WO2024254547A2 - Methods and systems for the electrocatalysis of municipal sludge and biosolids - Google Patents
Methods and systems for the electrocatalysis of municipal sludge and biosolids Download PDFInfo
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- WO2024254547A2 WO2024254547A2 PCT/US2024/033133 US2024033133W WO2024254547A2 WO 2024254547 A2 WO2024254547 A2 WO 2024254547A2 US 2024033133 W US2024033133 W US 2024033133W WO 2024254547 A2 WO2024254547 A2 WO 2024254547A2
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- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/006—Electrochemical treatment, e.g. electro-oxidation or electro-osmosis
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- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
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- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/467—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
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- C25B9/00—Cells or assemblies of cells; Constructional parts of cells; Assemblies of constructional parts, e.g. electrode-diaphragm assemblies; Process-related cell features
- C25B9/17—Cells comprising dimensionally-stable non-movable electrodes; Assemblies of constructional parts thereof
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Definitions
- TITLE METHODS AND SYSTEMS FOR THE ELECTROCATALYSIS OF MUNICIPAL
- the present disclosure relates to an improved method and system for the electrolysis of biosolids, sludge, food waste, manure.
- the present disclosure relates to the electrocatalysis of sludge on transition metal based electrodes in order to produce synthetic nitrogen based fertilizer, phosphorus based fertilizer, and an electrolyzed solid organic fertilizer from waste activated sludge, manure from concentrated animal feeding operations, and food waste.
- Waste activated sludge is the major byproduct of municipal wastewater treatment plants. Management and disposal of waste activated sludge create challenges for wastewater treatment plants such as high energy consumption and operational costs.
- Waste activated sludge contains organic material like lignocellulosic waste that could be converted to produce high value chemicals such as volatile fatty acids. Accordingly, the leftover activated sludge is an organic-rich material with the high potential to produce value-added chemicals such as short chain fatty acids.
- Sludge in concentrated animal feeding operations such as lagoons, also contain nitrogen varying from 5 to 10% weight. Phosphorus is also present in these streams with most of the concentration in the solids.
- the present disclosure is directed to an improved method and system for the electrolysis of biosolids, sludge, food waste, manure.
- the method and system involve the electrocatalysis of sludge on transition based electrodes (such as for example, nickel (Ni), copper (Cu), iron (Fe), cobalt (Co), chromium (Cr), manganese (Mn), Scandium (Sc), etc.).
- transition based electrodes such as for example, nickel (Ni), copper (Cu), iron (Fe), cobalt (Co), chromium (Cr), manganese (Mn), Scandium (Sc), etc.
- transition based electrodes such as for example, nickel (Ni), copper (Cu), iron (Fe), cobalt (Co), chromium (Cr), manganese (Mn), Scandium (Sc), etc.
- transition based electrodes such as for example, nickel (Ni), copper (Cu), iron (Fe), cobalt (Co), chromium (
- the method can include selecting a sludge source.
- the method also can include preparing a slurry.
- the slurry can include the sludge source and an electrolyte.
- the method also can include adjusting a pH of the slurry.
- the adjusting the pH of the slurry can result in the slurry having an adjusted pH in a range between approximately 8 and 14.
- the method also can include flowing the slurry through an electrochemical cell.
- the electrochemical cell can include an anode, a cathode, and a catalyst.
- the method also can include applying a potential between the anode and the cathode. Applying the potential can include oscillating a cell voltage between the anode and the cathode at an oscillation frequency.
- the method also can include, resultant to the applying the potential, breaking down carbon bonds in the slurry with nitrogen and phosphorus.
- the method also can include releasing inorganic nitrogen and inorganic phosphorus.
- the method also can include obtaining an electrolyzed sludge.
- the electrolyzed sludge can include an electrolyzed solid organic fertilizer comprising nitrogen and phosphorus.
- the method can also include the introduction of a separator or membrane between the two electrodes.
- FIG. 1 depicts a process for the electrolysis of sludge for the production of nitrogen based fertilizer and phosphorus based fertilizer with an organic fertilizer/carbon sink, in accordance with certain embodiments of the present disclosure.
- FIG. 2 depicts a system for the electrolysis of sludge for the production of nitrogen based fertilizer and phosphorus based fertilizer, in accordance with certain embodiments of the present disclosure.
- the present disclosure relates to an improved method and system for the electrolysis of biosolids, sludge, food waste, manure.
- the present disclosure relates to the electrocatalysis of sludge on transition based electrodes in order to produce synthetic nitrogen based fertilizer and phosphorus based fertilizer from waste activated sludge and concentrated animal feeding operations.
- FIG. 1 depicts a process for the electrolysis of sludge for the production of nitrogen based fertilizer and phosphorus based fertilizer with an organic fertilizer/carbon sink, in accordance with certain embodiments of the present disclosure.
- FIG. 2 depicts a system for the electrolysis of sludge for the production of nitrogen based fertilizer and phosphorus based fertilizer, in accordance with certain embodiments of the present disclosure.
- the present disclosure relates to a method and system for the electrolysis of biosolids, sludge, food waste, manure.
- the process as shown in FIG. 1, the process may transform municipal sludge, manure, concentrated animal feeding operations sludge, and food waste into nitrogen based fertilizer, phosphorus based fertilizer, ammonia, slow-release organic fertilizer, and carbon sink char.
- the process of FIG. 1 provides the conversion and valorization of municipal and concentrated animal feeding operations sludge into value products such as ammonia, low-release organic fertilizer, phosphorus, and soil enhancement nutrient with the ability to serve as a carbon sink.
- the process may result in the products of inorganic nitrogen-based fertilizer, inorganic phosphorus based fertilizer, fatty acids, hydrogen, and organic N-P fertilizer.
- the inorganic nitrogen-based fertilizer may be ammonia, ammonium salts, calcium nitrate, or combinations thereof.
- the inorganic phosphorus- based fertilizer may be one or more calcium phosphates.
- the slow-release organic fertilizer may be or include electrolyzed biosolids.
- the fertilizer may contain consistent nitrogen and phosphorus content and a microstructure to enhance plant growth due to slow release of nitrogen increasing nutrient use efficiency.
- the method and system for the electrolysis can include carbon sink material, since electrolyzed biosolids, such as those in a slow- release organic fertilizer, have the property to absorb carbon dioxide.
- the process may begin with the introduction of sludge.
- the sludge may be sewage.
- the sludge may be manure.
- the sludge may be a combination of one or more of municipal sludge, manure, concentrated animal feeding operations sludge, and food waste.
- the process may continue with the preparation of a slurry.
- the slurry can include the sludge and an electrolyte.
- the sludge may include between approximately 0.5 percent and 40 percent solids as a mass percentage of solute in the solution.
- the process may involve, in certain embodiments, the adjustment of the pH of the slurry.
- the pH of the slurry may be adjusted between 8 and 14 using potassium hydroxide (KOH), sodium hydroxide (NaOH), calcium oxide (CaO), or other equivalent salt. These salts can also serve as electrolyte in the slurry. Operating the process at higher pH values is feasible but the range provided presents an economic advantage.
- the process can include flowing the slurry through an electrochemical cell containing two electrodes, an anode and cathode.
- the electrochemical cell can also include a membrane or separator.
- the addition of separator allows the separation of hydrogen gas that can evolve under certain applied voltages.
- the electrochemical cell can contain an anode, a cathode, a membrane or separator for collecting hydrogen, an electrolyte, and a reference electrode.
- the anode may include a conductive material, support, such as for example but not limited to, (Ni) gauze/mesh, stainless steel, Hastelloy, graphite, nickel (Ni), nickel (Ni) foam, copper (Cu), cobalt (Co), chromium (Cr), zinc (Zn), titanium (Ti), titanium (Ti) foam, aluminum (Al), aluminum (Al) foam, vanadium (V), manganese (Mn), Scandium (Sc), Ruthenium (Ru), Rhodium (Rh), Iron (Fe), Silver (Ag), Gold (Au), or combinations thereof.
- a conductive material support, such as for example but not limited to, (Ni) gauze/mesh, stainless steel, Hastelloy, graphite, nickel (Ni), nickel (Ni) foam, copper (Cu), cobalt (Co), chromium (Cr), zinc (Zn), titanium (Ti), titanium (Ti) foam, aluminum (Al), aluminum (Al) foam
- the anode may include any conductive material that is resistant to corrosion based on the electrolyte, cell voltage and temperature of the system.
- the supports can include carbon, carbon fibers, graphene.
- the anode may include a catalyst that includes metals such as nickel (Ni), iron (Fe), cobalt (Co), chromium (Cr), copper (Cu), zinc (Zn), ruthenium (Ru), rhodium (Rh), vanadium (V), manganese (Mn), titanium (Ti), Scandium (Sc) and combinations thereof.
- the catalyst may include composites of graphene metal combinations.
- the catalyst may have loadings 0.1 mg/cm 2 to 2 mg/cm 2
- the catalysts can also be used as a direct metal or support in certain embodiments.
- the cathode may include a conductive material, support, such as for example but not limited to, nickel (Ni) gauze/mesh, stainless steel, Hastelloy, graphite, nickel (Ni), nickel (Ni) foam, copper (Cu), cobalt (Co), chromium (Cr), zinc (Zn), titanium (Ti), titanium (Ti) foam, aluminum (Al), aluminum (Al) foam, vanadium (V), manganese (Mn), Scandium (Sc), Ruthenium (Ru), Rhodium (Rh), Iron (Fe), Silver (Ag), Gold (Au), or combinations thereof.
- a conductive material support, such as for example but not limited to, nickel (Ni) gauze/mesh, stainless steel, Hastelloy, graphite, nickel (Ni), nickel (Ni) foam, copper (Cu), cobalt (Co), chromium (Cr), zinc (Zn), titanium (Ti), titanium (Ti) foam, aluminum (Al), aluminum (A
- the anode may include any conductive material that is resistant to corrosion based on the electrolyte, cell voltage and temperature of the system.
- the supports can include carbon, carbon fibers, graphene.
- the anode may include a catalyst that includes metals such as nickel (Ni), iron (Fe), cobalt (Co), chromium (Cr), copper (Cu), zinc (Zn), ruthenium (Ru), rhodium (Rh), vanadium (V), manganese (Mn), titanium (Ti), Scandium (Sc) and combinations thereof.
- the catalyst may include composites of graphene metal combinations.
- the catalyst may have loadings 0.1 mg/cm 2 to 2 mg/cm 2
- the catalysts can also be used as a direct metal or support in certain embodiments.
- a membrane and/or a separator may be included in the electrochemical cell.
- the electrochemical cell may contain a membrane such as for example but not limited to nafion, fritted glass, and/or separators, such as for example but not limited to polyethylene.
- the electrolyte may have a strong and weak basis.
- the electrolyte may include potassium hydroxide (KOH), sodium hydroxide (NaOH), calcium oxide (CaO), or combinations thereof.
- KOH potassium hydroxide
- NaOH sodium hydroxide
- CaO calcium oxide
- the electrolyte may be present at concentrations such that pH is maintained between approximately 8 and 14.
- the process also can include applying an oscillation of potential between the two electrodes.
- the cell voltage can be applied between the anode and the cathode of the cell.
- a current is applied instead of a voltage.
- the voltage can be oscillated with a frequency of 1, 10, 30, 60 seconds and 15, 30 minutes.
- the effective cell voltage may be up to 2.0V (discounted by the ohmic resistance, counters, wires, etc.), depending on the type of electrolyte used and the temperature.
- the cell voltage for the electrochemical cell may vary from 0.8V to 2.0V excluding the ohmic resistance.
- the cell voltage applied can prevent water oxidation at the anode of the cell, and the oxidation potential is a function of the electrolyte and temperature used.
- the temperature is controlled.
- the temperature may be controlled between approximately 20 °C to 80 °C.
- the applied potential breaks down carbon bonds with nitrogen and phosphorus.
- the process can include releasing the nitrogen and phosphorus as inorganic phosphorus and nitrogen.
- inorganic phosphorus may include phosphates.
- inorganic nitrogen may be ammonia, nitrates, or combinations thereof.
- the product of the process may include an electrolyzed solid containing a fraction of nitrogen and phosphorus in organic form which can be applied as an organic fertilizer.
- the microstructure of the electrolyzed sludge may, in some embodiments, serve as a sink for the absorption of carbon dioxide (CCh) from the atmosphere.
- the process of FIG. 1 may reduce the time for producing organic fertilizer.
- the fertilizer may include carbon, nitrogen, and phosphorus.
- biological process takes 30 to 45 days to digest organic waste into fertilizer.
- sludge electrolysis reduces the digestion time to less than six hours.
- Residence time for conversion for the process of FIG. 1 may be two hours. This residence time for conversion in the process of FIG. 1 is significantly lower than processes using anaerobic digesters, which typically take approximately 10 to 20 days.
- the process of FIG. 1 can result in a reduction of 24.85 percent in total solids and 46.42 percent in volatile solids, which represents approximately a 25 percent reduction in sludge disposal cost when compared to conventional treatment methods.
- the process can result in the conversion of 68% of the organic nitrogen into inorganic nitrogen.
- a slow-release fertilizer (electrolyzed sludge) was produced using the process for the electrolysis of sludge for the production of nitrogen based fertilizer and phosphorus based fertilizer with an organic fertilizer/carbon sink.
- the electrolyzed sludge solids after electrolysis
- the microstructure of the material changed, creating surfaces with micro and nanoparticles. This material contained nitrogen and phosphorus in concentrations like compost.
- the microstructure change enabled a slow release of the fertilizer, creating an advantage in the soil.
- the change in the micro- structure can minimize the release of inorganic fertilizer when mixed in the soil with synthetic inorganic fertilizer.
- a carbon sink material, electrolyzed sludge was produced using the process for the electrolysis of sludge for the production of nitrogen based fertilizer and phosphorus based fertilizer with an organic fertilizer/carbon sink.
- the electrolyzed sludge released the volatile carbon. Because of the change in the microstructure, the product behaves similar to an activated carbon, enabling the absorption of carbon dioxide (CO2) and other contaminants.
- CO2 carbon dioxide
- the other contaminants may include methane, benzene, toluene, or combinations thereof.
- a method for electrocatalysis of sludge including selecting a sludge source; preparing a slurry, where the slurry includes the sludge source and an electrolyte; adjusting a pH of the slurry, where the adjusting the pH of the slurry results in the slurry having an adjusted pH in a range between approximately 8 and 14; flowing the slurry through an electrochemical cell, where the electrochemical cell includes an anode, a cathode, and a catalyst; applying a potential between the anode and the cathode, where applying the potential includes oscillating a cell voltage between the anode and the cathode at an oscillation frequency; resultant to the applying the potential, breaking down carbon bonds in the slurry with nitrogen and phosphorus; releasing inorganic nitrogen and inorganic phosphorus; and obtaining an electrolyzed sludge, where the electrolyzed sludge includes an electrolyzed solid comprising nitrogen and phosphorus.
- Clause 2 The method of any foregoing clause, where the sludge source includes one or more of municipal sludge, manure, concentrated animal feeding operations sludge, and food waste.
- Clause 3 The method of any foregoing clause, where the sludge source includes a solid in a mass percent in a range between approximate 0.5 and 40 percent.
- anode includes (Ni) gauze/mesh, stainless steel, Hastelloy, graphite, nickel (Ni), nickel (Ni) foam, copper (Cu), cobalt (Co), chromium (Cr), zinc (Zn), titanium (Ti), titanium (Ti) foam, aluminum (Al), aluminum (Al) foam, vanadium (V), manganese (Mn), Scandium (Sc), Ruthenium (Ru), Rhodium (Rh), Iron (Fe), Silver (Ag), Gold (Au), or combinations thereof.
- the cathode includes nickel (Ni) gauze/mesh, stainless steel, Hastelloy, graphite, nickel (Ni), nickel (Ni) foam, copper (Cu), cobalt (Co), chromium (Cr), zinc (Zn), titanium (Ti), titanium (Ti) foam, aluminum (Al), aluminum (Al) foam, vanadium (V), manganese (Mn), Scandium (Sc), Ruthenium (Ru), Rhodium (Rh), Iron (Fe), Silver (Ag), Gold (Au), or combinations thereof.
- Clause 23 A electrolyzed solid organic fertilizer including nitrogen, carbon, and phosphorus.
- Clause 24 The electrolyzed solid organic fertilizer of any foregoing clause, where the electrolyzed solid organic fertilizer promotes a nitrogen circular economy.
- Clause 25 The electrolyzed solid organic fertilizer of any foregoing clause, where the electrolyzed solid organic fertilizer facilitates reduced runoff.
- Amounts and other numerical data may be presented herein in a range format. It is to be understood that such range format is used merely for convenience and brevity and should be interpreted flexibly to include not only the numerical values explicitly recited as the limits of the range, but also to include all the individual numerical values or sub-ranges encompassed within that range as if each numerical value and sub-range is explicitly recited. For example, a numerical range of approximately 1 to approximately 4.5 should be interpreted to include not only the explicitly recited limits of 1 to approximately 4.5, but also to include individual numerals such as 2, 3, 4, and sub-ranges such as 1 to 3, 2 to 4, etc.
- the phrase “A, B, C, and/or D” includes A, B, C, and D individually, but also includes any and all combinations and subcombinations of A, B, C, and D.
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- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Electrochemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Materials Engineering (AREA)
- Metallurgy (AREA)
- Environmental & Geological Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- General Chemical & Material Sciences (AREA)
- Inorganic Chemistry (AREA)
- Treatment Of Sludge (AREA)
Abstract
Description
Claims
Priority Applications (6)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| AU2024283861A AU2024283861A1 (en) | 2023-06-07 | 2024-06-07 | Methods and systems for the electrocatalysis of municipal sludge and biosolids |
| CN202480051130.XA CN121666366A (en) | 2023-06-07 | 2024-06-07 | Method and system for electrocatalytic treatment of municipal sludge and biosolids |
| KR1020267000584A KR20260035891A (en) | 2023-06-07 | 2024-06-07 | Method and system for the electrocatalytic decomposition of municipal sewage sludge and biosolids |
| EP24820192.3A EP4724400A2 (en) | 2023-06-07 | 2024-06-07 | Methods and systems for the electrocatalysis of municipal sludge and biosolids |
| US18/909,776 US20250034018A1 (en) | 2023-06-07 | 2024-10-08 | Staged methods and systems for the valorization of sludge and biosolids |
| MX2025014787A MX2025014787A (en) | 2023-06-07 | 2025-12-08 | Methods and systems for the electrocatalysis of municipal sludge and biosolids |
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| Application Number | Priority Date | Filing Date | Title |
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| US202363506601P | 2023-06-07 | 2023-06-07 | |
| US63/506,601 | 2023-06-07 |
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| Application Number | Title | Priority Date | Filing Date |
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| US18/909,776 Continuation-In-Part US20250034018A1 (en) | 2023-06-07 | 2024-10-08 | Staged methods and systems for the valorization of sludge and biosolids |
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| Publication Number | Publication Date |
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| WO2024254547A2 true WO2024254547A2 (en) | 2024-12-12 |
| WO2024254547A3 WO2024254547A3 (en) | 2025-01-16 |
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| PCT/US2024/033133 Ceased WO2024254547A2 (en) | 2023-06-07 | 2024-06-07 | Methods and systems for the electrocatalysis of municipal sludge and biosolids |
Country Status (7)
| Country | Link |
|---|---|
| US (1) | US20250034018A1 (en) |
| EP (1) | EP4724400A2 (en) |
| KR (1) | KR20260035891A (en) |
| CN (1) | CN121666366A (en) |
| AU (1) | AU2024283861A1 (en) |
| MX (1) | MX2025014787A (en) |
| WO (1) | WO2024254547A2 (en) |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103395879A (en) * | 2013-07-31 | 2013-11-20 | 无锡柯马机械有限公司 | Aactive sludge electrocatalysis device |
| CN106542613A (en) * | 2016-10-09 | 2017-03-29 | 洛阳鼎威材料科技有限公司 | A kind of sewage disposal electro-catalysis anode material, and preparation method thereof |
| CN114230097A (en) * | 2021-12-18 | 2022-03-25 | 广州博睿水处理科技有限公司 | Treatment process of sewage containing organic phosphorus |
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2024
- 2024-06-07 EP EP24820192.3A patent/EP4724400A2/en active Pending
- 2024-06-07 AU AU2024283861A patent/AU2024283861A1/en active Pending
- 2024-06-07 CN CN202480051130.XA patent/CN121666366A/en active Pending
- 2024-06-07 WO PCT/US2024/033133 patent/WO2024254547A2/en not_active Ceased
- 2024-06-07 KR KR1020267000584A patent/KR20260035891A/en active Pending
- 2024-10-08 US US18/909,776 patent/US20250034018A1/en active Pending
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| Publication number | Publication date |
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| KR20260035891A (en) | 2026-03-13 |
| US20250034018A1 (en) | 2025-01-30 |
| CN121666366A (en) | 2026-03-13 |
| WO2024254547A3 (en) | 2025-01-16 |
| EP4724400A2 (en) | 2026-04-15 |
| AU2024283861A1 (en) | 2026-01-15 |
| MX2025014787A (en) | 2026-03-02 |
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