broadly and generically herein. Each of the narrower species and subgeneric groupings falling within the generic disclosure also form part of the invention. This includes the generic description of the invention with a proviso or negative limitation removing any subject matter from the genus, regardless of whether or not the excised material is specifically recited herein. In addition, where features or aspects of the invention are described in terms of Markush groups, those skilled in the art will recognize that the invention is also thereby described in terms of any individual member or subgroup of members of the Markush group.
[0056] The following statements describe some of the elements or features of the invention. Because this application is a provisional application, these statements may become changed upon preparation and filing of a nonprovisional application. Such changes are not intended to affect the scope of equivalents according to the claims issuing from the
nonprovisional application, if such changes occur. According to 35 U.S.C. § 111(b), claims are not required for a provisional application. Consequently, the statements of the invention cannot be interpreted to be claims pursuant to 35 U.S.C. § 112. STATEMENTS OF THE INVENTION:
[0057] 1. A system for producing hydrogen cyanide via the Andrussow process,
comprising:
a reactor zone wherein oxygen, ammonia, and methane are allowed to react in the presence of a catalyst comprising platinum or platinum alloy to provide a product stream comprising at least hydrogen cyanide (HCN), hydrogen, and waste product;
an HCN recovery zone wherein the hydrogen cyanide is substantially removed from the product stream to generate a hydrogen cyanide product and a combustible gas mixture comprising the hydrogen and the waste product; and
a flare zone wherein at least the combustible gas mixture is burned in a hydrogen mode to produce at least carbon dioxide and water.
[0058] 2. The system of statement 1, wherein a hydrocarbon mixture comprises the methane.
[0059] 3. The system of statement 2, wherein the hydrocarbon mixture comprises natural gas, biogas, substantially pure methane, or mixtures thereof.
[0060] 4. The system of any one of statements 1-3, further comprising a hydrogen recovery system that recovers at least some hydrogen from at least one of the product stream and the combustible gas mixture.
[0061] 5. The system of any one of statements 1-4, further comprising an ammonia recovery system that substantially removes ammonia from the product stream.
[0062] 6. The system of any one of statements 1-5, wherein the hydrogen cyanide product is at least about 98.5 vol% pure hydrogen cyanide.
[0063] 7. The system of any one of statements 1-6, wherein the combustible gas mixture comprises at least about 8 vol% hydrogen.
[0064] 8. The system of any one of statements 1-7, wherein the flare has a flare exit velocity of less than about 37.2 meters per second.
[0065] 9. The system of any one of statements 1-8, wherein the flare has a flare exit velocity of less than about Vmax, wherein Vmax is defined by:
Vmax = (XH2 - K *K2, wherein
Vma = maximum permitted flare exit velocity, meters per second
K\ = constant, 6.0 volume% hydrogen K2 = constant, 3.9 meters per second per volume % hydrogen XH2 = volume % hydrogen, on a wet basis, as calculated by using the American Society for Testing and Materials (ASTM) Method D 1946-77.
[0066] 10. The system of any one of statements 1-9, wherein the flare zone comprises temperatures of greater than about 1000 °C, greater than about 1200 °C, of greater than about 1350 °C, of greater than about 1500 °C, of greater than about 1600 °C, or greater than about 1800 °C
[0067] 11. The system of any one of statements 1-10, wherein the flare zone comprises an unassisted flare.
[0068] 12. The system of any one of statements 1-11, wherein the flare zone comprises at least a 3.0 inch diameter flare tip.
[0069] 13. The system of any one of statements 1-12, further comprising a flare stabilizer.
[0070] 14. The system of any one of statements 1-13, wherein the flare zone further comprises natural gas.
[0071] 15. The system of any one of statements 1-14, further comprising a hydrogen source that adds hydrogen to the combustible gas mixture.
[0072] 16. The system of any of statements 1-15, further comprising a detector that quantifies components in the combustible gas mixture.
[0073] 17. The system of statement 16, further comprising a valve operably linked to the detector, where the valve is configured to permit supplementing the combustible gas mixture with hydrogen or methane when a set value of non-combustible components, corresponding to a lower threshold of heat content, are detected in the combustible gas mixture.
[0074] 18. The system of statement 16, further comprising a valve operably linked to the detector, where the valve is configured to permit supplementing the oxygen permitted to react when a hydrogen concentration below a threshold value is detected in the combustible gas- mixture.
[0075] 19. The system of statement 18, wherein the threshold value is based on a heat content value of the combustible gas mixture.
[0076] 20. The system of statement 18 or 19, wherein the valve is operably linked to an air feed stream. [0077] 21. The system of statement 18 or 19, wherein the valve is operably linked to an oxygen feed stream.
[0078] 22. The system of statement 18 or 19, wherein the valve is operably linked to an oxygen enriched air feed stream.
[0079] 23. The system of any one of statements 1 -22, wherein the flare zone further comprises a non-hydrogen combustible gas mixture burned in a non-hydrogen mode.
[0080] 24. The system of statement 23, wherein the non-hydrogen combustible gas mixture comprises a heat value of at least about 200 BTU/scf.
[0081] 25. The system of any one of statements 1 -24, wherein the waste product comprises less than about 1.5% HCN.
[0082] 26. The system of any one of statements 1-25, further comprising at least one liquid separator, upstream of the flare, to remove at least a portion of liquid present in the combustible gas mixture or non-hydrogen combustible gas mixture.
[0083] 27. A method for burning a waste product produced by an Andrussow process, comprising:
allowing oxygen, ammonia, and methane to react in the presence of a catalyst comprising platinum to give a product stream comprising at least hydrogen cyanide, hydrogen, and a waste product;
extracting the hydrogen cyanide from the product stream to produce a hydrogen cyanide stream and a gaseous waste stream comprising at least a portion of the hydrogen and the waste product; and
feeding the gaseous waste stream to a hydrogen mode flare.
[0084] 28. The method of statement 27, further comprising extracting ammonia from the product stream.
[0085] 29. The method of statement 27 or 23, further comprising separating at least a portion of liquid from the gaseous waste stream prior to feeding the extracted stream to the hydrogen mode flare.
[0086] 30. The method of any one of statements 27-29, further comprising recovering hydrogen from the gaseous waste stream.
[0087] 31. The method of any one of statements 27-30, further comprising extracting ammonia prior to extracting the hydrogen cyanide. [0088] 32. The method of any one of statements 27-31 , further comprising flaring the gaseous waste stream at a flare exit velocity of less than about 37.2 meters per second.
[0089] 33. The method of any one of statements 27-32, further comprising flaring the gaseous waste stream at a flare exit velocity of less than about Vmax, wherein Vmax is defined by:
Vmax = (XH2 - i)*K2, wherein
Vmax = maximum permitted flare exit velocity, meters per second
K] = constant, 6.0 volume% hydrogen
K2 = constant, 3.9 meters per second per volume % hydrogen
XH2 = volume % hydrogen, on a wet basis, as calculated by using the
American Society for Testing and Materials (ASTM) Method D 1946-77.
[0090] 34. The method of any one of statements 27-33, further comprising flaring the gaseous waste stream at a temperature of greater than about 1650 °C.
[0091] 35. The method of any one of statements 27-34, further comprising stabilizing the hydrogen mode flare with a flare stabilizer.
[0092] 36. The method of any one of statements 27-35, further comprising increasing a hydrogen concentration of the gaseous waste to increase a heating value of the gaseous waste.
[0093] 37. The method of any one of statements 27-36, further comprising
supplementing the gaseous waste with a hydrogen supplement stream.
[0094] 38. The method of statement 36, further comprising increasing an amount of the oxygen allowed to react.
[0095] 39. The method of any one of statements 27-37, further comprising: detecting a hydrogen concentration of the gaseous waste; and increasing an amount of oxygen allowed to react when the hydrogen concentration is detected below a threshold value.
[0096] 40. The method of statement 39, further comprising increasing an oxygen concentration of an air feed stream.
[0097] 41. The system or method of any one or any combination of statements 1-40 is optionally configured such that all elements or options recited are available to use or select from.

Claims

CLAIMS What is claimed is:
1. A system for producing hydrogen cyanide via an Andrussow process, comprising:
a reactor zone wherein oxygen, ammonia, and methane are allowed to react in the presence of a catalyst comprising platinum to provide a product stream comprising at least hydrogen cyanide (HCN), hydrogen, and waste product;
an HCN recovery zone wherein the hydrogen cyanide is substantially removed from the product stream to generate a hydrogen cyanide product and a combustible gas mixture comprising the hydrogen and the waste product; and
a flare zone wherein at least the combustible gas mixture is burned in a hydrogen mode to produce at least carbon dioxide and water.
2. The system of claim 1 , wherein a hydrocarbon mixture comprises the methane.
3. The system of claim 2, wherein the hydrocarbon mixture comprises natural gas, biogas, substantially pure methane, or mixtures thereof.
4. The system of any one of claims 1-3, further comprising a hydrogen recovery system connected to the reactor zone that recovers at least some hydrogen from at least one of the product stream and the combustible gas mixture.
5. The system of any one of claims 1-4, further comprising an ammonia recovery system that substantially removes ammonia from the product stream.
6. The system of any one of claims 1-5, wherein the hydrogen cyanide product is at least about 98.5 vol% pure hydrogen cyanide.
7. The system of any one of claims 1-6, wherein the combustible gas mixture comprises at least about 8 vol% hydrogen.
8. The system of any one of claims 1-7, wherein the flare has a flare exit velocity of less than about 37.2 meters per second.
9. The system of any one of claims 1 -8, wherein the flare has a flare exit velocity of less than about Vraax, wherein Vmax is defined by:
Vmax = (XH2 - Ki)*K2, wherein
max = maximum permitted flare exit velocity, meters per second Ki = constant, 6.0 volume% hydrogen
K2 = constant, 3.9 meters per second per volume % hydrogen
XH2 = volume % hydrogen, on a wet basis, as calculated by using the American Society for Testing and Materials (ASTM) Method Dl 946-77.
10. The system of any one of claims 1-9, wherein the flare zone comprises temperatures of greater than about 1350 °C.
11. The system of any one of claims 1-10, wherein the flare zone comprises an unassisted flare.
12. The system of any one of claims 1-1 1, wherein the flare zone comprises at least a 3.0 inch diameter flare tip.
13. The system of any one of claims 1-12, further comprising a flare stabilizer.
14. The system of any one of claims 1-13, wherein the flare zone further comprises natural gas.
15. The system of any one of claims 1-14, further comprising a hydrogen source that adds hydrogen to the combustible gas mixture.
16. The system of any of claims 1-15, further comprising a detector that quantifies components in the combustible gas mixture.
17. The system of claim 16, further comprising a valve operably linked to the detector, where the valve is configured to permit supplementing the combustible gas mixture with hydrogen or methane when a set value of non-combustible components, corresponding to a lower threshold of heat content, are detected in the combustible gas mixture.
18. The system of claim 16, further comprising a valve operably linked to the detector, where the valve is configured to permit supplementing the oxygen permitted to react when a hydrogen concentration below a threshold value is detected in the combustible gas-mixture.
19. The system of claim 18, wherein the threshold value is based on a heat content value of the combustible gas mixture.
20. The system of claim 18 or 19, wherein the valve is operably linked to an air feed stream.
21. The system of claim 18 or 19, wherein the valve is operably linked to an oxygen feed stream.
22. The system of claim 18 or 19, wherein the valve is operably linked to an oxygen enriched air feed stream.
23. The system of any one of claims 1-22, wherein the flare zone further comprises a non- hydrogen combustible gas mixture burned in a non-hydrogen mode.
24. The system of claim 23, wherein the non-hydrogen combustible gas mixture comprises a heat value of at least about 200 BTU/scf.
25. The system of any one of claims 1-24, wherein the waste product comprises less than about 1.5 vol% HCN.
26. The system of any one of claims 1-25, further comprising at least one liquid separator, upstream of the flare, to remove at least a portion of liquid present in the combustible gas mixture or non-hydrogen combustible gas mixture.
27. A method for burning a waste product produced by an Andrussow process, comprising: allowing oxygen, ammonia, and methane to react in the presence of a catalyst comprising platinum to give a product stream comprising at least hydrogen cyanide, hydrogen, and a waste product;
extracting the hydrogen cyanide from the product stream to produce a hydrogen cyanide stream and a gaseous waste stream comprising at least a portion of the hydrogen and the waste product; and
feeding the gaseous waste stream to a hydrogen mode flare.
28. The method of claim 27, further comprising extracting ammonia from the product stream.
29. The method of claim 27 or 28, further comprising separating at least a portion of liquid from the gaseous waste stream prior to feeding the extracted stream to the hydrogen mode flare.
30. The method of any one of claims 27-29, further comprising recovering hydrogen from the gaseous waste stream.
31. The method of any one of claims 27-30, further comprising extracting ammonia prior to extracting the hydrogen cyanide.
32. The method of any one of claims 27-31 , further comprising flaring the gaseous waste stream at a flare exit velocity of less than about 37.2 meters per second.
33. The method of any one of claims 27-32, further comprising flaring the gaseous waste stream at a flare exit velocity of less than about Vmax, wherein Vmax is defined by:
Vmax = (XH2 - ¾)*¾, wherein
Vmax = maximum permitted flare exit velocity, meters per second
Ki = constant, 6.0 volume% hydrogen
K2 = constant, 3.9 meters per second per volume % hydrogen
XH2 = volume % hydrogen, on a wet basis, as calculated by using the American Society for Testing and Materials (ASTM) Method D 1946-77.
34. The method of any one of claims 27-33, further comprising flaring the gaseous waste stream at a temperature of greater than about 1650 °C.
35. The method of any one of claims 27-34, further comprising stabilizing the hydrogen mode flare with a flare stabilizer.
36. The method of any one of claims 27-35, further comprising increasing a hydrogen concentration of the gaseous waste to increase a heating value of the gaseous waste.
37. The method of any one of claims 27-36, further comprising supplementing the gaseous waste with a hydrogen supplement stream.
38. The method of claim 36, further comprising increasing an amount of the oxygen allowed to react.
39. The method of any one of claims 27-37, further comprising:
detecting a hydrogen concentration of the gaseous waste; and
increasing an amount of oxygen allowed to react when the hydrogen concentration is detected below a threshold value.
40. The method of claim 39, further comprising increasing an oxygen concentration of an air feed stream.
PCT/US2013/074609 2012-12-18 2013-12-12 Apparatus and method of an improved flare in an andrussow process Ceased WO2014099591A1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
US201261738817P 2012-12-18 2012-12-18
US61/738,817 2012-12-18

Publications (1)

Publication Number Publication Date
WO2014099591A1 true WO2014099591A1 (en) 2014-06-26

Family

ID=49881124

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/US2013/074609 Ceased WO2014099591A1 (en) 2012-12-18 2013-12-12 Apparatus and method of an improved flare in an andrussow process

Country Status (4)

Country Link
CN (1) CN103864112B (en)
HK (1) HK1198994A1 (en)
TW (1) TW201441156A (en)
WO (1) WO2014099591A1 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107420917A (en) * 2016-05-24 2017-12-01 英尼奥斯欧洲股份公司 Exhaust gas incinerator control

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE549055C (en) 1930-04-15 1932-04-22 I G Farbenindustrie Akt Ges Process for the production of hydrogen cyanide
US1934838A (en) 1930-04-14 1933-11-14 Ig Farbenindustrie Ag Production of hydrocyanic acid
EP1172137A2 (en) * 2000-07-12 2002-01-16 Rohm And Haas Company Laboratory scale reaction systems
WO2009075692A2 (en) * 2007-05-14 2009-06-18 Invista Technologies S.A.R.L. High efficiency reactor and process

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE102007014586A1 (en) * 2007-03-23 2008-09-25 Evonik Röhm Gmbh Process for the production of hydrogen cyanide (HCN)
TWM501893U (en) * 2012-12-18 2015-06-01 Invista Tech Sarl Apparatus of an improved flare in an andrussow process

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US1934838A (en) 1930-04-14 1933-11-14 Ig Farbenindustrie Ag Production of hydrocyanic acid
DE549055C (en) 1930-04-15 1932-04-22 I G Farbenindustrie Akt Ges Process for the production of hydrogen cyanide
EP1172137A2 (en) * 2000-07-12 2002-01-16 Rohm And Haas Company Laboratory scale reaction systems
WO2009075692A2 (en) * 2007-05-14 2009-06-18 Invista Technologies S.A.R.L. High efficiency reactor and process

Non-Patent Citations (6)

* Cited by examiner, † Cited by third party
Title
"Ullmann's Encyclopedia of Industrial Chemistry", vol. 8, 1987, VCH VERLAGSGESELLSCHAFT, pages: 161 - 162
CLEAN DEVELOPMENT MECHANISM PROJECT DESIGN DOCUMENT FORM (CDM PDD, 28 July 2006 (2006-07-28)
ERIC L. CRUMP: "U.S. Environmental Protection Agency, Office of Air Quality Planning and Standards", ECONOMIC IMPACT ANALYSIS FOR THE PROPOSED CYANIDE MANUFACTURING NESHAP, May 2000 (2000-05-01), Retrieved from the Internet <URL:http://nepis.epa.gov/Exe/ZyPDF.cgi?Dockey=P100AHG1.PDF>
GARY R. MAXWELL ET AL.: "Assuring process safety in the transfer of hydrogen cyanide manufacturing technology", J. OF HAZARDOUS MATERIALS, vol. 142, 2007, pages 677 - 84
N.V. TRUSOV: "Effect of Sulfur Compounds and Higher Homologues of Methane on Hydrogen Cyanide Production by the Andrussow Method", RUS. J. OF APPLIED CHEMISTRY, vol. 74, no. 10, 2001, pages 1693 - 97
PESCE, L.D.: "Cyanides. Kirk-Othmer Encyclopedia of Chemical Technology", 12 March 2010, pages: 1 - 29, XP002723419, DOI: 10.1002/0471238961.0325011416051903.a01.pub2 *

Also Published As

Publication number Publication date
HK1198994A1 (en) 2015-06-19
TW201441156A (en) 2014-11-01
CN103864112B (en) 2019-01-04
CN103864112A (en) 2014-06-18

Similar Documents

Publication Publication Date Title
Ma et al. Study on removal of elemental mercury from simulated flue gas over activated coke treated by acid
CN108455529B (en) Device and method for hydrogen recovery in andrussow process
WO2014099591A1 (en) Apparatus and method of an improved flare in an andrussow process
WO2013190335A1 (en) Improved sulphur dioxide treatment
TWI519475B (en) Process for producing hydrogen cyanide and recovering hydrogen
JP5939189B2 (en) How to operate steelworks
JP2016502970A (en) Reduction of organonitrile impurity level in HCN by oxygen andrussault process
TWM501893U (en) Apparatus of an improved flare in an andrussow process
EP2877447B1 (en) Use of urea synthesis purge gas in an integrated ammonia-urea process and related plant
TWI519477B (en) Enhanced methane control for andrussow process
CN204237572U (en) For the system of the recirculation in Andrussow process
EP2935108A1 (en) Reactor scheme in andrussow process
CN204237573U (en) For arranging the system of the reactor in Andrussow process
EP2935111A1 (en) Apparatus and method for reducing catalyst poisoning in an andrussow process
HK1198995A1 (en) System and method for recycling in andrussow process
CN113816398B (en) Ammonia ratio variation in Anderlufu process
TWM493541U (en) Reaction assembly for preparing hydrogen cyanide
WO2011140294A1 (en) Method and apparatus for eliminating pollutants from a gas stream
Yi et al. Purifying PH3 with Cu2+ Absorption Solution
JPS6197123A (en) CO recovery method from CO-containing mixed gas

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 13812429

Country of ref document: EP

Kind code of ref document: A1

DPE1 Request for preliminary examination filed after expiration of 19th month from priority date (pct application filed from 20040101)
NENP Non-entry into the national phase

Ref country code: DE

122 Ep: pct application non-entry in european phase

Ref document number: 13812429

Country of ref document: EP

Kind code of ref document: A1