Reactors and methods for producing and recovering extracellular metal or metalloid nanoparticles
US-2019194040-A1 · Jun 27, 2019 · US
US2016257582A1 · US · A1
| Field | Value |
|---|---|
| Publication number | US-2016257582-A1 |
| Application number | US-201415023906-A |
| Country | US |
| Kind code | A1 |
| Filing date | Sep 23, 2014 |
| Priority date | Sep 26, 2013 |
| Publication date | Sep 8, 2016 |
| Grant date | — |
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Embodiments herein relate to methods for sludge reduction for pretreatment of nitrotoluene wastewater using electro-catalytic redox. The embodiments may include (a) adjusting a pH of the nitrotoluene wastewater to 1.5 to 2.0, standing for precipitation, draining sludge of the nitrotoluene wastewater at the bottom, obtaining supernatant of nitrotoluene wastewater, placing the supernatant through a cathode inlet into a cathode chamber of an electrochemical reactor; (b) performing electrochemical treatment, wherein reduction reaction of the supernatant of the nitrotoluene wastewater takes place at the cathode chamber, the nitrotoluene wastewater is placed into the anode chamber for oxidation reaction through the cathode outlet, the catholyte tank, and the anode inlet in sequence; (c) adjusting the nitrotoluene wastewater treated in step (b) via the anolyte tank, and then discharging the nitrotoluene wastewater into a biochemical system. The embodiments reduce toxicity of mixed acid nitration wastewater and therefore improve its biodegradability.
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What is claimed is: 1 . A method for sludge reduction for pretreatment of nitrotoluene wastewater using electro-catalytic redox, the method comprising: (a) adjusting a pH of the nitrotoluene wastewater to 1.5 to 2.0, standing for precipitation, draining sludge of the nitrotoluene wastewater at bottom, obtaining supernatant of nitrotoluene wastewater, and placing the supernatant through a cathode inlet into a cathode chamber of an electrochemical reactor, wherein: the electrochemical reactor comprising an anode chamber, the cathode chamber, an anode, a cathode, a catholyte tank, a cation exchange membrane, an anolyte tank and flow meters, the anode chamber and the cathode chamber are separated by the cation exchange membrane, the anode and the cathode are located in the anode chamber and a cathode chamber, respectively, the cathode chamber comprises the cathode inlet and a cathode outlet, the anode chamber comprises the anode outlet and the anode inlet, the cathode outlet and the catholyte tank are connected via a first channel, the catholyte tank is connected to the anode inlet via a second channel, the outlet of the anode is connected through a third channel with the anolyte tank, the flow meters comprise two flow meters, which are located at the first channel between the cathode outlet and the catholyte tank and at the third channel between the anode outlet and the anolyte tank, the cathode comprises a graphite plate, a titanium plate, a titanium plate loaded with ruthenium oxide or iridium oxide, and the anode is a titanium-based dimensionally stable electrode of which a coating comprises ruthenium oxide or iridium oxide; (b) performing electrochemical treatment, wherein: reduction reaction of the supernatant of the nitrotoluene wastewater takes place at the cathode chamber, the nitrotoluene wastewater is placed into the anode chamber for oxidation reaction through the cathode outlet, the catholyte tank, and the anode inlet in sequence, a current density of the anode and the cathode is about 5 to 50 mA/cm 2 , the nitrotoluene wastewater is placed in the cathode chamber and the anode chamber for about 1 to 6 h, and a distance between the anode and the cathode spacing is about 1.5 to 3 cm; and (c) adjusting the nitrotoluene wastewater treated in step (b) via the anolyte tank, and then discharging the nitrotoluene wastewater into a biochemical system. 2 . The method of claim 2 , wherein the adjusting the pH of the nitrotoluene wastewater to 1.5 to 2.0 and standing for precipitation comprises adjusting the pH of the nitrotoluene wastewater to 1.5 to 2.0 using sulfuric acid or industrial waste acid and standing for precipitation for about 0.5 to 2 hours. 3 . The method of claim 1 , wherein a volume of the catholyte tank is about 5 to 10 times of a volume of the cathode chamber. 4 . The method of claim 1 , wherein a volume of the anode tank is about 5 to 10 times of a volume of the anode chamber.
Electrodes comprising a substrate and a coating · CPC title
by neutralisation; pH adjustment (for degassing C02F1/20; using ion-exchange C02F1/42; for flocculation or precipitation of suspended impurities C02F1/52; for removing dissolved compounds C02F1/58) · CPC title
by electroreduction · CPC title
from the manufacture of organic compounds · CPC title
by electrooxydation · CPC title
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