Dosing method of thiobacillus thiooxidans energy substances for municipal sludge dehydration treatment
A technology of Thiobacillus thiooxidans and municipal sludge, which is applied in the fields of biological sludge treatment, dehydration/drying/thickened sludge treatment, etc., can solve the problems that cannot fully meet the requirements of leaching microbial proliferation, affect the number and activity of microorganisms, and affect biological Leach acidification and oxidation efficiency and other issues, to achieve the effect of benefiting subsequent resource utilization, low risk of secondary pollution, and short conditioning time
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Embodiment 1
[0023] Embodiment 1 (sulfur source type (S in the dehydration process) 0 and Na 2 S 2 o 3 )Research)
[0024] The sludge used in this experiment was taken from the residual sludge in the secondary sedimentation tank of a certain urban sewage plant, and its basic properties are shown in Table 1.
[0025] Table 1 Basic properties of the sludge tested
[0026]
[0027]
[0028] The test procedure is as follows:
[0029] (1) Take 150mL of the test sludge with the properties shown in Table 1, do not add 2g / L single sulfur source (S 0 and Na 2 S 2 o 3 ), placed in a water bath shaker at a speed of 180r / min and shaken at a constant temperature of 28°C for culture; when the pH value of the sludge system was 2.8, the first culture was completed to obtain 20 mL of culture; then, to the second Add 130mL of the test sludge with the properties shown in Table 1 to the primary culture, and carry out the second shake flask culture under the same conditions; finally, add 6.5 vol...
Embodiment 2
[0033] Embodiment 2 (ferrous iron source composite sulfur source (Na 2 S 2 o 3 +FeSO 4 、Na 2 S 2 o 3 +FeCl 2 )Research)
[0034] The test procedure is as follows:
[0035] (1) Take 150mL of test sludge with the properties shown in Table 1, add 6g / L ferrous source to compound 2g / L sulfur source (Na 2 S 2 o 3 +FeSO 4 、Na 2 S 2 o 3 +FeCl 2), placed in a water bath shaker at a speed of 180r / min and shaken at a constant temperature of 28°C for culture; when the pH value of the sludge system was 2.8, the first culture was completed to obtain 20 mL of culture; then, to the second Add 130mL of the test sludge with the properties shown in Table 1 to the primary culture, and carry out the second shake flask culture under the same conditions; finally, add 6.5 volumes of the test sludge with the properties shown in Table 1 to the second culture. The sludge was cultured in shake flasks repeatedly to obtain the inoculum;
[0036] (2) the inoculum that step (1) obtains is dr...
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