Method for efficiently utilizing phosphorus in municipal domestic sewage sludge
A technology for urban domestic sewage and phosphorus elements, which is applied in the direction of sludge treatment, pyrolysis sludge treatment, chemical instruments and methods, etc., can solve the limited space available for phosphorus elements (for example, cannot be directly absorbed and utilized by plants, phosphorus elements Low availability, limited separation of phosphorus phase substances, etc., to achieve the effect of improving the utilization efficiency, benefiting plant growth, and high reusability
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Embodiment 1
[0029] This embodiment provides a method for efficient utilization of phosphorus in urban domestic sewage sludge, comprising the following steps:
[0030] Pretreatment of urban domestic sewage sludge: first, the urban domestic sewage sludge is taken from the dewatered sludge of the urban domestic sewage treatment plant (the basic physical and chemical properties of the urban domestic sewage sludge are shown in Table 1), and then the urban domestic sewage sludge is After the sewage sludge is exposed to the sun for 48 hours, the urban domestic sewage sludge is mechanically crushed and screened, and the sludge particles with a mesh number of 200-100 (0.075-0.15mm) are collected, and the sludge particles are sealed and stored . In this embodiment, the urban domestic sewage sludge is sun-dried and mechanically crushed.
[0031] Adding calcium oxide: weighing the above sludge granules, and adding calcium oxide to the sludge granules, the mass ratio of the calcium oxide to the sludg...
Embodiment 2
[0037]The difference between this embodiment and the first embodiment is that in this embodiment, calcium oxide is added to the sludge particles, and the mass ratio of the calcium oxide to the sludge particles is 1:4, and other steps are the same as the first embodiment. The sludge biochar that present embodiment obtains, this sludge biochar is carried out 31 P solid NMR analysis and characterization, obtained the sludge biochar 31 P solid nuclear magnetic resonance spectrum, after performing Gaussian peak splitting on the spectrum, calculate the spectral peak area of each phosphorus source material in the sludge biochar, and obtain the spectral peak area corresponding to the hydroxyl calcium phosphate in the sludge biochar It accounts for 4.17% of the spectral peak area of all phosphorus source substances in the sludge biochar.
Embodiment 3
[0039] The difference between this embodiment and the first embodiment is that in this embodiment, calcium oxide is added to the sludge particles, and the mass ratio of the calcium oxide to the sludge particles is 3:7, and other steps are the same as the first embodiment. The sludge biochar that present embodiment obtains, this sludge biochar is carried out 31 P solid NMR analysis and characterization, obtained the sludge biochar 31 P solid nuclear magnetic resonance spectrum, after performing Gaussian peak splitting on the spectrum, calculate the spectral peak area of each phosphorus source material in the sludge biochar, and obtain the spectral peak area corresponding to the hydroxyl calcium phosphate in the sludge biochar It accounts for 5.28% of the spectral peak area of all phosphorus source substances in the sludge biochar.
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