CN107603644A - It is a kind of to couple hydrothermal carbonization and the organic refuse treatment appts and handling process of biochemical reaction principle - Google Patents
It is a kind of to couple hydrothermal carbonization and the organic refuse treatment appts and handling process of biochemical reaction principle Download PDFInfo
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- CN107603644A CN107603644A CN201710939825.3A CN201710939825A CN107603644A CN 107603644 A CN107603644 A CN 107603644A CN 201710939825 A CN201710939825 A CN 201710939825A CN 107603644 A CN107603644 A CN 107603644A
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- 238000000034 method Methods 0.000 title claims abstract description 41
- 230000008569 process Effects 0.000 title claims abstract description 36
- 238000005842 biochemical reaction Methods 0.000 title claims abstract description 28
- 238000012545 processing Methods 0.000 claims abstract description 95
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 77
- 230000000050 nutritive effect Effects 0.000 claims abstract description 66
- 239000007789 gas Substances 0.000 claims abstract description 32
- 230000008878 coupling Effects 0.000 claims abstract description 11
- 238000010168 coupling process Methods 0.000 claims abstract description 11
- 238000005859 coupling reaction Methods 0.000 claims abstract description 11
- 238000004519 manufacturing process Methods 0.000 claims abstract description 10
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 9
- 239000001301 oxygen Substances 0.000 claims abstract description 9
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 9
- 239000005416 organic matter Substances 0.000 claims abstract description 3
- 239000007788 liquid Substances 0.000 claims description 62
- 239000000463 material Substances 0.000 claims description 42
- 239000003245 coal Substances 0.000 claims description 39
- 238000000926 separation method Methods 0.000 claims description 28
- 238000001816 cooling Methods 0.000 claims description 23
- 238000010438 heat treatment Methods 0.000 claims description 23
- 239000010815 organic waste Substances 0.000 claims description 20
- 238000006243 chemical reaction Methods 0.000 claims description 17
- 238000003756 stirring Methods 0.000 claims description 16
- 238000012544 monitoring process Methods 0.000 claims description 15
- 238000001035 drying Methods 0.000 claims description 14
- 239000000047 product Substances 0.000 claims description 14
- 239000007787 solid Substances 0.000 claims description 13
- 239000012265 solid product Substances 0.000 claims description 12
- 239000011344 liquid material Substances 0.000 claims description 11
- 238000001471 micro-filtration Methods 0.000 claims description 9
- 238000005255 carburizing Methods 0.000 claims description 6
- 239000003153 chemical reaction reagent Substances 0.000 claims description 6
- 239000000706 filtrate Substances 0.000 claims description 6
- 230000001580 bacterial effect Effects 0.000 claims description 5
- 238000001764 infiltration Methods 0.000 claims description 5
- 238000005374 membrane filtration Methods 0.000 claims description 5
- 238000001728 nano-filtration Methods 0.000 claims description 5
- 239000002994 raw material Substances 0.000 claims description 5
- 239000011343 solid material Substances 0.000 claims description 5
- 238000000108 ultra-filtration Methods 0.000 claims description 5
- 238000013461 design Methods 0.000 claims description 3
- 238000002360 preparation method Methods 0.000 claims description 3
- 241001148471 unidentified anaerobic bacterium Species 0.000 claims description 3
- 241000894006 Bacteria Species 0.000 claims 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 abstract description 16
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 abstract description 16
- 229910052799 carbon Inorganic materials 0.000 abstract description 16
- 239000001569 carbon dioxide Substances 0.000 abstract description 8
- 229910002092 carbon dioxide Inorganic materials 0.000 abstract description 8
- 230000008859 change Effects 0.000 abstract description 6
- 150000007524 organic acids Chemical class 0.000 abstract description 5
- 235000016709 nutrition Nutrition 0.000 abstract description 4
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- 238000006555 catalytic reaction Methods 0.000 abstract description 3
- 239000003337 fertilizer Substances 0.000 abstract description 3
- 244000005700 microbiome Species 0.000 abstract description 3
- 235000015097 nutrients Nutrition 0.000 abstract description 3
- 230000035484 reaction time Effects 0.000 abstract description 3
- 230000000813 microbial effect Effects 0.000 abstract description 2
- 238000004065 wastewater treatment Methods 0.000 abstract description 2
- 230000000284 resting effect Effects 0.000 abstract 1
- 238000005516 engineering process Methods 0.000 description 15
- 239000010813 municipal solid waste Substances 0.000 description 9
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 description 6
- 229910001220 stainless steel Inorganic materials 0.000 description 6
- 239000010935 stainless steel Substances 0.000 description 6
- 238000002156 mixing Methods 0.000 description 5
- 229920003023 plastic Polymers 0.000 description 5
- 239000002028 Biomass Substances 0.000 description 4
- 230000005540 biological transmission Effects 0.000 description 4
- BDAGIHXWWSANSR-UHFFFAOYSA-N methanoic acid Natural products OC=O BDAGIHXWWSANSR-UHFFFAOYSA-N 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 239000010865 sewage Substances 0.000 description 4
- 239000010802 sludge Substances 0.000 description 4
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- OSWFIVFLDKOXQC-UHFFFAOYSA-N 4-(3-methoxyphenyl)aniline Chemical compound COC1=CC=CC(C=2C=CC(N)=CC=2)=C1 OSWFIVFLDKOXQC-UHFFFAOYSA-N 0.000 description 2
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- 239000002253 acid Substances 0.000 description 2
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- -1 bed mud Chemical compound 0.000 description 2
- 238000006114 decarboxylation reaction Methods 0.000 description 2
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- 238000006297 dehydration reaction Methods 0.000 description 2
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- 235000019253 formic acid Nutrition 0.000 description 2
- 230000008676 import Effects 0.000 description 2
- 238000005259 measurement Methods 0.000 description 2
- 230000001473 noxious effect Effects 0.000 description 2
- 238000004806 packaging method and process Methods 0.000 description 2
- 244000144985 peep Species 0.000 description 2
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- 238000005086 pumping Methods 0.000 description 2
- 239000010902 straw Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 230000026676 system process Effects 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- 239000003643 water by type Substances 0.000 description 2
- 206010019233 Headaches Diseases 0.000 description 1
- 230000001133 acceleration Effects 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 239000002361 compost Substances 0.000 description 1
- 238000005336 cracking Methods 0.000 description 1
- 230000029087 digestion Effects 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 125000000524 functional group Chemical group 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 231100000869 headache Toxicity 0.000 description 1
- 238000011086 high cleaning Methods 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 125000004435 hydrogen atom Chemical class [H]* 0.000 description 1
- 239000011261 inert gas Substances 0.000 description 1
- 239000010806 kitchen waste Substances 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
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Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
Hydrothermal carbonization and the organic refuse treatment appts and handling process of biochemical reaction principle are coupled the invention discloses a kind of, by the way that hydrothermal carbonization and microbial biochemical Catalysis Principles are combined, form new coupling processing technical matters, the above-mentioned discarded object containing organic carbon is converted into biological carbon, the problem for solving wastewater treatment in system;Crop nutritive water with notable fertilizer efficiency of the production simultaneously rich in organic matter and nutrition, efficiency and benefit are significantly improved, the final gas discharge of whole technological process is substantially carbon dioxide.The crop nutritive water organic carbon content 1 30% that the present invention obtains, total nutrient NPK0.1 10%, small molecular organic acid class (C<5) microorganism based on, aerobic and oxygen mixes 1,000 1000000000/ milliliters of group, with reaction time and resting period change of producing.
Description
Technical field
The present invention relates to a kind of organic refuse treatment appts for coupling hydrothermal carbonization and biochemical reaction principle and processing work
Skill, belong to the fields such as the innoxious and recycling treatment of the discarded object containing organic carbon.
Background technology
House refuse, kitchen garbage, sewage disposal sludge, Sediments, refuse leachate, wooden waste residue, crops straw
Stalk etc. belongs to " organic waste ", and the general character of these discarded objects is containing organic carbon.By taking common kitchen garbage as an example, it
Amount is big, and moisture content is high, is a problem during China's urban garbage disposal.Anaerobic digestion of kitchen wastes is big at present
It is more using the technology such as ferment, make compost.Exist reaction speed is slow, processing not exclusively, produce the problems such as noxious odor and gas.Again
Such as organic waste and refuse leachate, this is an international headache.Recyclable rubbish etc. is all sorted, finally remaining to fill out
One of Main Ingredients and Appearance buried is organic waste.Organic waste is the very big but problem without solution of refuse landfill amount.It is each
Refuse landfill using land limited and quantity of refuse sustainable growth all because perplexed.Organic waste crop root, it is natural
The components such as high organic that refuse leachate caused by precipitation etc. contains, high ammonia nitrogen make it that biotechnology is helpless.Rubbish oozes
Drinking water and the groundwater resources safety in the city on transparent liquid serious threat refuse landfill periphery.With garbage loading embeading amount not
Disconnected increase, the collection and processing of refuse leachate are increasingly urgent.Therefore, it is badly in need of finding suitable China meal of these organic wastes
The technology path and equipment of kitchen garbage as resource processing.
Cracking and hydrothermal carbonization are existing abiotic treating method for organic refuse.Both of which can reduce organic waste biology
Hydrogen, oxygen content in matter, and change into the carbide rich in carbon.Carbonization is cracked to refer in inert gas container, will be organic
(1-20 DEG C/min) is heated to 350-700 DEG C and stops a few houres to a kind of typical carbonization method of several days discarded object at a slow speed;
Hydrothermal carbonization (Hydro-thermal Carbonization;HTC it is) that abandoned biomass is closed water-soluble at 150-350 DEG C
More than 1h is stopped in liquid, is a kind of acceleration pyrolysis for being dehydrated decarboxylation.Compared with tradition cracks carbonization technology, hydrothermal carbonization
With significant advantage:1st, substantial amounts of pretreatment expense has been saved without drying in the high abandoned biomass of processing water content
With;2nd, it is mainly dehydration to chemically react, and carbon fixed efficiency is high in abandoned biomass;3rd, reaction condition is gentle, simultaneously
The exothermic process of dehydration decarboxylation provides part energy for reaction, therefore the technology energy consumption is low;4th, hydrothermal carbonization remains greatly
Oxygen, nitrogen in amount abandoned biomass, carbide surface contain abundant oxygen-containing, nitrogen-containing functional group, can be applied to a variety of necks
Domain;5th, processing equipment is simple and convenient to operate, is strong using scalable section.But in the industry of conventional hydrothermal carbonization technology
Change in application, the processing of output waste water seriously adds the cost of technology, and limits the promotion and application of HTC technologies.
The content of the invention
A kind of the present invention is intended to provide organic refuse treatment appts and place for coupling hydrothermal carbonization and biochemical reaction principle
Science and engineering skill.By the way that hydrothermal carbonization and microbial biochemical Catalysis Principles are combined, new coupling processing technical matters is formed, will
The above-mentioned discarded object containing organic carbon is converted into biological carbon, the problem for solving wastewater treatment in system;Production is rich in organic simultaneously
The crop nutritive water with notable fertilizer efficiency of matter and nutrition, significantly improves efficiency and benefit.
Organic waste of the present invention includes but is not limited to house refuse, kitchen garbage, sewage disposal sludge, water body
The discarded objects containing organic carbon such as bed mud, refuse leachate, wooden waste residue, agricultural crop straw.
The organic refuse treatment appts of present invention coupling hydrothermal carbonization and biochemical reaction principle, including pretreatment system 1,
Hydrothermal carbonization retort 2, biological coal processing system 3, liquid processing system 4 and crop nutritive water processing system 5;
The pretreatment system 1 is used to crush organic waste, mixed and heat etc. to pre-process, and meets material
The feed conditions of hydrothermal carbonization retort 2.The pretreatment system 1 includes crushing system 6, charging system 7 and prepares tank 8,
Stirring system 9, heating system 10, detecting system 11, discharge system 12 and other accessory systems are provided with the preparation tank 8
13;In actual motion, pretreatment system 1 can also be covered more and be used in combination with a set of exclusive use.
The hydrothermal carbonization retort 2 is used to carry out hydrothermal carbonization reaction, including charging system 7, heating system 10, stirring
System 9, monitoring system 11, blowdown system 15, discharge system 12, other accessory systems 13 and cooling system 14.Hydrothermal carbonization
The aqueous solid product generated in retort 2 delivers to biological coal processing system 3 after the cooling of cooling system 14 and is used to produce
Biological coal finished product, gaseous product (predominantly carbon dioxide, a small amount of steam and micro organic volatile composition) pass through blowdown system 15
Deliver to crop nutritive water processing system 5.In actual motion, two or more general hydrothermal carbonization retort 2
Close and use, the quantity of each system includes but is not limited to 1 set in hydrothermal carbonization retort 2.The hydrothermal carbonization retort 2 is
The material such as stainless steel or heat resistant plastice is made.
The biological coal processing system 3 is used for the processing of biological coal finished product, including solid-liquid separation system and baking
Dry systems.Wherein solid-liquid separation system is used for the separation of solid and liquid of the aqueous solid product generated in hydrothermal carbonization retort 2,
Solid material after separation processes biological coal by drying system, and liquid enters liquid processing system 4 or crop nutritive water
Processing system 5.The quantity of each system in biological coal processing system 3 includes but is not limited to 1 set.Separation of solid and liquid
Including but not limited to commercialized solid-liquid separation system, drying system are including but not limited to commercialized system at present at present
Drying system.
The liquid processing system 4 is used for the processing that liquid in system 3 is processed to biological coal, including but not limited to
Current commercialized micro-filtration (MF), ultrafiltration system (UF), nanofiltration system (NF) and counter-infiltration system (RO) etc., according to operation need
A set of or complete unit can be opened.
The crop nutritive water processing system 5 includes charging system 7, crop nutritive water retort 16 and processing
System 18, stirring system 9, heating system 10, monitoring system 11, discharging are provided with the crop nutritive water retort 16
System 12, other accessory systems 13, gas handling system 17 and blowdown system 15.System 5 is processed in the crop nutritive water
In, the liquid from liquid processing system 4 or biological coal processing system 3 is anti-into crop nutritive water by charging system 7
Tank 16 is answered, meanwhile, the gas from hydrothermal carbonization retort 2 enters crop nutritive water retort 16 by gas handling system 17;Make
Material caused by thing nutritive water retort 16 enters processing system 18 by discharge system 12 and processes crop nutrition
Water, gas discharge after being handled by the collection of blowdown system 15, and the final gas discharge of whole technological process is substantially carbon dioxide.
In actual motion, crop nutritive water processing system 5 can be used in combination with one or more sets, crop nutritive water processing system
The quantity of each system includes but is not limited to 1 set in 5.
Crushing system 6 includes but is not limited to the modes such as hand breaking, Mechanical Crushing.
Charging system 7 is used for the addition of material, including but not limited to artificial, forklift, transmission belt, pumping etc..
Prepare tank 8 to be made up of materials such as stainless steel or heat resistant plastices, the pretreatment of mixing and preheating for material etc..
Stirring system 9 is used for the mixing of material, including but not limited to artificial, mechanical agitation, pump circulation stirring, pneumatically stirs
The mode such as mix.
Heating system 10 is used for the heating of material, the including but not limited to mode such as steam heating, electrical heating, oil heating.
Monitoring system 11 is used for the monitoring of associated control parameters in retort, including but not limited to level monitoring, temperature
Monitoring and sample tap and peep hole with the chemical measurements of water such as pH etc..
Discharge system 12 is used for the transfer of differential responses tank, different system material, can be any side such as artificial, machinery
Formula, including but not limited to forklift, transmission belt, pump etc..
Other accessory systems 13 include but is not limited to Butterworth Hatch, staff's mouth, acid solution or lye import etc..
Cooling system 14 is used for the cooling of material in hydrothermal carbonization retort 2, the including but not limited to side such as water cooling, oil cooling
Formula.
Blowdown system 15 is used for the emptying of gas material in retort, including but not limited to the emptying side such as artificial, machinery
Formula.
Crop nutritive water retort 16 is made up of materials such as stainless steel or common plastics, for carrying out biochemical reaction.
The subsequent production that processing system 18 is used for crop nutritive water is processed, such as product proportioning, packaging, storage etc..
In actual motion, the quantity of processing system 18 includes but is not limited to 1 set.
The organic waste treatment technique of present invention coupling hydrothermal carbonization and biochemical reaction principle, comprises the following steps:
1st, pre-process
Organic waste is entered by charging system 7 after the break process of crushing system 6 and prepares tank 8, is preparing tank 8
Interior heating simultaneously mixes, and pretreated material is obtained, to reach the feed conditions of hydrothermal carbonization retort 2;The pretreated material
Temperature >=50 DEG C, water content >=30%, material size<125cm3。
2nd, hydrothermal carbonization reacts
The pretreated material is sent into hydrothermal carbonization retort 2 by charging system 7, carries out hydrothermal carbonization reaction,
The aqueous solid product of generation through cooling system 14 cooling after deliver to biological coal processing system 3, gas be cooled to 50 DEG C with
Crop nutritive water processing system 5 is delivered to after lower.Hydrothermal carbonization reaction design parameter is as follows:Temperature is 80-400 DEG C, pressure
For 0-30 MPa, pH is that 2-9 (passes through C<5 small molecular organic acid regulation pH value, such as formic acid, acetic acid).
3rd, the production of biological coal
The aqueous solid product generated in hydrothermal carbonization retort 2 carries out separation of solid and liquid through solid-liquid separation system, after separation
Solid material by drying system process biological coal (30-200 DEG C of drying temperature), liquid material be cooled to 70 DEG C with
Enter liquid processing system 4 or crop nutritive water processing system 5 after lower (for liquid material, if necessary to enter hydro-thermal
Carburizing reagent tank reuse, then need to be handled into liquid processing system 4, if work will not can be directly entered if reuse
Thing nutritive water processes system).
4th, liquid handling
The liquid material obtained after step 3 separation of solid and liquid is filtered by membrane filtration system, by the non-solubilised state in liquid
Larger molecular organicses are collected, and deliver to and raw material is used as in hydrothermal carbonization retort 2, and filtrate delivers to the processing of crop nutritive water
System 5.The membrane filtration system includes microfiltration systems (MF), ultrafiltration system (UF), nanofiltration system (NF), counter-infiltration system
Etc. (RO) one or more in.
5th, biochemical reaction
The filtrate and step 2 that the liquid material and/or step 4 that step 3 obtains obtain react caused gas and deliver to work
Biochemical reaction is carried out in thing nutritive water retort 16, the material obtained after biochemical reaction is crop nutritive water, and gas is through collecting
Discharged after processing.The final gas discharge of whole technological process is substantially carbon dioxide.Biochemical reaction major parameter is as follows:Temperature
20-70 DEG C, pH value 3-9 of degree, and add the mixed bacterial being made up of aerobic flora and oxygen flora and anaerobic bacteria flora.Added
Mixed bacterial can be the sludge of sewage treatment plant or the bed mud etc. in river course.
The ratio of gas and liquid need not be controlled in biochemical reaction process, the simultaneous reactions time also without control, leads to
It is often that can be determined according to product purpose 3-200 hours.
The crop nutritive water organic carbon content 1-30% that the present invention obtains, total nutrient NPK0.1-10%, small molecular organic acid
Class (C<5) microorganism based on, aerobic and oxygen mixes group's 1000-1000000000/ milliliters, with reaction time and storage of producing
Time change.
The core of hydrothermal carbonization technology is its economy.The determinant of economy is the reaction temperature of retort, pressure
The processing of caused liquid and the circulation of wherein organic carbon are reacted again in power and catalyst efficiency and course of reaction.Conventional
Hydrothermal carbonization technology, should so as to seriously restrict the technology commercialization just because of above-mentioned reason causes high cost and non-Economy
With.The present invention fundamentally solves the economy problems of hydrothermal carbonization.Various organic wastes are converted into biology by the present invention
Carbon and the crop nutritive water with notable fertilizer efficiency rich in organic matter and nutrition, and any noxious emission is not produced, it is whole
Uniquely discharge is a small amount of carbon dioxide to individual technical matters.
Compared with the prior art, beneficial effects of the present invention are embodied in:
1st, organic waste such as house refuse, stalk etc. can be converted into biological coal by the present invention and other added values are high
Cleaning products, realize garbage as resource utilize.Traditional HTC technologies produce a large amount of waste water, significantly increase HTC technologies
Cost, and limit the promotion and application of HTC technologies.The present invention can solve this bottleneck, significantly reduce technical costs.
2nd, the present invention is again introduced into reaction, substantially using larger molecular organicses in mocromembrane technology recovery reactor output object
The full utilization of raw material is realized, substantially increases reaction efficiency and process efficiency.
Brief description of the drawings
Fig. 1 is present invention coupling hydrothermal carbonization and the organic refuse treatment appts schematic diagram of biochemical reaction principle;
Fig. 2 is the structural representation of pretreatment system 1 in processing unit of the present invention;
Fig. 3 is the structural representation of hydro-thermal carburizing reagent tank 2 in processing unit of the present invention, is two hydro-thermal carbon in schematic diagram
Change retort combination;
Fig. 4 is the structural representation that crop nutritive water processes system 5 in processing unit of the present invention.
Label in figure:1 pretreatment system;2 hydrothermal carbonization retort;3 biological coals process system;4 liquid handling systems
System;5 crop nutritive waters process system;6 crushing systems;7 charging systems;8 prepare tank;9 stirring systems;10 heating systems;
11 monitoring systems;12 discharge systems;13 other accessory systems;14 cooling systems;15 blowdown systems;16 crop nutritive waters react
Tank;17 gas handling systems.
Embodiment
As shown in figure 1, present invention coupling hydrothermal carbonization and the organic refuse treatment appts of biochemical reaction principle, including it is pre-
Processing system 1, hydrothermal carbonization retort 2, biological coal processing system 3, liquid processing system 4 and the processing of crop nutritive water
Production system 5;
The pretreatment system 1 is used to crush organic waste, mixed and heat etc. to pre-process, and meets material
The feed conditions of hydrothermal carbonization retort 2.As shown in Fig. 2 the pretreatment system 1 includes crushing system 6, the and of charging system 7
Prepare tank 8, it is described preparation tank 8 in be provided with stirring system 9, heating system 10, detecting system 11, discharge system 12 and its
His accessory system 13;In actual motion, pretreatment system 1 can also be covered more and be used in combination with a set of exclusive use.
As shown in figure 3, the hydrothermal carbonization retort 2 is used to carry out hydrothermal carbonization reaction, including charging system 7, heating
System 10, stirring system 9, monitoring system 11, blowdown system 15, discharge system 12, other accessory systems 13 and cooling system
14.The aqueous solid product generated in hydrothermal carbonization retort 2 delivers to biological coal processing system after the cooling of cooling system 14
System 3 is used to produce biological coal finished product, and gaseous product (predominantly carbon dioxide, a small amount of steam and micro organic volatile composition) is logical
Cross blowdown system 15 and deliver to crop nutritive water processing system 5.In actual motion, two or more general hydro-thermals
Carburizing reagent tank 2 is used in combination, and the quantity of each system includes but is not limited to 1 set in hydrothermal carbonization retort 2.The hydro-thermal
Carburizing reagent tank 2 is made up of materials such as stainless steel or heat resistant plastices.
The biological coal processing system 3 is used for the processing of biological coal finished product, including solid-liquid separation system and baking
Dry systems.Wherein solid-liquid separation system is used for the separation of solid and liquid of the aqueous solid product generated in hydrothermal carbonization retort 2,
Solid material after separation processes biological coal by drying system, and liquid enters liquid processing system 4 or crop nutritive water
Processing system 5.The quantity of each system in biological coal processing system 3 includes but is not limited to 1 set.Separation of solid and liquid
Including but not limited to commercialized solid-liquid separation system, drying system are including but not limited to commercialized system at present at present
Drying system.
The liquid processing system 4 is used for the processing that liquid in system 3 is processed to biological coal, including but not limited to
Current commercialized micro-filtration (MF), ultrafiltration system (UF), nanofiltration system (NF) and counter-infiltration system (RO) etc., according to operation need
A set of or complete unit can be opened.
As shown in figure 4, the crop nutritive water processing system 5 includes charging system 7, crop nutritive water retort 16
With processing system 18, stirring system 9, heating system 10, monitoring system are provided with the crop nutritive water retort 16
System 11, discharge system 12, other accessory systems 13, gas handling system 17 and blowdown system 15.Processed in the crop nutritive water
In production system 5, the liquid from liquid processing system 4 or biological coal processing system 3 is entered by charging system 7 to be made
Thing nutritive water retort 16, meanwhile, the gas from hydrothermal carbonization retort 2 enters crop nutritive water by gas handling system 17
Retort 16;Material caused by crop nutritive water retort 16 enters processing system 18 by discharge system 12 and processes life
Crop nutritive water is produced, gas discharges after being handled by the collection of blowdown system 15, and the final gas discharge of whole technological process is basic
It is carbon dioxide.In actual motion, crop nutritive water processing system 5 can be used in combination with one or more sets, crop nutritive water
The quantity of each system includes but is not limited to 1 set in processing system 5.
Crushing system 6 includes but is not limited to the modes such as hand breaking, Mechanical Crushing.
Charging system 7 is used for the addition of material, including but not limited to artificial, forklift, transmission belt, pumping etc..
Prepare tank 8 to be made up of materials such as stainless steel or heat resistant plastices, the pretreatment of mixing and preheating for material etc..
Stirring system 9 is used for the mixing of material, including but not limited to artificial, mechanical agitation, pump circulation stirring, pneumatically stirs
The mode such as mix.
Heating system 10 is used for the heating of material, the including but not limited to mode such as steam heating, electrical heating, oil heating.
Monitoring system 11 is used for the monitoring of associated control parameters in retort, including but not limited to level monitoring, temperature
Monitoring and sample tap and peep hole with the chemical measurements of water such as pH etc..
Discharge system 12 is used for the transfer of differential responses tank, different system material, can be any side such as artificial, machinery
Formula, including but not limited to forklift, transmission belt, pump etc..
Other accessory systems 13 include but is not limited to Butterworth Hatch, staff's mouth, acid solution or lye import etc..
Cooling system 14 is used for the cooling of material in hydrothermal carbonization retort 2, the including but not limited to side such as water cooling, oil cooling
Formula.
Blowdown system 15 is used for the emptying of gas material in retort, including but not limited to the emptying side such as artificial, machinery
Formula.
Crop nutritive water retort 16 is made up of materials such as stainless steel or common plastics, for carrying out biochemical reaction.
The subsequent production that processing system 18 is used for crop nutritive water is processed, such as product proportioning, packaging, storage etc..
In actual motion, the quantity of processing system 18 includes but is not limited to 1 set.
As shown in figure 1, the various organic wastes containing organic carbon such as house refuse, stalk pass through in pretreatment system 1
After crossing the processing such as broken, mixing and heating, carried out into hydrothermal carbonization retort 2 with hydrothermal carbonization catalytic reaction, subsequently into
Biological coal processes system 3, and solid produces biological coal as Raw material processing, and liquid is (micro- directly or through liquid processing system
Filter membrane) 4 processing after, into crop nutritive water process system 5.
The organic waste treatment technique of present invention coupling hydrothermal carbonization and biochemical reaction principle is as follows:
1st, pre-process
Organic waste is entered by charging system 7 after the break process of crushing system 6 and prepares tank 8, is preparing tank 8
Interior heating simultaneously mixes, and pretreated material is obtained, to reach the feed conditions of hydrothermal carbonization retort 2;The pretreated material
Temperature >=50 DEG C, water content >=30%, material size<125cm3。
2nd, hydrothermal carbonization reacts
The pretreated material is sent into hydrothermal carbonization retort 2 by charging system 7, carries out hydrothermal carbonization reaction,
The aqueous solid product of generation through cooling system 14 cooling after deliver to biological coal processing system 3, gas be cooled to 50 DEG C with
Crop nutritive water processing system 5 is delivered to after lower.Hydrothermal carbonization reaction design parameter is as follows:Temperature is 80-400 DEG C, pressure
For 0-30 MPa, pH is that 2-9 (passes through C<5 small molecular organic acid regulation pH value, such as formic acid, acetic acid).
3rd, the production of biological coal
The aqueous solid product generated in hydrothermal carbonization retort 2 carries out separation of solid and liquid through solid-liquid separation system, after separation
Solid material by drying system process biological coal (30-200 DEG C of drying temperature), liquid material be cooled to 70 DEG C with
Enter liquid processing system 4 or crop nutritive water processing system 5 after lower (for liquid material, if necessary to enter hydro-thermal
Carburizing reagent tank reuse, then need to be handled into liquid processing system 4, if work will not can be directly entered if reuse
Thing nutritive water processes system).
4th, liquid handling
The liquid material obtained after step 3 separation of solid and liquid is filtered by membrane filtration system, by the non-solubilised state in liquid
Larger molecular organicses are collected, and deliver to and raw material is used as in hydrothermal carbonization retort 2, and filtrate delivers to the processing of crop nutritive water
System 5.The membrane filtration system includes micro-filtration (MF), ultrafiltration system (UF), nanofiltration system (NF), counter-infiltration system (RO) etc.
In one or more.
5th, biochemical reaction
The filtrate and step 2 that the liquid material and/or step 4 that step 3 obtains obtain react caused gas and deliver to work
Biochemical reaction is carried out in thing nutritive water retort 16, the material obtained after biochemical reaction is crop nutritive water, and gas is through collecting
Discharged after processing.The final gas discharge of whole technological process is substantially carbon dioxide.Biochemical reaction major parameter is as follows:Temperature
20-70 DEG C, pH value 3-9 of degree, and add the mixed bacterial being made up of aerobic flora and oxygen flora and anaerobic bacteria flora.Added
Mixed bacterial can be the sludge of sewage treatment plant or the bed mud etc. in river course.
The ratio of gas and liquid need not be controlled in biochemical reaction process, the simultaneous reactions time also without control, leads to
It is often that can be determined according to product purpose 3-200 hours.
The crop nutritive water organic carbon content 1-30% that the present invention obtains, total nutrient NPK0.1-10%, small molecular organic acid
Class (C<5) microorganism based on, aerobic and oxygen mixes group's 1000-1000000000/ milliliters, with reaction time and storage of producing
Time change.
Claims (10)
1. a kind of couple hydrothermal carbonization and the organic refuse treatment appts of biochemical reaction principle, it is characterised in that:Including pre- place
Reason system (1), hydrothermal carbonization retort (2), biological coal processing system (3), liquid processing system (4) and crop nutritive water
Processing system (5);
The pretreatment system (1) is used to crush organic waste, mixed and heat etc. to pre-process, and material is met water
The feed conditions of hot carburizing reagent tank (2);
The hydrothermal carbonization retort (2) is used to carry out hydrothermal carbonization reaction;
The biological coal processing system (3) is used for the processing of biological coal finished product, including solid-liquid separation system and drying
System;
Processing of the liquid processing system (4) for processing liquid in system (3) to biological coal, including microfiltration systems,
One or more in ultrafiltration system, nanofiltration system and counter-infiltration system;
The crop nutritive water processing system (5) includes charging system (7), crop nutritive water retort (16) and processing life
Production system (18).
2. device according to claim 1, it is characterised in that:
The pretreatment system (1) includes crushing system (6), charging system (7) and prepares tank (8), in the preparation tank (8)
It is provided with stirring system (9), heating system (10), detecting system (11), discharge system (12) and other accessory systems (13).
3. device according to claim 1, it is characterised in that:
The hydrothermal carbonization retort (2) includes charging system (7), heating system (10), stirring system (9), monitoring system
(11), blowdown system (15), discharge system (12), other accessory systems (13) and cooling system (14);Hydrothermal carbonization retort
(2) the aqueous solid product of generation delivers to biological coal processing system (3) after cooling system (14) cooling and is used to produce in
Biological coal finished product, gaseous product deliver to crop nutritive water by blowdown system (15) and process system (5).
4. device according to claim 1, it is characterised in that:
Solid-liquid separation system is used to contain generation in hydrothermal carbonization retort (2) in the biological coal processing system (3)
The separation of solid and liquid of water solid product, the solid material after separation process biological coal by drying system, and liquid enters liquid
Processing system (4) or crop nutritive water processing system (5).
5. device according to claim 1, it is characterised in that:
Be provided with the crop nutritive water retort (16) stirring system (9), heating system (10), monitoring system (11),
Discharge system (12), other accessory systems (13), gas handling system (17) and blowdown system (15).
6. device according to claim 1 or 5, it is characterised in that:
In crop nutritive water processing system (5), from liquid processing system (4) or biological coal processing system
3 liquid enters crop nutritive water retort (16) by charging system (7), meanwhile, the gas from hydrothermal carbonization retort (2)
Body enters crop nutritive water retort (16) by gas handling system (17);Material caused by crop nutritive water retort (16) passes through
Discharge system (12) enter processing system (18) processing crop nutritive water, gas by blowdown system (15) collection at
Discharged after reason.
7. a kind of organic waste treatment technique for coupling hydrothermal carbonization and biochemical reaction principle, it is characterised in that including following step
Suddenly:
Step 1:Pretreatment
Organic waste is entered by charging system after crushing system break process and prepares tank, is preparing to heat simultaneously in tank
Mix, pretreated material is obtained, to reach the feed conditions of hydrothermal carbonization retort;
Step 2:Hydrothermal carbonization reacts
The pretreated material is sent into hydrothermal carbonization retort by charging system, carries out hydrothermal carbonization reaction, generation
Aqueous solid product delivers to biological coal processing system after cooling system cools down, and gas delivers to work after being cooled to less than 50 DEG C
Thing nutritive water processes system;
Step 3:The production of biological coal
The aqueous solid product generated in hydrothermal carbonization retort carries out separation of solid and liquid, the solid after separation through solid-liquid separation system
Material processes biological coal by drying system, and liquid material enters liquid processing system 4 or made after being cooled to less than 70 DEG C
Thing nutritive water processes system;
Step 4:Liquid handling
The liquid material obtained after step 3 separation of solid and liquid is filtered by membrane filtration system, the non-solubilised state in liquid is divided greatly
Sub- organic matter is collected, and delivers to and raw material is used as in hydrothermal carbonization retort, and filtrate delivers to crop nutritive water processing system;
Step 5:Biochemical reaction
The filtrate and step 2 that the liquid material and/or step 4 that step 3 obtains obtain react caused gas and deliver to crop battalion
Support and biochemical reaction is carried out in water retort, the material obtained after biochemical reaction is crop nutritive water, and gas is after collection is handled
Discharge.
8. handling process according to claim 7, it is characterised in that:
In step 1, temperature >=50 DEG C of the pretreated material, water content >=30%, material size<125cm3。
9. handling process according to claim 7, it is characterised in that:
In step 2, hydrothermal carbonization reaction design parameter is as follows:Temperature is 80-400 DEG C, pressure 0-30MPa, pH value 2-9.
10. handling process according to claim 7, it is characterised in that:
In step 5, biochemical reaction major parameter is as follows:20-70 DEG C of temperature, pH value 3-9, and add by aerobic flora and oxygen bacterium
The mixed bacterial that group and anaerobic bacteria flora are formed.
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110842010A (en) * | 2019-11-27 | 2020-02-28 | 山东百川同创能源有限公司 | Clean energy regeneration treatment process for high-viscosity organic waste |
CN111282974A (en) * | 2020-03-23 | 2020-06-16 | 深圳垚鑫淼环境科技有限公司 | Treatment method and treatment system for kitchen waste |
US11414962B2 (en) * | 2020-09-08 | 2022-08-16 | Frederick William MacDougall | Coalification and carbon sequestration using deep ocean hydrothermal borehole vents |
US11794893B2 (en) | 2020-09-08 | 2023-10-24 | Frederick William MacDougall | Transportation system for transporting organic payloads |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE102012002590A1 (en) * | 2012-02-13 | 2013-08-14 | Ava-Co2 Schweiz Ag | Treating process water obtained from a hydrothermal carbonization process, comprises supplying the process water charged with working pressure into membrane, which divides process water into permeate emerging through membrane, and retentate |
CN103722002A (en) * | 2014-01-23 | 2014-04-16 | 杭州互惠环保科技有限公司 | Domestic waste comprehensive treatment method based on anaerobic digestion and hydrothermal carbonization |
CN105950251A (en) * | 2016-05-12 | 2016-09-21 | 华南理工大学 | Garden rubbish utilization method based on hydrothermal carbonization and solid biomass fuel |
CN206244619U (en) * | 2016-10-26 | 2017-06-13 | 深圳先进技术研究院 | A kind of sludge treating system based on hydrothermal carbonization |
CN107129028A (en) * | 2017-05-18 | 2017-09-05 | 珠海汇东环保科技有限公司 | A kind of supporting processing hydrothermal carbonization system off gas and waste water and the method for producing crop nutritive water |
CN207375999U (en) * | 2017-10-11 | 2018-05-18 | 珠海汇东环保科技有限公司 | A kind of organic refuse treatment appts for coupling hydrothermal carbonization and biochemical reaction principle |
-
2017
- 2017-10-11 CN CN201710939825.3A patent/CN107603644A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE102012002590A1 (en) * | 2012-02-13 | 2013-08-14 | Ava-Co2 Schweiz Ag | Treating process water obtained from a hydrothermal carbonization process, comprises supplying the process water charged with working pressure into membrane, which divides process water into permeate emerging through membrane, and retentate |
CN103722002A (en) * | 2014-01-23 | 2014-04-16 | 杭州互惠环保科技有限公司 | Domestic waste comprehensive treatment method based on anaerobic digestion and hydrothermal carbonization |
CN105950251A (en) * | 2016-05-12 | 2016-09-21 | 华南理工大学 | Garden rubbish utilization method based on hydrothermal carbonization and solid biomass fuel |
CN206244619U (en) * | 2016-10-26 | 2017-06-13 | 深圳先进技术研究院 | A kind of sludge treating system based on hydrothermal carbonization |
CN107129028A (en) * | 2017-05-18 | 2017-09-05 | 珠海汇东环保科技有限公司 | A kind of supporting processing hydrothermal carbonization system off gas and waste water and the method for producing crop nutritive water |
CN207375999U (en) * | 2017-10-11 | 2018-05-18 | 珠海汇东环保科技有限公司 | A kind of organic refuse treatment appts for coupling hydrothermal carbonization and biochemical reaction principle |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110842010A (en) * | 2019-11-27 | 2020-02-28 | 山东百川同创能源有限公司 | Clean energy regeneration treatment process for high-viscosity organic waste |
CN111282974A (en) * | 2020-03-23 | 2020-06-16 | 深圳垚鑫淼环境科技有限公司 | Treatment method and treatment system for kitchen waste |
US11414962B2 (en) * | 2020-09-08 | 2022-08-16 | Frederick William MacDougall | Coalification and carbon sequestration using deep ocean hydrothermal borehole vents |
US11794893B2 (en) | 2020-09-08 | 2023-10-24 | Frederick William MacDougall | Transportation system for transporting organic payloads |
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