Process for producing phosphorus-chlorine compounds from phosphorus-oxygen compound-containing material
The reaction of phosphorus-oxygen compounds with tetrachloroethene at elevated temperatures efficiently produces phosphorus oxychloride, addressing energy and environmental concerns in existing phosphorus-chlorine compound production methods.
Patent Information
- Application Number
- PCT/EP2024/069052
- Authority / Receiving Office
- WO · WO
- Patent Type
- Applications
- Current Assignee / Owner
- Priority Date
- 2023-07-11
- Filing Date
- 2024-07-05
- Publication Date
- 2025-01-16
AI Technical Summary
Current methods for producing phosphorus-chlorine compounds are energy-intensive, generate toxic by-products, and result in long reaction times, with the use of carbon tetrachloride being environmentally banned due to ozone layer damage.
Reacting materials containing phosphorus-oxygen compounds with tetrachloroethene at 500 to 1000°C to produce phosphorus-chlorine compounds, particularly phosphorus oxychloride, in the presence of an inert gas, allowing for efficient isolation in the exhaust gas stream.
This process effectively produces phosphorus oxychloride with reduced energy consumption and environmental impact, avoiding the handling of toxic substances and ozone-damaging reagents, while achieving quantitative conversion.
Smart Images

Figure IMGF000002_0001
Abstract
Description
[0001] Process for the extraction of -chlorine-' from material
[0002] The invention relates to a process for converting material containing phosphorus-oxygen compounds into at least one phosphorus-chlorine compound. These compounds can then be used for industrial purposes.
[0003] The digestion of phosphates, especially water-insoluble ones, with the aim of technically and economically exploiting or quantitatively determining the phosphorus compound they contain plays a major role in analytics and technology. In analytics, it is used to determine phosphorus in rocks or ores. Calcium phosphate sources are industrially reacted with sulfuric acid in huge quantities to obtain water-soluble phosphoric acid, which is used primarily as a fertilizer or detergent additive, and to a lesser extent as an acidifier, for example, in the food industry.
[0004] Phosphate extraction / phosphoric acid extraction is carried out technically by lowering the pH value in an aqueous slurry of ground phosphate rock, preferably with mineral acids such as sulfuric acid or phosphoric acid, followed by filtration. The disadvantages of this process are that it requires very large quantities of acid and a technically difficult-to-manage filtration step with corresponding byproducts is mandatory. It also generates large amounts of waste.
[0005] However, these reactions do not lead to the desired phosphorus-chlorine compounds.
[0006] The production of phosphorus-chlorine compounds on an industrial scale is carried out exclusively via the energy-intensive and laborious detour of the synthesis of elemental phosphorus followed by reaction with elemental chlorine.
[0007] The extraction of phosphorus-chlorine compounds on an industrial scale generally occurs via elemental phosphorus, produced from phosphate rock, coal, and additives in an electric arc furnace, followed by the combustion of the phosphorus with chlorine to form phosphorus-chlorine compounds. Disadvantages here include the very high electricity consumption, the high temperatures, the handling of toxic white phosphorus, the arsenic compounds it contains, the handling of toxic chlorine, the immense quantities of slag that must be disposed of, and the very large CO2 footprint. However, only phosphorus chlorides such as PCh are accessible in this way. Phosphorus oxychloride POCl3 is not available in this way; it must first be produced in a further step by oxidation from PCl3.
[0008] One method for the direct extraction of phosphorus-chlorine compounds from phosphates as a volatile compound is the use of carbon tetrachloride, sometimes in combination with chlorine and / or with inert gases such as carbon dioxide. The sample is heated to 700°C to 900°C, and the gas stream is passed over it. The gas stream is then fed into a scrubber and analyzed for phosphate. Quantitative conversion is reported, and the method has been tested on numerous metal phosphates (Jannasch, P., Jilke, W.; Journal für praktisch Chemie, 21, 1908 and Jannasch P., Jilke, W.; Journal für praktisch Chemie, 113, 1909).
[0009] The disadvantage of this process is the long reaction times described. Above all, the use of carbon tetrachloride in industrial processes has now been banned because the compound damages the ozone layer, making this reaction technically impossible.
[0010] Task
[0011] The object of the present invention was therefore to find a process for producing phosphorus-chlorine compounds that no longer has the described disadvantages of the prior art. Surprisingly, a process for producing phosphorus-chlorine compounds, in particular phosphorus oxychloride, was found, which is characterized in that i. a material containing a phosphorus-oxygen compound is reacted in the presence of tetrachloroethene at a temperature of 500 to 1000°C, preferably 600 to 900°C, in particular 700 to 850°C, and ii. the resulting phosphorus-chlorine compounds, in particular phosphorus oxychloride, are removed and isolated in the exhaust gas stream.
[0012] The phosphorus-chlorine compound phosphorus oxychloride is preferably prepared using the process according to the invention.
[0013] Phosphorus-oxygen compounds
[0014] Various materials containing phosphorus-oxygen compounds can be used. For example, the phosphorus-oxygen compound-containing material can contain at least one phosphorus-oxygen compound selected from the group of inorganic alkali and / or alkaline earth metal salts of phosphorus-oxygen compounds, their phosphates, in particular calcium phosphates, apatites, in particular chloroapatites or hydroxylapatites, sodium phosphates, iron phosphates, aluminum phosphates, lithium iron phosphates, in particular lithium iron phosphate or lithium iron manganese phosphate, or phosphinic acids, phosphoric acids, their respective polyacids or anhydrides, or mixtures thereof.
[0015] The phosphorus-oxygen compound-containing material preferably contains calcium phosphates, in particular their corresponding orthophosphates or metaphosphates or polyphosphates, or mixtures thereof. Particularly preferred calcium phosphates are calcium phosphate, in particular calcium orthophosphate, calcium metaphosphate, calcium hydroxylapatite, or mixtures thereof.
[0016] The phosphorus-oxygen compound-containing material preferably contains at least one inorganic phosphate, in particular the corresponding orthophosphates, metaphosphates, or polyphosphates, or mixtures thereof. It particularly preferably contains calcium phosphate, particularly preferably calcium orthophosphate or calcium hydroxylapatite.
[0017] The phosphorus-oxygen compound-containing material preferably contains at least one phosphorus-oxygen compound with a content, calculated as elemental phosphorus, of 1 to 44 wt.%, preferably of 1 to 30 wt.%, in particular of 5 to 28 wt.%, based on the phosphorus-oxygen compound-containing material.
[0018] Also preferred is the process which is characterized in that the phosphorus-oxygen compound-containing material is sewage sludge ash or a black mass containing iron phosphates.
[0019] Sewage sludge ash is preferably understood to refer to both the solid residue resulting from sewage sludge incineration and the solid residue resulting from sewage sludge gasification to produce fuel gas. Sewage sludge ash can contain various components, such as aluminum phosphates, iron phosphates such as calcium iron phosphate (e.g., CaFe(PO4)7) or whitlockite (Ca3(PO4)2), gypsum, calcium hydroxides, oxides, and carbonates, iron oxides such as hematite (Fe2O3), quartz (SiO2), and Indialite (Mg2Al4SisOi8), to name just a few.
[0020] The sewage sludge ash preferably contains a proportion of phosphorus-oxygen compounds, in particular phosphates, with a content calculated as phosphorus of 1.5 to 13.1 wt.%, based on the phosphorus-oxygen compound-containing material, preferably iron compounds of 1 to 21 wt.% (calculated as elemental iron), and a proportion of aluminum compounds of 0.7 to 20.2 wt.%, calculated as elemental aluminum, likewise in each case based on the phosphorus-oxygen compound-containing material. The sum of iron and aluminum compounds is preferably 1.7 to 41.2 wt.%, calculated as the respective elemental metal.
[0021] The sewage sludge ash can usually contain other typical elements, calculated on the basis of the respective element, preferably:
[0022] Calcium from 4 to 38% by weight,
[0023] Potassium from 0 to 2 wt.%,
[0024] Magnesium from 0.1 to 4 wt.%,
[0025] Sodium from 0.1 to 4% by weight
[0026] Sulphur from 0 to 7 wt.%,
[0027] Silicon from 0 to 24 wt% and
[0028] Titanium from 0 to 2 wt%.
[0029] The elements together, calculated as oxides, preferably make up more than 70 wt.% of the sewage sludge ash.
[0030] The respective components can preferably be present as oxides, phosphates, or sulfates. The iron compound is preferably present as an iron(III) compound at 50-100 wt.%. Preferably, 80 wt.% or more of the phosphates are present as metal phosphates of aluminum, calcium, or iron. In addition, the sewage sludge ash may contain numerous other elements in minor amounts, primarily copper, zinc, lead, barium, and manganese. The silicon mentioned above is present primarily as sand, primarily from the filtration processes commonly used in sewage treatment plants.
[0031] The phosphorus-oxygen compound-containing material can, in a preferred form, consist of 100% of an iron phosphate compound or contain it only partially. The material used preferably contains the iron phosphate compounds in total with a content, calculated as elemental phosphorus, of 1 to 22 wt. %, preferably 10 to 21 wt. %, based on the phosphorus-oxygen compound-containing material. The preferred material used contains at least one iron phosphate compound selected from the group consisting of iron phosphates, in particular iron(II) phosphate, iron(III) phosphate and iron(III) pyrophosphate, lithium iron phosphate (LFP), lithium iron manganese phosphate (LFMP), in particular LFP and / or LFMP with the general common formula LiFe(II). x )Mn x PO4, where 0 <x<0,9, insbesondere 0<x<0,6 ist, oder Mischungen davon. Bevorzugt wird ein LFP- und / oder LFMP-haltiges Material, enthaltend vorzugsweise LiFe(i- x )Mn xPO4 of the above formula. As such, a material containing a proportion of 2 to 100 wt.%, preferably 40 to 99 wt.%, in particular 50 to 99 wt.%, particularly preferably 70 to 99 wt.% of LFP and / or LFMP is used for the process according to the invention. Preferably, the composition of the material used can also be described by determining the weight fraction of certain elements in the preferably LFP- and / or LFMP-containing material used, in each case based on the amount of material, wherein the material used preferably contains:
[0032] 1 to 36 wt.% Fe, preferably 0.4 to 20 wt.% calculated as elemental phosphorus, based on LFP and / or LFMP-containing material,
[0033] 0 to 35 wt% Mn, 1 to 8 wt% Li and
[0034] 1 to 55 wt.%, preferably 1 to 40 wt.%, in particular 1 to 30 wt.% carbon. These quantities of the elements can come from the LFP, the LFMP, but also from the remaining components of the material used, such as residues of metallic components.
[0035] The elemental components are preferably determined using classical methods for elemental analysis. The type and quantity of the iron phosphate compound present is preferably determined using the X-ray scattering (XRD) method on a powder in reflection using a Cu-K a Radiation is determined. The resulting reflections are compared with data from, for example, the ICDD (International Centre for Diffraction Data), and the resulting iron phosphate-containing phases are assigned.
[0036] For lithium iron phosphate, the reflections from JCPDS (International Centre for Powder Diffraction Data Sample) card #83-2092 are used for comparison. Preferably, the material used further contains 1 to 55 wt.%, preferably 1 to 40 wt.%, in particular 1 to 30 wt.% of carbon, in particular graphite and / or carbon black. The sum of LFP and / or LFMP and carbon in the preferably LFP and / or LFMP-containing material used is preferably more than 70 wt.%, preferably more than 80 wt.%, particularly preferably more than 90 wt. Typically, the LFP and / or LFPM-containing battery cells are mechanically disassembled as far as possible, and the remainder, containing the cathode and anode material, optionally binder, and other components, is comminuted to a mass that is black due to the dark LFP / LFMP and the graphite-containing anode material and is therefore called a "black mass."Due to technically incomplete separation, the black mass may also contain residues of other battery components, such as metals.
[0037] The phosphorus-oxygen compound-containing material can therefore also be the so-called black mass, with a proportion of phosphate compounds of 0.4 to 21 wt.% calculated as elemental phosphorus, based on the phosphorus-oxygen compound-containing material.
[0038] The material used may also contain metals, preferably from 0 to 15 wt.%, preferably 0 to 5 wt.%, in particular Al, Cu, Co and Ni may be contained.
[0039] The aluminum content, determined as elemental aluminum, of the material used is preferably less than 10 wt.%, in particular less than 5 wt.%.
[0040] It is preferred that the material used preferably contains less than 10 wt.%, in particular less than 1 wt.%, particularly preferably less than 0.1 wt.% of polymer particles, in particular plastic such as polyethylene and / or polypropylene.
[0041] The preferred material containing LFP and / or LFMP is black mass from battery shredding.
[0042] The material or phosphorus-oxygen compound used preferably has an average particle size of 0.1 μm to 50 mm, preferably 0.5 to 10 mm. Depending on the size, the particle size can be determined simply by sieving or, for smaller particles, by laser diffraction or laser scattering. The most suitable method is known to the person skilled in the art. The material used, which preferably contains LFP and / or LFMP, can also be a coated material. Carbon, especially graphite, and metal oxides are preferred coating agents.
[0043] The water content of the phosphorus-oxygen compound or material used is preferably less than 5% by weight, in particular less than 1% by weight.
[0044] Proceedings
[0045] The conversion of the phosphorus-oxygen compound-containing material takes place in the presence of tetrachloroethylene. This can be used as such or in the form of its precursor chloroform, which releases HCl above 500°C and converts to tetrachloroethylene, or in the form of a mixture containing tetrachloroethylene and chloroform. Since the thermal conversion of chloroform to tetrachloroethylene is accompanied by the formation of HCl, which is useless for further reaction with phosphorus-oxygen compounds, tetrachloroethylene is preferred as the starting material, if available.
[0046] Optionally, the reaction can also be carried out in the presence of an inert gas. Examples of suitable inert gases include nitrogen, carbon dioxide, and / or argon. The tetrachloroethylene, which is optionally used together with chloroform and optionally a carrier gas, preferably contains an oxygen content of less than 0.1, in particular less than 0.05, percent by volume, based on the total of the gas stream containing these components. The preferred inert gas is preferably nitrogen, carbon dioxide, or argon.
[0047] Preferably, a weight ratio of the sum of tetrachloroethene and / or chloroform to inert gas of 1:0 to 1:6, preferably between 1:0 and 1:4, is used.
[0048] The conversion of the phosphorus-oxygen compound-containing material is preferably carried out in a fluidized-bed, packed-bed, or moving-bed reactor, in a shaft furnace, or in a furnace, which is most easily designed as an indirectly heated tube furnace or rotary kiln. The respective reactors are preferably gas-tight. Optionally, the material can be shaped before being introduced into a furnace, for example, by briquetting, extruding, or pelletizing. Auxiliary materials such as phyllosilicates, especially bentonites, as well as ligninsulfonate, methylcellulose, water glass, starch, or others can be used for this purpose.
[0049] The phosphorus-oxygen compound-containing material to be used in the process according to the invention is preferably introduced into a reactor, which is preferably provided with a layer resistant to the reaction conditions to be established. Preferred reactor materials are nickel- or graphite-coated reactors. Particular preference is given to reactors that allow movement of the material during the reaction, in order to allow the most effective contact of the reactants and heat distribution. Preferred reactors are fluidized-bed reactors, rotary tube reactors, or a reaction in an extruder with screw propulsion.
[0050] In the case of a tubular reactor, the reactor length is preferably 0.2 to 40 m. The residence time in the reactor during the reaction generally depends on the temperature and the possibility of contact between the reactants. The process according to the invention can be operated batchwise or continuously. A gas stream of tetrachloroethylene and / or chloroform, optionally diluted by an inert carrier gas stream, is preferably passed through the reactor and over the phosphorus-oxygen compounds or over the material containing them, while simultaneously maintaining the reaction temperature at 500 to 1000°C, preferably at 600 to 900°C, in particular at 700 to 850°C. The reaction time can be between a few minutes and 10 hours, preferably between 20 minutes and 5 hours.
[0051] Preferably, 0.75 to 4 mol of tetrachloroethene or 1 to 4.5 mol of chloroform are used per mol of phosphorus of the phosphorus-oxygen compound-containing material.
[0052] The products formed during the reaction, which may be volatile at the reaction temperature, in these examples mainly phosphoryl chloride, iron chloride, but also aluminum chloride and possibly other heavy metal chlorides such as zinc chloride or chlorides from the rare earth group, are preferably resublimated from the exhaust gas stream at different cool points and collected separately.
[0053] Preferred deposition temperatures for FeCh are less than 701°C, in particular less than 700°C to 307°C, for FeCh less than or equal to 307°C, in particular 150°C to 300°C and for AlCh less than or equal to 150°C, in particular 110°C to 149°C.
[0054] Phosphoryl chloride is preferably collected in a condenser at preferably less than 110°C.
[0055] Both the sublimate and the residue are essentially water-soluble and can preferably be further separated and isolated from their aqueous solutions, for example, after determining their possible existence according to the classical H2S separation process, they can be separated and isolated from each other in the form of their sulfides, chlorides, phosphates, fluorides or other precipitated compounds.
[0056] Examples
[0057] Analytics
[0058] The analysis was carried out in an ICP-OES after dissolving the calcium phosphate sample used in suitable acids, after calibration for the respective element using calibrated standard solutions of the respective elements.
[0059] Example 1
[0060] 10 g of technical-grade calcium phosphate (obtained from sewage sludge ash processing) containing (in wt.%) Ca: 35%, PO4: 52%, Fe: 0.14%, and Al: 0.48%, each determined by ICP-OES, are introduced into a quartz reactor (120 mm diameter) placed in a tube furnace. The reactor is heated to 150°C.
[0061] Tetrachloroethylene at a rate of 0.2 ml / min is evaporated in a total evaporator and mixed with a nitrogen flow of 1 l / min at 150°C. The tetrachloroethylene and nitrogen mixture enters the quartz reactor, which is heated to 150°C to prevent condensation of the reactant, and passes over the calcium phosphate. The gaseous reaction products leave the reactor as an off-gas stream, which is cooled to 100°C and passed through a gas cell with optical windows through which an infrared spectrum of the gas phase is recorded. Heating during this phase of the reaction serves solely to prevent condensation of reactants and products.
[0062] The solid is heated to 780°C in the reactor and gas stream within 2 hours, while the exiting exhaust gas stream is continuously monitored by recording IR spectra.
[0063] It is also possible to heat the sample to 780°C before adding tetrachloroethylene.
[0064] From a temperature of 750°C, the conversion to POCI3 begins to become rapid, which is characterized by the bands in the IR (observed: 592cm -1 (P-Cl), 1322cm -1 (P=O), Literature: 590cm -1 and 1322 cm -1 (±6cm -1 ), Shimanouchi, T., Tables of Molecular Vibrational Frequencies Consolidated Volume II, J. Phys. Chem. Ref. Data, 1972, 6, 3, 993-1102.).
[0065] The POCI3 is collected in a capacitor.
[0066] At the end of the reaction, 13.2 g of a solid colored black by adhering soot traces is obtained, consisting essentially of CaCl and partially molten. This solid reaction product can be dissolved in water and used for other purposes, such as phosphate precipitation in wastewater treatment plants. Example 2
[0067] 50 g of technical-grade calcium phosphate (obtained from sewage sludge ash processing) containing (in wt%) Ca: 35%, PO4: 52%, Fe: 0.14%, and Al: 0.48%, each determined by ICP-OES, are introduced into a quartz reactor (120 mm diameter) placed in a tube furnace. The reactor is heated to 150°C.
[0068] Chloroform is evaporated at 0.2 ml / min in a total evaporator and mixed with a nitrogen flow of 1 l / min at 100°C. The chloroform and nitrogen mixture enters the quartz reactor, which is heated to 150°C to prevent condensation of the reactant, and passes over the calcium phosphate. The gaseous reaction products leave the reactor, are cooled to 100°C, and are passed through a gas cell with optical windows through which an infrared spectrum of the gas phase is recorded. Heating during this phase of the reaction serves solely to prevent condensation of reactants and products.
[0069] The solid is heated to 780°C in the reactor and gas stream within 2 hours, while the exiting exhaust gas stream is continuously monitored by recording IR spectra.
[0070] It is also possible to heat the sample to 780°C before adding chloroform.
[0071] Above a temperature of 500°C, chloroform decomposes into HCl and tetrachloroethylene.
[0072] Above 600°C, the resulting tetrachloroethylene reacts with the calcium phosphate initially introduced into the reaction mixture to form calcium chloride and phosphoryl chloride. The POCl3 is collected in a condenser. The latter can be identified by characteristic bands in the infrared spectrum. Above 750°C, the reaction reaches a rate at which significant conversion rates are achieved. The reaction is terminated 20 minutes after reaching the target temperature of 780°C.
Claims
1. A process for the preparation of phosphorus-chlorine compounds, characterized in that i. a material containing a phosphorus-oxygen compound is reacted in the presence of tetrachloroethene at a temperature of 500 to 1000°C and ii. the phosphorus-chlorine compounds formed, in particular phosphorus oxychloride, are removed and isolated in the exhaust gas stream.
2. A process for the preparation of phosphorus-chlorine compounds according to claim 1, characterized in that the reaction takes place at a temperature of 600 to 900°C, in particular at 700 to 850°C.
3. A process for the preparation of phosphorus-chlorine compounds according to at least one of claims 1 to 2, characterized in that the phosphorus-chlorine compound is phosphorus oxychloride.
4. A process for the preparation of phosphorus-chlorine compounds according to at least one of claims 1 to 3, characterized in that the phosphorus-oxygen compound-containing material contains at least one phosphorus-oxygen compound selected from the group of phosphates, in particular calcium phosphates, apatites, in particular chloroapatites or hydroxyapatites, sodium phosphates, iron phosphates, aluminum phosphates, lithium iron phosphates, in particular lithium iron phosphate or lithium iron manganese phosphate or phosphinic acids, phosphoric acids, their respective polyacids or anhydrides or mixtures thereof.
5. A process for the preparation of phosphorus-chlorine compounds according to at least one of claims 1 to 4, characterized in that the phosphorus-oxygen compound-containing material contains at least one inorganic phosphate, in particular the corresponding orthophosphates or metaphosphates or polyphosphates or mixtures thereof.
6. A process for the preparation of phosphorus-chlorine compounds according to at least one of claims 1 to 5, characterized in that the phosphorus-oxygen compound-containing material contains calcium phosphate, particularly preferably calcium orthophosphate, calcium metaphosphate and / or calcium hydroxylapatite.
7. A process for the preparation of phosphorus-chlorine compounds according to at least one of claims 1 to 6, characterized in that the phosphorus-oxygen compound-containing material contains at least one phosphorus-oxygen compound with a content, calculated as elemental phosphorus, of 1 to 44 wt.%, preferably of 1 to 30 wt.%, in particular of 5 to 28 wt.%, based on the phosphorus-oxygen compound-containing material.
8. A process for the preparation of phosphorus-chlorine compounds according to at least one of claims 1 to 7, characterized in that the phosphorus-oxygen compound-containing material is sewage sludge ash or a black mass containing iron phosphates.
9. A process for the preparation of phosphorus-chlorine compounds according to at least one of claims 1 to 8, characterized in that the phosphorus-oxygen compound-containing material has an average particle size of 0.1 pm to 50 mm, preferably of 0.5 to 10 mm.
10. A process for the preparation of phosphorus-chlorine compounds according to at least one of claims 1 to 9, characterized in that tetrachloroethene and / or chloroform, optionally with an inert gas, is used for the reaction of the phosphorus-oxygen compound-containing material.
11. A process for the preparation of phosphorus-chlorine compounds according to at least one of claims 1 to 10, characterized in that phosphoryl chloride is derived from the exhaust gas stream and separated by condensation, preferably at less than 110°C.
Citation Information
Patent Citations
Process of producing phosphorus pentoxide
US1606319A
Process of producing phosphorus chloride from phosphate rocs
US1730521A
Process for manufacturing phosphorus oxychloride
US3927179A
