Method for producing biogas through mixing gibberellin fungus dreg and kitchen waste and carrying out anaerobic fermentation
A technology of food waste and anaerobic fermentation, applied in the direction of fermentation, waste fuel, etc., can solve the problems of low cost, high resources, waste, etc., and achieve the effects of improving system gas production, efficient operation, and simple equipment
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Embodiment 1
[0019] The food waste is collected and removed from larger impurities, then thoroughly mixed and crushed with a pulverizer, and then sieved through a sieve with a particle size of <5 mm as raw material. The inoculum sludge should be the sludge rich in active methanogens, centrifuge the sludge after standing for 6 hours at a speed of 4000 r / min for 5 minutes, remove the supernatant, and select the concentrated sludge after centrifugation. Add 30 g / L (according to 30 grams of inoculum sludge per liter of fermentation substrate) to the mixed substrate at the start-up stage of fermentation. Mix gibberellin residue and kitchen waste at a carbon-to-nitrogen ratio of 13.5:1, when the mixed substrate concentration VS = 10 g / L, the anaerobic fermentation temperature is 35±1°C, and the organic load is 4 gVS / (L ·d), under the reaction condition of hydraulic retention time of 8.6d, the average daily maximum gas production reaches 650m L / d.
Embodiment 2
[0021] The food waste is collected and removed from larger impurities, then thoroughly mixed and crushed with a pulverizer, and then sieved through a sieve with a particle size of <5 mm as raw material. Sludge should be rich in active methane bacteria, centrifuge the sludge after standing for 6 hours at 4000 r / min for 5 minutes, remove the supernatant, select the centrifuged concentrated sludge and put it in Add 30 g / L (according to 30 grams of inoculum sludge per liter of fermentation substrate) to the mixed substrate at the start-up stage of fermentation. Mix gibberellin residue and kitchen waste at a carbon-to-nitrogen ratio of 13.5:1. When the mixed substrate concentration VS = 10 g / L, the anaerobic fermentation temperature is 45±1°C, and the organic load is 5 gVS / (L·d), under the reaction condition of hydraulic retention time of 5.5d, the average daily maximum gas production reaches 720 mL / d.
Embodiment 3
[0023] The food waste is collected and removed from larger impurities, then thoroughly mixed and crushed with a pulverizer, and then sieved through a sieve with a particle size of <5 mm as raw material. Sludge should be rich in active methane bacteria, centrifuge the sludge after standing for 6 hours at 4000 r / min for 5 minutes, remove the supernatant, select the centrifuged concentrated sludge and put it in Add 30 g / L (according to 30 grams of inoculum sludge per liter of fermentation substrate) to the mixed substrate at the start-up stage of fermentation. Mix gibberellin residue and kitchen waste at a carbon-to-nitrogen ratio of 13.5:1. When the mixed substrate concentration VS = 10 g / L, the anaerobic fermentation temperature is 55±1°C, and the organic load is 6 gVS / (L·d), the maximum daily gas production reached an average of 760 mL / d under the reaction condition of a hydraulic retention time of 4.3 d.
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