Background technology
Along with several big water system eutrophication aggravations of China, break out wawter bloom, red tide phenomenon in succession, country also improves constantly the water body emission standard.Biological denitrificaion is to use the most general technology in the municipal sewage treatment, and the removal of total nitrogen finally will be passed through denitrification process, and denitrifying bacteria is converted into N with the nitric nitrogen that aerobic processes produces under anoxia condition
2Enter atmosphere, to reach the purpose of removing total nitrogen in the water.Reach Nitrogen removal effect preferably, denitrification process must have enough organic carbon sources (general BOD
5/ TN>3-5 thinks that promptly carbon source is sufficient).But, present China municipal effluent BOD
5M.L. is lower, and the insufficient problem of ubiquity denitrifying carbon source has limited greatly that the Sewage Plant with biological denitrificaion function is stable to play a role effectively.
To the not enough problem of denitrifying carbon source, early stage research mainly is to add low molecule organic matters such as methyl alcohol, ethanol in the denitrification section, and this additional carbon can improve denitrification rate, but costs an arm and a leg.In recent years the research of additional carbon being mainly utilizes trade effluent or percolate as denitrifying carbon source; Can not only realize economic additional carbon dosing method; Can also solve the handling problem of part trade effluent and percolate; But the ammonia nitrogen of these waste water ubiquity high densitys, heavy metal ion and other toxic substance are not enough as water quality is understood, and blindly add and may produce serious toxic side effect to whole denitrification system; Mainly be as denitrifying carbon source in addition with excess sludge after anaerobic digestion; This method also can improve denitrification efficient; But contain a large amount of phosphoric acid salt in the mud after anaerobic treatment; Before as denitrifying carbon source, need carry out the chemical precipitation dephosphorization, so not only increased running cost also can because of dephosphorization thoroughly or medicament add the excessive Sewage treatment systems secondary pollution problem that causes.
Summary of the invention
To the problem that above method exists, the present invention mainly provides a kind of method of utilizing the excess sludge ethanol-type fermentation supplementing denitrifying carbon source, and main purpose is:
(1) solves the insufficient problem of sewage work's denitrifying carbon source;
(2) utilize the main end products ethanol of ethanol-type fermentation, acetate as adding the denitrification organic carbon source;
(3) avoid the mud after the anaerobic treatment as denitrification section organic carbon source problem, the problem includes: phosphorus accumulation problem.
The present invention in order to achieve the above object, particular content is following:
A kind of method of utilizing the excess sludge ethanol-type fermentation supplementing denitrifying carbon source comprises: thermal hydrolysis reactor drum, fermentation reactor, return line, condensing works, carbon source holding tank and shore pipe; It is characterized in that: the excess sludge of sewage work gets into fermentation reactor after the pre-treatment of thermal hydrolysis reactor drum; To ferment the back remainder through the shore pipe discharging; Other part is back to the thermal hydrolysis reactor drum through return line; The trip temperature of going forward side by side regulation and control are between 120 ℃-130 ℃, and the materials such as ethanol, acetate that make boiling point be lower than 120 ℃ exist with gaseous form, reclaim this portion of product to carbon source holding tank through the condensing and recycling device at last.
The thermal hydrolysis reactor drum can effectively improve the anaerobic digestion performance of mud as the pretreatment unit of excess sludge, and for effective control in follow-up ethanol-type fermentation stage provides safeguard, and the thermal hydrolysis reactor drum has special condensation of gas retrieving arrangement.
Fermentation reactor receives the pretreated mud of thermal hydrolysis, and is domesticating of substrate culture ethanol-type fermentation bacterium with it, and fermentation reactor is controlled at the ethanol-type fermentation stage, and tunning is main with ethanol, acetate; Part resultant product is discharged through shore pipe, and other product is back to the thermal hydrolysis reactor drum; When ethanol-type fermentation mud is back to the thermal hydrolysis reactor drum; Thermal hydrolysis is controlled between 120 ℃~130 ℃; Because the boiling point of ethanol and acetate is respectively 118 ℃ and 78.3 ℃; Ethanol and acetate evaporate in pyrohydrolysis process, and through the condensing and recycling device main end products ethanol of ethanol-type fermentation and acetate are reclaimed, and are added to sewage work's denitrification section supplementary carbon source as the high-quality organic carbon source.
Beneficial effect of the present invention
1, the used mud of the present invention is from the excess sludge of sewage work, and the product after it is handled has not only effectively utilized resource as denitrifying carbon source, and mud is further handled, and finally reaches the purpose of waste recycling;
2, fermentation reactor is controlled at the ethanol-type fermentation stage, collects the main end products ethanol of ethanol-type fermentation, acetate through the condensing and recycling mode.As denitrifying carbon source, can effectively improve denitrification efficient with this;
3, reclaim main end products ethanol of ethanol-type fermentation and acetate after evaporating with the condensing and recycling device, avoid the system's phosphorus accumulation problem that directly causes with anaerobically digested sludge as denitrifying carbon source.
Description of drawings
Fig. 1 is a kind of method process schematic representation that utilizes the excess sludge ethanol-type fermentation supplementing denitrifying carbon source
Label declaration among the figure:
1, thermal hydrolysis reactor drum 2, fermentation reactor 3, mud return line 4, condensing works
5, carbon source holding tank 6, shore pipe 7, advance the mud pipe
Embodiment:
It is following to specify embodiment of the present invention in conjunction with Fig. 1:
With simple phase carbon source is that matrix is cultivated the ethanol-type fermentation bacterium; Cultured ethanol-type fermentation bacterium is added in the fermentation reactor (2) as seed sludge; Control parameters (pH value, basicity, temperature, redox potential etc.) is controlled at the ethanol-type fermentation stage with fermentation reactor (2); Stable back progressively replaces simple liquid matrix with the pretreated excess sludge product of thermal hydrolysis reactor drum (1), and the ethanol-type fermentation bacterium is tamed, and it is the ethanol-type fermentation stage of matrix that fermentation reactor (2) is controlled at mud; Fermentation after product remainder is through shore pipe (6) discharging; Other part is back to thermal hydrolysis reactor drum (1) through return line (3), and with temperature adjusting between 120 ℃~130 ℃, the material such as ethanol, acetate that makes boiling point be lower than 120 ℃ exists with gaseous form; Reclaim this portion of product to carbon source holding tank (5) through condensing and recycling device (4) at last, the high-quality organic carbon source after the recovery replenishes according to the shortage situation of place Sewage Plant denitrifying carbon source and adds.