Device for Removing Nitrogen and Carbon Using Microporous Aerated Biofilms
US-2022242764-A1 · Aug 4, 2022 · US
US9422179B2 · US · B2
| Field | Value |
|---|---|
| Publication number | US-9422179-B2 |
| Application number | US-201414290397-A |
| Country | US |
| Kind code | B2 |
| Filing date | May 29, 2014 |
| Priority date | May 30, 2013 |
| Publication date | Aug 23, 2016 |
| Grant date | Aug 23, 2016 |
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Procedure using zeolite, clinoptilolite type in an upflow anaerobic reactor and sludge blanket (UASBs) in order to obtain granular active sludge, thereby improving the density of the sludge, and thereby, their settling properties, and increase of biomass within reactor by immobilizing microorganisms, to achieve an increase in the efficiency of the removal of organic material and the production of biogas (60-70% methane) in more than 20% over the same type reactor used so far without zeolite, enabling the use of such reactor for treating wastewater with a high concentration of proteins, amino acids and other nitrogen compounds and which prevents the accumulation of nitrogen, which is toxic to the process by allowing zeolite-clinoptilolite, the exchange with alkali and alkaline earth found in specific points of the crystal structure of clinoptilolite by ammonia nitrogen, and also preventing the development of filamentous bacteria, which are difficult to hold up within the reactor and reduces its efficiency.
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The invention claimed is: 1. A process for anaerobic digestion of wastewater with a concentration of ammonia nitrogen, organic nitrogen, or proteins, in an upflow anaerobic digester and sludge blanket (UASB), with immobilization of microorganisms and inhibition controlled ammonium, the process comprising steps of: a) inoculating digested sludge wastewater with a concentration of nitrogen or of proteins that are contained in the digester; b) adding to residual inoculated wastewater from step a), zeolite-clinoptilolite having an average particle size of 0.5-2 mm, in a percentage of 15 to 23% volume of zeolite based on the total volume of sludge; c) adding to granular activated sludge resulting from step b), increasing volumes of wastewater with a concentration of nitrogen or protein to reach predetermined operating conditions; d) monitoring the operation of the digester under predetermined operating conditions of step c), and quantify the removal of organic matter and ammonia nitrogen in an effluent of the digester, the concentration of nitrogen in the digester, biogas production in the digester and a methane concentration in the biogas; e) adding zeolite in an accumulation of granular activated sludge of the digester, to detect at least an increase in concentration of ammonium nitrogen in the effluent of the digester, a decrease in removal efficiency, a decrease in removal efficiency of organic material or a decrease in biogas production, keeping constant the volume of sludge in the digester, in a proportion of 20% based on the total volume of the digester; optionally f) removing excess sludge produced from the bottom of the digester, and subjecting the excess sludge to dehydration by using sunlight or an alternative method such that a concentration material is obtained with nutrients with a moisture concentration of 20-30%, which can be used as a biofertilizer or slow release fertilizer nutrients. 2. The process of claim 1 wherein the wastewater containing a concentration of ammonia nitrogen, organic nitrogen, or proteins are selected from agricultural wastewater or wastewater of the food industry. 3. The method of claim 1 wherein the wastewater with a concentration of ammonia nitrogen, organic nitrogen, or proteins of livestock origin are selected from wastewater generated in pig farming or wastewater from dairies. 4. The method of claim 1 wherein the concentration of ammonia nitrogen in the wastewater is greater than 1,000 mg/L. 5. The method of claim 2 wherein the concentration of ammonia nitrogen in the wastewater is greater than 1,000 mg/L. 6. The method of claim 3 wherein the concentration of ammonia nitrogen in the wastewater is greater than 1,000 mg/L.
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