CN111871382A - Method for deodorizing wet garbage biogas residue fermentation product - Google Patents

Method for deodorizing wet garbage biogas residue fermentation product Download PDF

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Publication number
CN111871382A
CN111871382A CN202010728312.XA CN202010728312A CN111871382A CN 111871382 A CN111871382 A CN 111871382A CN 202010728312 A CN202010728312 A CN 202010728312A CN 111871382 A CN111871382 A CN 111871382A
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wet garbage
biogas residue
bentonite
garbage biogas
wet
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徐冰
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Shanghai Academy of Landscape Architecture Science and Planning
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Shanghai Academy of Landscape Architecture Science and Planning
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/20Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/103Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate comprising silica
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/12Naturally occurring clays or bleaching earth
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/16Alumino-silicates
    • B01J20/18Synthetic zeolitic molecular sieves
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

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  • Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Dispersion Chemistry (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Engineering & Computer Science (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention relates to a biogas residue deodorization method, in particular to a method for deodorizing fermentation products of wet garbage biogas residues. The invention aims to provide a method for deodorizing wet garbage biogas residue fermentation products. In order to solve the technical problems, the invention provides a method for deodorizing a wet garbage biogas residue fermentation product, which comprises cinnamaldehyde, bentonite and wet garbage biogas residue carbide. The cinnamaldehyde is an aldehyde organic compound, is yellow viscous liquid, is an allowable food synthetic spice specified in GB2076-2011, and can be used for preparing meat, seasonings, oral care products, chewing gum and candy essence. The bentonite is a non-metal mineral product with montmorillonite as a main mineral component, has strong adsorbability to gas, water and organic compounds, and is odorless, tasteless, nontoxic and environment-friendly. The wet garbage biogas residue carbide is a product obtained by high-temperature carbonization of wet garbage biogas residue after composting and has strong adsorption capacity.

Description

Method for deodorizing wet garbage biogas residue fermentation product
Technical Field
The invention relates to a method for deodorizing biogas residues, in particular to a method for improving the odor of wet garbage biogas residues.
Background
Malodorous gases are mainly sulfur-containing compounds (H)2S、SO2、SO3) Part of organic substances (alkanes, alkenes, alkynes, alcohols, aldehydes, ethers, esters, organic acids, phenols, aromatic hydrocarbons, etc.) and part of halogens (chlorine-containing compounds). The range of wet garbage is determined since the implementation of 'Shanghai City domestic garbage management regulation' on 7/1/2019, and the recovery amount of the recyclables in the whole city reaches 5600 tons/day. After the wet garbage is sorted to remove impurities such as plastic bags and the like, the wet garbage is sent into an anaerobic tank for fermentation to generate methane through the steps of crushing, cooking, extracting oil and the like, and each ton of the wet garbage can generate methane80 cubic meters, generates electricity by about 150 ℃ after combustion, and has a slag tapping rate of 30 percent. In order to better utilize the resource, the recycling of wet garbage biogas residues is developed.
The detection proves that the odor components in the wet garbage biogas residue mainly comprise ethanol, acetaldehyde, propionaldehyde, ethyl acetate, limonene, alpha-pinene, beta-pinene, methyl mercaptan and dimethyl disulfide. At present, low-temperature plasma deodorization equipment, a thermal combustion method, an adsorption method, a spraying method, a biological method and ultraviolet photolysis are mostly used for treating the odor in the market. Wherein, the low-temperature plasma has high investment at one time and secondary pollution. Thermal combustion process equipment is subject to corrosion, consumes fuel, and has high treatment cost. The biological method is immature and has no success.
The invention is technically characterized in that the characteristic of strong adsorbability after the wet garbage biogas residues are carbonized is utilized, the wet garbage biogas residues are utilized from the source, and the modified bentonite is utilized to change the physical and chemical properties of the wet garbage biogas residues and the effect of cinnamaldehyde neutralization odor to reduce the odor condition.
Disclosure of Invention
In view of the above, the invention provides a method for improving the odor of wet garbage biogas residues, which can effectively improve the odor condition of the wet garbage biogas residues.
The invention aims to provide a method for improving the odor of wet garbage biogas residues, which comprises the following steps: comprises cinnamyl aldehyde, bentonite and wet garbage biogas residue carbide. Cinnamaldehyde is permitted in GB2076-2011, has density of 1.046-1.052, melting point (deg.C) of-7.5 deg.C, refractive index (20 deg.C) of 1.619-1.623, acid value of 1.0% or less, boiling point (deg.C) of 253 (normal pressure), colorless or yellowish liquid, and bentonite density of 2-3g/cm3,Milk white powder.
The bentonite raw material is crushed, then the bentonite is added into an aluminum sulfate solution, the pH value is regulated to be neutral by stirring, and the bentonite modified by aluminum sulfate can be obtained by drying at the temperature of 500-600 ℃ after filtering and drying. The addition amount of the aluminum sulfate is 1-5 wt%.
The fermentation temperature of the wet garbage biogas residue carbide raw material is required to be 60-80 ℃, the stirring frequency is 10 minutes, the stirring is stopped for 40 minutes, the ventilation is uninterrupted, the fermentation strain is wet garbage aerobic thermophilic bacteria (the aerobic thermophilic bacteria specifically comprise bacillus subtilis A2, bacillus stearothermophilus M1, bacillus pumilus T6 and bacillus licheniformis N2), the fermentation time is 12-16 days, and the pH value is 5.5-7.0. The wet garbage biogas residue carbide is carbonized at the high temperature of 900-1200 ℃ for 6-10h under the condition of air isolation, and then oxidized and activated by air, carbon dioxide, water vapor or the mixed gas of the air, the carbon dioxide and the water vapor under the condition of 600-900 ℃.
The modifier also comprises a supported material, wherein the supported material comprises any one of titanium dioxide, silicon dioxide and zirconium dioxide supported by any one of MCM-41, TS-1, SBA-15 and HY molecular sieves. The load material is prepared by taking a molecular sieve as a template and adopting a sol-gel method.
The addition amount of the load type material is 0.05-0.1% of the total mass of the wet garbage biogas residue carbide; the loading amount of the titanium dioxide, the silicon dioxide or the zirconium dioxide is 0.5 to 2 percent.
Based on the odor improving material, the invention also provides a method for improving the odor of the wet garbage biogas residue by using the odor improving agent for the wet garbage biogas residue, which is characterized in that the cinnamaldehyde is prepared into a solution with the concentration of 500-2000ppm and is uniformly sprayed on the carbide of the wet garbage biogas residue; the temperature is controlled to be 50-60 ℃ by material enclosing, bentonite or aluminum sulfate modified bentonite is added and mixed evenly, and the effect of deodorization can be achieved.
Or mixing the cinnamaldehyde and the load-type material, and spraying the mixture on the wet garbage biogas residue carbide; the temperature is controlled to be 50-60 ℃ by material enclosing, bentonite or aluminum sulfate modified bentonite is added and mixed evenly, and the effect of deodorization can be achieved.
During the process of mixing and spraying the supported material and the cinnamaldehyde, 30-40% of the cinnamaldehyde is adsorbed in the supported material, the supported material forms small solid particles after being sprayed, gaps are formed in carbides of wet garbage biogas residues, and in the process of overflowing of wet garbage odor, the odor overlaps with the flavor of the cinnamaldehyde, so that more than 90% of the odor is reduced. During stacking, the odor does not disappear, but is immobilized in the carbonized material via the overlapping taste of cinnamaldehyde by the strong adsorption characteristics of the supported material. Thereby achieving the purpose of deodorization.
Detailed description of the preferred embodiments
Example 1
The wet garbage biogas residue odor modifier comprises cinnamaldehyde, bentonite and wet garbage biogas residue carbide, and the mass ratio of the raw materials is 0.001: 6: 15. the wet garbage biogas residue carbide is prepared by adding aerobic thermophilic bacteria into wet garbage raw materials at 60-80 ℃ under ventilation, fermenting for 12-16 days, carbonizing the fermentation product at 1000 ℃ for 8h, and oxidizing, activating and sintering in the air at 1000 ℃ for 3 h.
Example 2
The wet garbage biogas residue odor modifier comprises cinnamaldehyde, aluminum sulfate modified bentonite and wet garbage biogas residue carbide, and the mass ratio of the raw materials is 0.003: 7: 14. the wet garbage biogas residue carbide is prepared by adding aerobic thermophilic bacteria into wet garbage raw materials at 60-80 ℃ under ventilation, fermenting for 12-16 days, carbonizing the fermentation product at 1000 ℃ for 8h, and oxidizing, activating and sintering in the air at 1000 ℃ for 3 h. The aluminum sulfate modified bentonite is prepared by adding 2.5wt% of aluminum sulfate into crushed bentonite, adding an aluminum sulfate solution, stirring to adjust the pH value to be neutral, filtering, drying and drying at 500 ℃.
Example 3
The wet garbage biogas residue odor modifier comprises cinnamaldehyde, aluminum sulfate modified bentonite and wet garbage biogas residue carbide, and the mass ratio of the raw materials is 0.005: 10: 15. the wet garbage biogas residue carbide is prepared by adding aerobic thermophilic bacteria into a wet garbage raw material at 60-80 ℃ under ventilation, fermenting for 12-16 days, carbonizing the fermentation product at 1200 ℃ for 8h, and performing oxidation activation sintering in air and water vapor (wherein the addition amount of the water vapor only keeps 40% of the air humidity) at 900 ℃ for 3 h. The aluminum sulfate modified bentonite is prepared by adding 2.5wt% of aluminum sulfate into crushed bentonite, adding an aluminum sulfate solution, stirring to adjust the pH value to be neutral, filtering, drying and drying at 500 ℃.
Example 4
The wet garbage biogas residue odor modifier comprises cinnamaldehyde, SBA-15 loaded zirconium dioxide, aluminum sulfate modified bentonite and wet garbage biogas residue carbide, and the mass ratio of the raw materials is 0.005: 10: 15. the wet garbage biogas residue carbide is prepared by adding aerobic thermophilic bacteria into a wet garbage raw material at 60-80 ℃ under ventilation, fermenting for 12-16 days, carbonizing the fermentation product at 1200 ℃ for 8h, and performing oxidation activation sintering in air and water vapor (wherein the addition amount of the water vapor only keeps 40% of the air humidity) at 900 ℃ for 3 h. The aluminum sulfate modified bentonite is prepared by adding 2.5wt% of aluminum sulfate into crushed bentonite, adding an aluminum sulfate solution, stirring to adjust the pH value to be neutral, filtering, drying, and drying at 500 ℃ to obtain the aluminum sulfate modified bentonite, wherein the addition of SBA-15-loaded zirconium dioxide is 0.1% of the total mass of wet garbage biogas residue carbide, and the loading capacity of the zirconium dioxide is 2%.
Example 5
The wet garbage biogas residue odor modifier comprises cinnamaldehyde, MCM-41 loaded silica, aluminum sulfate modified bentonite and wet garbage biogas residue carbide, and the mass ratio of the raw materials is 0.005: 10: 15. the wet garbage biogas residue carbide is prepared by adding aerobic thermophilic bacteria into a wet garbage raw material at 60-80 ℃ under ventilation, fermenting for 12-16 days, carbonizing the fermentation product at 1200 ℃ for 8h, and performing oxidation activation sintering in air and water vapor (wherein the addition amount of the water vapor only keeps 40% of the air humidity) at 900 ℃ for 3 h. The aluminum sulfate modified bentonite is prepared by adding 2.5wt% of aluminum sulfate into crushed bentonite, adding an aluminum sulfate solution, stirring to adjust the pH value to be neutral, filtering, drying and drying at 500 ℃. The addition amount of MCM-41 loaded silicon dioxide is 0.08 percent of the total mass of wet garbage biogas residue carbide, and the loading amount of the silicon dioxide is 1.5 percent.
The modifier of the embodiment 1 to 5 is adopted to respectively carry out deodorization treatment on a certain refuse treatment plant of Shanghai Songjiang leaf elysees, a certain refuse treatment plant of Shanghai Songjiang creek and a certain refuse treatment plant of Shanghai Yanpu, and the effect is as follows:
TABLE 1 certain refuse treatment plant of Shanghai Songjiang leaf elysees
Ppm of methane Styrene ppm Ammonia gas ppm Methyl mercaptan ppm Dimethylamine ppm Propionaldehyde ppm
Before treatment 260-380 2-10 74-87 0.2-0.4 3-7 16-23
Example 1 25-33 Less than 1.5 5-10 0.05-0.1 0.05-0.1 Less than 3
Example 2 10-17 Less than 1 5-10 Less than 0.05 Less than 0.05 1.2-2.5
Example 3 5-15 0.2-0.5 3-8 0 0 0.8-1.0
Example 4 0-10 0 0.6-4 0 0 0.1-0.5
Example 5 0-8 0 0.4-2.5 0 0 0.1-0.5
As can be seen from the table, the odor modifying agents of examples 1 to 5 all achieved significant reduction in the odor of garbage, but examples 4 and 5 exhibited significant effects, and none of them were detected in the indexes related to styrene, methyl mercaptan, and dimethylamine, and showed excellent effects.

Claims (8)

1. The wet garbage biogas residue odor modifier is characterized by comprising cinnamaldehyde, bentonite and wet garbage biogas residue carbide, wherein the mass ratio of the raw materials is 0.001-0.005: 5-10: 12-18.
2. The odor improver for wet garbage biogas residues as defined in claim 1, wherein the carbide of wet garbage biogas residues is obtained by adding aerobic thermophilic bacteria to a raw material of wet garbage under ventilation at 60-80 ℃, fermenting for 12-16 days, carbonizing the fermentation product at 1000-1200 ℃ for 6-10h, and then performing oxidation activation sintering with air, water vapor or a mixture of the two at 900-1200 ℃ for 2-3 h.
3. The wet garbage biogas residue odor modifier as defined in claim 2, wherein the bentonite is aluminum sulfate modified bentonite, which is prepared by crushing bentonite, adding aluminum sulfate solution, stirring to adjust pH to neutrality, filtering, drying, and drying at 600 ℃ to obtain aluminum sulfate modified bentonite.
4. The wet garbage biogas residue odor improver as claimed in claim 3, wherein the aluminum sulfate is added in an amount of 1-5 wt%.
5. The wet waste biogas residue odor improver according to claim 4, wherein the improver further comprises a supported material, and the supported material comprises a supported material obtained from any one of titanium dioxide, silicon dioxide and zirconium dioxide supported by any one of MCM-41, TS-1, SBA-15 and HY molecular sieves.
6. The wet waste biogas residue odor improver according to claim 5, wherein the addition amount of the load-type material is 0.05-0.1% of the total mass of the wet waste biogas residue carbide; the loading amount of the titanium dioxide, the silicon dioxide or the zirconium dioxide is 0.5 to 2 percent.
7. The method for improving the odor of the wet garbage biogas residue by adopting the wet garbage biogas residue odor improver as defined in any one of claims 1 to 6, is characterized in that the cinnamaldehyde is prepared into a solution of 500-2000ppm and uniformly sprayed on the carbide of the wet garbage biogas residue; the temperature is controlled to be 50-60 ℃ by material enclosing, bentonite or aluminum sulfate modified bentonite is added and mixed evenly, and the effect of deodorization can be achieved.
8. The improved process of claim 7, wherein cinnamaldehyde is mixed with a support material and sprayed onto the wet landfill sludge carbide; the temperature is controlled to be 50-60 ℃ by material enclosing, bentonite or aluminum sulfate modified bentonite is added and mixed evenly, and the effect of deodorization can be achieved.
CN202010728312.XA 2020-07-27 2020-07-27 Method for deodorizing wet garbage biogas residue fermentation product Pending CN111871382A (en)

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CN103960284A (en) * 2014-05-09 2014-08-06 尹无忌 Deodorant disinfectant for household garbage
CN105060946A (en) * 2015-08-05 2015-11-18 广州英昊环境科技有限公司 Method and device for preparing fertilizer from kitchen garbage
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CN109694161A (en) * 2019-01-22 2019-04-30 智造起源科技有限公司 Sewage, sludge and garbage as resource and energy closure processing system and method
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