Patent Application
20230182068
This invention relates to compositions and methods of selective and fast ammonia removal in ammonia-contaminated liquid and gas streams.
Ammonia-contaminated liquid and gas streams are generated by industrial sectors such as municipal wastewater treatments, landfills, petroleum refineries, and concentrated animal feeding operations. If discharged to the environment without treatment, these contaminated streams contribute to water and air pollution.
Ammonia in contaminated liquid streams is most commonly removed by the biological nutrient removal (BNR) process. The prior arts, for example, US EPA's Municipal Nutrient Removal Technologies Reference Document, Volume 1—Technical Report (EPA 832-R-08-006, September 2008); Biological Nutrient Removal (BNR) Operation in Wastewater Treatment Plants—MOP 29 (Water Environment Federation and the American Society of Civil Engineers. Alexandria, Va.: WEF Press), teaches that many configurations of BNR processes are practiced by the municipal wastewater treatment plant to remove ammonia. Biological processes are inherently slow and temperature-dependent, and therefore are expensive to build, maintain and operate. Less commonly, ammonia may be removed from the liquid stream by chemical and physical treatment. U.S. Pat. No. 8,939,676 (Eden, et al) and U.S. Pat. No. 10,266,423 (Theodoulou, et al) teach methods of air stripping at high pH to remove ammonia from contaminated liquid streams and recover free ammonia or ammonium sulfate solution as products.
Ammonia in contaminated gas streams may be removed by absorption in acid solutions or thermal destruction. U.S. Pat. No. 9,108,164 teaches a process to capture ammonia from an ammonia-contaminated gas stream using acid to form ammonium salt, but it is challenging to market or dispose of the byproducts. The methods of thermal destruction have the disadvantage of potentially creating secondary pollution problems.
Despite the existence of many prior arts for ammonia removal in the liquid and gas streams, there remains a need for treatment methods that overcome the limitations of prior arts.
Accordingly, this invention discloses new compositions and methods of selective and fast ammonia removal in ammonia-contaminated liquid and gas streams. The invention is based on the newly discovered reaction between water-soluble phosphonium compounds and ammonia which lead to the formation of covalent compounds. The reaction may be carried out at ambient conditions with the reaction reaching completion in 10 minutes or less.
In accordance with one or more aspects, the disclosed compositions may be water-soluble tetrakis(hydroxymethyl) phosphonium (THP) salts of, including but are not limited to, borate, carboxylates, halides, sulfate, and sulfonates; wherein said carboxylates may be linear or branched; wherein said halides may include bromide, chloride, fluoride, and iodide; wherein said sulfonates may comprise linear or branched, monomeric or polymeric sulfonates
According to at least one embodiment, the THP salts may be concentrated or dilute aqueous solutions. THP salts may be dosed to liquid waste stream at a molar ratio to ammonia in the range of 1:1 and 1:2. The pH of the waste stream may be adjusted to a range between 5 and 11, more preferably between 5.5 and 10, most preferably between 6.5 and 9, using pH elevating compounds. The pH elevating compounds may be a water-soluble base, such as sodium hydroxide and potassium hydroxide. In yet another embodiment, the pH elevating compounds may be water-insoluble bases such as calcium hydroxide and magnesium hydroxide. In yet another embodiment, the water-soluble bases and water-insoluble bases may be combined for pH adjustment.
In accordance with one or more aspects, a gas stream contaminated with ammonia may be directed to come in contact with a concentrated or dilute aqueous solution of THP salts. The absorbed ammonia reacts with THP salts to form insoluble compounds when a certain threshold of pH is reached.
In accordance with one or more aspects, the THP salts may be impregnated into solid substrates to form solid scavengers. The solid substrates may comprise any chemically compatible substrates, including but are not limited to, zeolite, perlite, activated carbon, glass fiber, silica, clay, synthetic fibers, and biobased substrates. Solid scavengers may be packed in a packed-bed scrubbing system. The ammonia-contaminated gas stream may be passed through the packed-bed system for treatment.
One or more embodiments relate generally to new compositions and methods of ammonia removal in contaminated liquid and gas streams. For illustration purposes, liquid streams and gas streams generated in wastewater treatment plants from the anaerobic digestion process are used as examples.
The municipal wastewater treatment plants (WWTP) represent one of the largest point sources of ammonia discharge. To meet the effluent limits for nitrogen nutrients, the technology of choice for WWTPs is predominantly the biological nutrient removal (BNR) process. The BNR processes are operated based on the key design criteria, solid retention time (SRT). SRT is typically maintained at 3-5 days for nitrification at summer temperature of 20° C. and doubled to 6-10 days at winter temperature of 10° C. Long SRT translates into a large reactor size, hence high capital cost.
In a typical WWTP, a side stream is generated from its anaerobic digestion process. This side stream contains high levels of ammonia-N, typically in the range of 600-1200 mg/l, which contributes to as much as 20-40% nitrogen load to the BNR process even though it only accounts for a fraction of the total plant flow. There has been considerable interest in the industry to treat side streams separately to reduce their impact on mainstream BNR. Several biological methods have been developed to treat side streams separately, but like mainstream BNR, these biological methods require long SRT.
The inventor has discovered a new ammonia treatment process that is substantially faster than the biological treatment process. One or more embodiments relate generally to the reaction between ammonia and water-soluble phosphonium salts. The water-soluble phosphonium may be tetrakis(hydroxymethyl)phosphonium (THP) salts of, including but not limited to, borate, carboxylates, halides, sulfate, and sulfonates; wherein said carboxylates may be linear or branched; wherein said halides may include bromide, chloride, fluoride, and iodide; wherein said sulfonates may comprise linear or branched, monomeric or polymeric sulfonates. For example, tetrakis(hydroxymethyl) phosphonium chloride (THPC) and tetrakis(hydroxymethyl) phosphonium sulfate (THPS) are commercially available in concentrated form as 80% aqueous solution. The concentrated form may be used with or without dilution.
Ammonia concentration in the side stream from the dewatering process of anaerobically digested sludge may be measured following standard methods. To a known volume of the side stream, the dose required for THPC or THPS at a stoichiometric ratio to ammonia is added. Strong bases such as sodium hydroxide and potassium hydroxide, are commercially available in concentrated form, such as 40-50%, may be used with or without dilution, and may be added to the waste stream to elevate the pH. The pH may be adjusted to a range of 5-11, more preferably to a range of 5.5-10, most preferably to a range of 6-9. An aliquot of samples may be drawn at different time intervals, such as every 5 minutes, and ammonia concentration is measured after filtering the sample. As shown in
The reaction between ammonia and THPC leads to the formation of insoluble compounds. Without wishing to be bound by any particular theory, it is believed that the reaction follows the mechanism of a modified Mannich reaction which leads to the formation of a short-chain polymer or oligomer.
In accordance with one or more embodiments, solid products may be either returned to the mainstream or optionally separated by centrifuge, decantation, or filtration. The recovered product may be dried and beneficially reused.
In accordance with one or more embodiments, the treatment products may be recovered as fertilizer. The side stream from anaerobically digested sludge contains phosphorous in addition to ammonia. The synergistic treatment of ammonia and phosphorous may be advantageously carried out in one single process using calcium hydroxide or magnesium hydroxide, either alone or in combination with a water-soluble base. Macronutrient analysis of the recovered product showed a similar level of nitrogen and phosphorous nutrients to other commercially recovered struvite products which are marketed as slow-release fertilizer (Table 1).
In accordance with one or more embodiments, a gas stream contaminated with ammonia may be passed through aqueous solutions of THP salts to afford the ammonia capture. In an experiment that simulates the air stripping of ammonia from liquid, a laboratory apparatus was set up as shown in
In accordance with one or more aspects, the THP salts may be impregnated into solid substrates to form solid scavengers. The solid substrates may comprise any chemically compatible substrates, including but are not limited to, zeolite, perlite, activated carbon, glass fiber, silica, clay, synthetic fibers, and biobased substrates. Solid scavengers may be packed in a packed-bed scrubbing system. The ammonia-contaminated gas stream may be passed through the packed-bed system for treatment.
A side stream sample is taken from a wastewater treatment plant, and the ammonia concentration is measured to be 1800 mg/L as expressed by N—NH3. To a 100 ml centrate sample under agitation, 1 ml of an 80% THPC compound (density 1.3 g/rip is added, followed by the addition of 10N NaOH (40%) to raise the pH to above 7. Allow the reaction to continue for 10 minutes. Solid is separated from liquid with a centrifuge, dried, and weighed.
10 ml 60% magnesium hydroxide slurry is combined with 60 ml 10N NaOH and completely dispersed under agitation. To 1000 ml centrate obtained from a wastewater treatment plant, 10 ml above mixture of the base are added, followed by addition of 10 ml THPC. The reaction mixture is continuously mixed for 30 minutes and allowed sufficient time to settle the solids. The supernatant is decanted and the remaining thickened solid is filtered through a 4.7-micron glass fiber filter and dried in an oven.
0.2 g recovered product is weighed and charged into 100 ml DI water, homogenized in a blender, and diluted to a final volume of 500 ml. The dispersed solid is analyzed for TKN and TP. The analysis for TKN and TP follows standard methods of SM 4500 N Org C and SM 4600 P E.
The analysis of bioavailable P follows AOAC method 963.03 in which 0.5 g of recovered solid is extracted with 50 ml ammonium citrate solution at 65° C. for one hour. The ammonium citrate solution is made by dissolving 37 g citrate acid in 150 ml DI water, followed by the addition of 40 ml concentrated ammonia (37%). As a control, a commercially available struvite product is obtained and analyzed by following the same procedure (Table 1).
While particular embodiments of the compositions and methods for the ammonia removal in liquid and gas streams have been shown and described, it will be appreciated by those skilled in the art that changes, and modifications may be made without departing from the inventions in their broader aspects and as outlined in the following claims.
