Lysine fermentation waste water processing method, and method for preparing citric acid through fermentation
A technology of lysine fermentation and treatment method, which is applied in the field of fermenting citric acid, and can solve problems such as difficulty in treating high-concentration wastewater
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Embodiment 1
[0067] 1) At a temperature of 60°C, the lysine fermentation wastewater (protein content is 0.3% by weight, sulfate ion content is 2% by weight, ammonium ion content is 0.3% by weight) is pumped into G17 activated carbon (commercially purchased in Guangzhou Jinlin Environmental Protection Technology Co., Ltd., the same below) bed, the volumetric space velocity of the pump is 0.8m 3 / (m 3 h). The lysine fermentation wastewater that passed through the G17 activated carbon bed was separated into 1.6m 3 / (m 3 The volume space velocity of h) is introduced into the bed layer of D318 macroporous weakly basic acrylic anion exchange resin (commercially purchased from Suqing Water Treatment Engineering Group Co., Ltd., with an exchange capacity of 6.5mmol / g (dry)). Obtain the lysine fermentation wastewater after anion exchange (hereinafter referred to as the treated lysine fermentation wastewater), the protein content in the treated lysine fermentation wastewater is 0.35% by weight, a...
Embodiment 2
[0074] 1) At a temperature of 60°C, pump lysine fermentation waste water (with a protein content of 0.5% by weight, a sulfate ion content of 5% by weight, and an ammonium ion content of 1.0% by weight) into the G17 activated carbon bed, and pump it into Volumetric airspeed is 0.8m 3 / (m 3 h). The lysine fermentation waste water that passed through the G17 activated carbon bed was 2.1m 3 / (m 3 The volume space velocity of h) is introduced into the bed layer of D818 macroporous weakly basic styrene-based anion exchange resin (commercially purchased from Jiangsu Suqing Water Treatment Engineering Group Co., Ltd., with an exchange capacity of 6.5mmol / g (dry)). Obtain the lysine fermentation wastewater after anion exchange (hereinafter referred to as the lysine fermentation wastewater after treatment), the protein content in the lysine fermentation wastewater after the treatment is 0.55% by weight, the sulfate ion content is 0.03% by weight %, ammonium ion content is 1.1% by we...
Embodiment 3
[0081] 1) At a temperature of 60°C, pump lysine fermentation waste water (with a protein content of 0.7% by weight, a sulfate ion content of 6% by weight, and an ammonium ion content of 2.0% by weight) into the G17 activated carbon bed, pumped into Volumetric airspeed is 0.8m 3 / (m 3 h). The lysine fermentation waste water that passed through the G17 activated carbon bed was 3 / (m 3 The volume space velocity of h) is introduced into the bed layer of 330 macroporous weakly basic epoxy-based anion exchange resin (commercially purchased from Bengbu Tianxing Resin Co., Ltd., with an exchange capacity of 9 mmol / g (dry)). Obtain the lysine fermentation wastewater after anion exchange (hereinafter referred to as the lysine fermentation wastewater after treatment), the protein content in the lysine fermentation wastewater after the treatment is 0.7% by weight, the sulfate ion content is 0.04% by weight %, ammonium ion content is 2.1% by weight;
[0082] 2) The treated lysine ferm...
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