CN203999290U - Sewage sludge advanced treatment apparatus - Google Patents
Sewage sludge advanced treatment apparatus Download PDFInfo
- Publication number
- CN203999290U CN203999290U CN201420437914.XU CN201420437914U CN203999290U CN 203999290 U CN203999290 U CN 203999290U CN 201420437914 U CN201420437914 U CN 201420437914U CN 203999290 U CN203999290 U CN 203999290U
- Authority
- CN
- China
- Prior art keywords
- mud
- heat
- vaporizer
- air
- drying installation
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Withdrawn - After Issue
Links
Landscapes
- Drying Of Solid Materials (AREA)
- Treatment Of Sludge (AREA)
Abstract
The utility model discloses a kind of sewage sludge advanced treatment apparatus, comprise shredder assembly, drying installation, incinerator and waste heat boiler, also comprise mud freezing container and lyophilize energy cycle system, lyophilize energy cycle system comprises compressor, vaporizer, condenser and is arranged at the First Heat Exchanger in mud freezing container, compressor outlet side is connected with condenser, and vaporizer is connected with the inlet end of compressor through First Heat Exchanger; Condenser is connected by gas pipeline and drying installation bottom, vaporizer with by gas pipeline, be connected with drying installation top.In waste heat boiler, be provided with heat-conducting oil pipes, heat-conducting oil pipes and air carry out heat and transmit air heating, and the air after heating is inputted respectively drying installation and mud freezing container, for drying sludge with thaw.The utility model need not add chemicals, does not increase mud handling capacity, the recycle of working medium energy and utilize mud self heat to improve freezing efficiency and the heat utilization ratio of mud.
Description
Technical field
The utility model relates to sewage sludge process field, specifically a kind of sewage sludge advanced treatment apparatus.
Background technology
In sewage treatment process, produce a large amount of mud, its quantity accounts for the 0.3%-0.5% that processes the water yield, processing investment and the running cost of mud are very huge, generally account for the 20%-50% of sewage work's working cost for the expense of sludge treatment, to sewage disposal, have brought white elephant.The method of sludge treatment mainly contains conditioning, dehydration, dry, then burns, the Disposal Measures such as landfill, recycling.Sludge dewatering is the very important ring of sludge treatment, and for mud, follow-up processing is disposed and had vital role.The key of sludge dewatering is to improve the dewatering of mud, current traditional treatment process is by adding flocculation agent and lime is first nursed one's health, then enter pressure filter and carry out mechanical dehydration, the mud outward transport that forms water ratio 60% left and right is dried, burning etc.Adding flocculation agent pretreatment process is the throwing out by flocculation agent, reduced the avidity of mud and water, changed the existence form of moisture in mud, in and sewage in contrary electric charge, compression double electric layer, plays adsorption bridging to de-steady flocculated particle, makes it form fast large flco, thereby make elimination of colloid stability cohesion, realize solid-liquid separation.Flocculant dosage is to account for the per-cent of sewage sludge solid dry weight, and different flocculant dosages can be distinguished to some extent.Although can significantly improve the dewatering of mud by adding the method for flocculation agent, but due to a large amount of flocculation agent of needs, not only increase the cost of sludge treatment, and a large amount of flocculation agents can be increased in the mud after dehydration, strengthen the treatment capacity of mud, and the lime adding is alkalescence, for follow-up drying and incinerating equipment, there is certain corrosive nature, according to practical experience, for the mud that adds flocculation agent and lime, to burn, the incinerator life-span can decline.And the amount of heat that other pretreatment processs need to consume as ultrasonic wave, microwave treatment, and need to set up corresponding treatment unit; Adopt biological process and thermodynamic method need to consume a large amount of biotechnological formulations and heat.
Adopt freezing method to carry out pre-treatment in early stage to mud, mud is through destroying the bonding force of mud and water and destroy the structure (be similar to freezing after built-in bean curd) of colloid after repeatedly freezing, make elimination of colloid stability cohesion and membranolysis, make out to form the easily interstitial water to remove of mechanical means with the cell interior water dialysis that mechanical means is difficult to remove, the rapid sedimentation of mud granule, dewatering speed is front higher tens times than freezing, adopt freezing method not add medicament, can save reagent cost, and can additionally not increase the mud handling capacity in later stage, simultaneously, also not impact of life-span for subsequent processing device.In conjunction with mud method for subsequent processing, complete sludge deep minimizing and process again.
Yet, the freezing main dependence physical environment of prior art to mud, mud being placed in to outdoor dependence physical environment under arctic weather is cooled to-10 ℃ of left and right and carries out freezing and thaw, but low, the consuming time length of efficiency, if and just in southern area or cannot operate in situation non-winter, natural condition require comparatively harsh.In addition, prior art is used external force carry out freezing and thaw and need to freeze and heat dual energy mud mud, and the waste gas of incineration organic efficiency after drying sludge is not high, and cost is very high, therefore be difficult to apply.
Utility model content
In view of this, the problem that increase flocculation agent can increase mud handling capacity and freezing efficiency is low, the waste gas of incineration rate of recovery is low that the utility model exists for above-mentioned prior art, provide a kind for the treatment of processes can not increase mud handling capacity, the sewage sludge advanced treatment apparatus that freezing efficiency is high and capacity usage ratio is high.
Technical solution of the present utility model is, a kind of sewage sludge advanced treatment apparatus of following structure is provided, comprise filter-pressing device, shredder assembly, drying installation, incinerator and waste heat boiler, filter-pressing device carries out by shredder assembly, carrying out break process after press filtration processing to mud, after sludge crushing, enter drying installation and carry out drying treatment, dried mud granule is sent in incinerator and is burned, and burns the high-temperature flue gas producing and enters waste heat boiler;
Described sewage sludge treatment unit also comprises mud freezing container and lyophilize energy cycle system, described lyophilize energy cycle system comprises compressor, vaporizer, condenser and is arranged at the First Heat Exchanger in mud freezing container, the outlet side of compressor is connected with condenser, condenser is connected with vaporizer through throttling element, and vaporizer is connected with the inlet end of compressor through First Heat Exchanger; Described condenser is connected with drying installation bottom by gas pipeline, and vaporizer is connected with drying installation top by gas pipeline, and described condenser is connected by gas pipeline with vaporizer simultaneously;
In described waste heat boiler, be provided with heat-conducting oil pipes, heat-conducting oil pipes and air carry out heat and transmit air heating, and the air after heating is inputted respectively drying installation and mud freezing container, for drying sludge with thaw.
Adopt above structure, the utility model compared with prior art, have the following advantages: adopt the utility model, utilized lyophilize energy cycle system, realized the freezing of mud in freezing container and being dried mud in drying installation simultaneously, working medium is under compressor effect, output High Temperature High Pressure gaseous working medium, through condenser, heat in working medium is by absorption of air, transfer heat to air, air themperature raises, Temperature of Working reduces, warm air passes in drying installation material is dried, working medium is condensed and becomes high-pressure liquid, high-pressure liquid working medium becomes low-pressure liquid working medium after throttling element step-down, low-pressure liquid working medium enters into vaporizer, absorb the air heat (from material top air out) in vaporizer, to air cooling-down, after saturated air cooling, the moisture that it can hold reduces, unnecessary hydrogenesis becomes liquid water to drain by the water accumulating disc of vaporizer, after working medium heat absorption, from low-pressure liquid, become low pressure gaseous state (insufficient if working medium absorbs the heat of air, the working medium that can only guarantee operative liquid flashes to gaseous working medium, and the liquid refrigerant of remainder and gaseous working medium form two-phase working substance) enter into First Heat Exchanger, working medium absorbs the heat of mud in First Heat Exchanger, mud is cooled to needed freezing temp-10 ℃~-15 ℃ (this temperature range is better, but be not limited to this numerical range), now liquid working substance is gasificated into gaseous working medium, gaseous working medium enters in compressor.Mud is through repeatedly freezing and thaw (thaw and can naturally thaw) in mud freezing container, destroyed the structure of mud, mud through thawing enters filter-pressing device, filter-pressing device is pressed into bulk pie mud by mud, send into again shredder assembly and carry out fragmentation formation mud granule, mud granule is dried in drying installation, has realized the stage of mud and has processed.Due to without adding chemicals in mud, therefore treating processes can not increase mud handling capacity, the recycle of working medium energy has improved the freezing efficiency of mud greatly; Only need by a small amount of compressor energy of cost, working medium can be by the heat " carrying " that is several times as much as energy consumption of compressor in freezing container in loft drier, realize the freezing and drying sludge of mud simultaneously, solved the cold source of freezing needs, solved again the origin of heat of dry needs, make cold and heat reach an extraordinary balance, greatly improved heat service efficiency, energy-saving effect is obvious; Meanwhile, the heat in waste heat boiler is recovered for thawing of mud and being dried of mud granule, has further promoted capacity usage ratio.
As preferably, waste heat boiler is extended at the two ends of heat-conducting oil pipes, and is connected with the second interchanger, and thermal oil enters the second interchanger and transfers heat to air; Air after the device that is condensed heating enters into the second interchanger and continues to absorb heat, forms high temperature air, and high temperature air, after blower fan pressurization, enters drying installation and mud freezing container by hot gas duct respectively.Thereby the heat in waste heat boiler is thawed for mud and mud granule dry.
As preferably, described mud freezing container is a plurality of, First Heat Exchanger is corresponding one by one with mud freezing container, the two ends of the First Heat Exchanger in a plurality of mud freezing containers are connected with compressor with vaporizer by working medium reversing valve respectively, the bottom of mud freezing container is provided with filtration, and the bottom of a plurality of mud freezing containers is communicated with filter-pressing device by liquid reversing valve and through fluid pipeline.Like this, the mud in a mud freezing container carry out freezing in, the mud of part mud freezing container carries out nature and thaws, what thawed is directly delivered in filter-pressing device, thereby improves processing efficiency, can produce continuously.
As preferably, described drying installation comprises loft drier and mud panel turnover mechanism, described mud panel turnover mechanism, and level is arranged on the vertical height of difference in loft drier, described mud panel turnover mechanism is staggered, and a mud panel turnover mechanism of bottommost layer stretches out outside loft drier.Like this, mud enters drying installation after fragmentation, first fall into the mud panel turnover mechanism the superiors, transmission along with mud panel turnover mechanism, mud drops on the mud panel turnover mechanism of lower one deck, the mud panel turnover mechanism of lower one deck commutates and drives to other one end, and so forth, can realize warm air and contact up and down with mud, omnibearing dry, improve drying effect, when dropping down onto a mud panel turnover mechanism of bottommost layer, because it stretches out outside loft drier, mud is sent to outside loft drier by it, enters next step operation and processes.
As preferably, described filter-pressing device is plate-and-frame filter press, plate-and-frame filter press comprises a plurality of sheet frames, below sheet frame, be provided with drawing-plate mechanism, described drawing-plate mechanism comprises polylith guiding piece and slide plate, is provided with articulated linkage, and is equipped with roller between adjacent two guiding pieces under every guiding piece, described polylith guiding piece is placed on slide plate, and can be rolled and be connected with slide plate by roller.Like this, by polylith drawing-plate mechanism, carry out pull, can realize the pull of a plurality of sheet frames, solved the current problem of a sheet frame of pull simultaneously, shorten the arm-tie time, improved the efficiency of press filtering of filter-pressing device.
As preferably, described waste heat boiler is provided with smoke eliminator, and described smoke eliminator removes the sour gas in flue gas and traps the particulate matter in flue gas.
Accompanying drawing explanation
Fig. 1 is sewage sludge advanced treatment apparatus schematic diagram of the present utility model;
Fig. 2 is the structural representation of drawing-plate mechanism.
As shown in the figure, 1, filter-pressing device, 1.1, sheet frame, 1.2, guiding piece, 1.3, slide plate, 1.4, articulated linkage, 1.5, roller, 2, shredder assembly, 3, drying installation, 3.1, loft drier, 3.2, mud panel turnover mechanism, 4, mud freezing container, 5, compressor, 6, vaporizer, 7, condenser, 8, First Heat Exchanger, 9, throttling element, 10, gas pipeline, 11, working medium reversing valve, 12, filtration, 13, liquid reversing valve, 14, fluid pipeline, 15, rotor pump, 16, incinerator, 17, waste heat boiler, 18, heat-conducting oil pipes, 19, the second interchanger, 20, hot gas duct, 21, smoke eliminator, 22, flue, 23, transfer mechanism, 24, blower fan.
Embodiment
Below in conjunction with the drawings and specific embodiments, the utility model is described in further detail.
As shown in the figure, a kind of sewage sludge treatment unit of the present utility model, comprise filter-pressing device 1, shredder assembly 2, drying installation 3, incinerator 16 and waste heat boiler 17,1 pair of mud of filter-pressing device carries out by shredder assembly 2, carrying out break process after press filtration processing, after sludge crushing, enter drying installation 3 and carry out drying treatment, dried mud granule is sent into the interior burning of incinerator 16 (entering incinerator by transfer mechanism 23 from the feed opening of drying installation), burns the high-temperature flue gas producing and enters waste heat boiler 17;
Described sewage sludge treatment unit also comprises mud freezing container 4 and lyophilize energy cycle system, described lyophilize energy cycle system comprises compressor 5, vaporizer 6, condenser 7 and is arranged at the First Heat Exchanger 8 in mud freezing container 4, the outlet side of compressor 5 is connected with condenser 6, condenser 7 is connected with vaporizer 6 through throttling element 9, and vaporizer 6 is connected with the inlet end of compressor 5 through First Heat Exchanger 8; Described condenser 7 is connected with drying installation 3 bottoms by gas pipeline 10, and vaporizer 6 is connected with drying installation 3 tops by gas pipeline 10, and described condenser 7 is connected by gas pipeline 10 with vaporizer 6 simultaneously;
In described waste heat boiler 17, be provided with heat-conducting oil pipes 18, heat-conducting oil pipes 8 carries out heat with air and transmits air heating, and the air after heating is inputted respectively drying installation 3 and mud freezing container 4, for mud be dried and thaw.
Waste heat boiler 17 is extended at the two ends of heat-conducting oil pipes 18, and is connected with the second interchanger 19, and thermal oil enters the second interchanger 19 and transfers heat to air; The air being condensed after device 7 heating enters into the second interchanger 19 and continues to absorb heat, forms high temperature air, and high temperature air, after blower fan 24 pressurizations, enters drying installation 3 and mud freezing container 4 by hot gas duct 20 respectively.
Described mud freezing container 4 is a plurality of, First Heat Exchanger 8 is corresponding one by one with mud freezing container 4, the two ends of the First Heat Exchanger 8 in a plurality of mud freezing containers 4 are connected with compressor 5 with vaporizer 6 by working medium reversing valve 11 respectively, the bottom of mud freezing container 4 is provided with filtration 12, and the bottom of a plurality of mud freezing containers 4 is passed through liquid reversing valve 13 and is communicated with filter-pressing device 1 through fluid pipeline 14; Mud after thawing pumps into filter-pressing device 1 by rotor pump 15 from mud freezing container 4.
Described drying installation 3 comprises loft drier 3.1 and mud panel turnover mechanism 3.2, described mud panel turnover mechanism, level is arranged on the vertical height of difference in loft drier 3.1, and described mud panel turnover mechanism 3.2 is staggered, and a mud panel turnover mechanism 3.2 of bottommost layer stretches out outside loft drier 3.1.
Described filter-pressing device 1 is plate-and-frame filter press, plate-and-frame filter press comprises a plurality of sheet frames 1.1, below sheet frame 1.1, be provided with drawing-plate mechanism, described drawing-plate mechanism comprises polylith guiding piece 1.2 and slide plate 1.3, between adjacent two guiding pieces 1.2, be provided with articulated linkage 1.4, and being equipped with roller 1.5 1.2 times at every guiding piece, described polylith guiding piece 1.2 is placed on slide plate 1.3, and can be rolled and be connected with slide plate 1.3 by roller 1.5.
High-temperature gas enters waste heat boiler 17 by flue 22, and described waste heat boiler 17 is provided with smoke eliminator 21, and described smoke eliminator 21 removes the sour gas in flue gas and traps the particulate matter in flue gas.
Sludge deep process flow is:
1) in freezing temp-10 ℃~-15 ℃, freezing time, carry out repeatedly under 72 hours freezing;
2) between 20-50 ℃, thaw (can adopt normal temperature unfreezing), thawing time is about 6 hours;
3) in plate-and-frame filter press, carry out mechanical dehydration, first it is the press filtration stage, press filtration pressure is 1.0-1.2Mpa, time of filter pressing is 1.5-2 hour, moisture percentage in sewage sludge 65%-70% now, then enter into the press dewatering stage, squeeze pressure is 1.5Mpa, the squeezing time is 1 hour, now the about 60%-65% of moisture percentage in sewage sludge;
4) plate-and-frame filter press bulk mud cake shape mud is out carried out to fragmentation in mud mixing shredder assembly, form little mud granule, mud granule size is generally in 20mm left and right;
5) mud after fragmentation is delivered in drying installation and is dried, drying installation is Multi-layer panel-turnover, and be 1 hour time of drying, drying temperature 60-100 ℃, after super-dry, the water ratio of mud is 10%-15%, and now vaporizer provides cold to mud freezing container;
6) mud through super-dry is sent to incinerator and burns, 850 ℃ of flue gases of generation are discharged and are entered into waste heat boiler by flue;
7) in waste heat boiler, high-temperature flue gas transfers heat to thermal oil, and thermal oil is heated to 250 ℃ of left and right, and thermal oil enters into the second interchanger and transfers heat to air, air is heated, and the air after heating enters in drying installation mud is dried;
8) smoke eliminator of Heat Treatment device gas outlet setting removes the trapping with particulate matter to sour gas, makes the flue gas of discharging atmosphere meet environmental requirement.
Specific works principle is as follows:
Mud enters into mud freezing container, first under First Heat Exchanger effect, refrigeration working medium enter into First Heat Exchanger in, working medium is absorbed heat to mud, make the freezing temp of mud reach specified temperature, mud under-10 ℃~-15 ℃, freezing time 72 hours through repeatedly freezing, destroy the bonding force of mud and water and the structure of destruction colloid, make elimination of colloid stability cohesion and membranolysis, the rapid sedimentation of mud granule, dewatering significantly improves, and dewatering speed is front higher tens times than freezing, freezing end.Now, working medium reversing valve flows to and to commutate working medium, and working medium flow-reversal, in another mud freezing container, has now been passed into the air with certain temperature in freezing mud freezing container and thawed, air themperature is between 20-50 ℃, and thawing time is 6 hours.
After thawing, mud passes through fluid pipeline, enter rotor pump, in adding of rotor pump, depress and enter board and frame machine (plate-and-frame filter press) and start press filtration and carry out mechanical dehydration, after press filtration after a while, pull open sheet frame, the mud of mud cake shape drops in device for transporting objects, through device for transporting objects, be transported to crusher, crusher carries out fragmentation to mud cake, form little mud granule, mud granule size remains on 20mm left and right, become short grained mud to improve the specific surface area of mud, be beneficial to the contact area that increases mud and high temperature air in dry, improve drying rate and effect.
Little mud granule enters into the upper strata turnover panel in drying machine, drops from level to level from top to down, and in the process dropping, constantly upset of mud, all fully contacts each surface with air.Dry air contacts with mud from bottom to top, absorption of air the moisture of mud become the wet air that humidity is very high and after vaporizer, drop to below dew point, separate out moisture, the moisture of separating out is discharged through water accumulating disc, air continues to be heated after condenser, enters in loft drier mud is dried.Mud leaves loft drier after being heated and being dried after basecoat turnover panel.
Mud is transported to incinerator by device for transporting objects after leaving loft drier, adjusting enters a wind of combustion chamber, under refiner effect, make it in fluidized bed combustion state, because the medium in fluidized-bed is in suspended state, gas-solid can fully mix contact, in whole stove, the temperature of burning zone is comparatively even, and the approximately 850 ℃ of discharges of waste gas that produce after burning enter into waste heat boiler.Meanwhile, the thermal oil in waste heat boiler is heated to 250 ℃ by 220 ℃, and the thermal oil after being heated heats air by the second interchanger, and the air after heating enters into dehumidification system and thawing apparatus to drying sludge and the heat supply of thawing.Gas-cleaning installation is comprised of removing with particle collection two parts of sour gas, gas sweetening can adopt semidrying, in flue gas, spray into certain calcium oxide, make it to react with the acidic substance in flue gas, and by spraying plant, control moisture and reach spray-dired reaction process.Depickling reactant is essentially solid state, there will not be discharge of wastewater.In flue gas, particle collection can be realized in conjunction with cyclonic separator or cloth bag by filtering net, sprays into a certain amount of activated carbon grain powder before, the objectionable impuritiess such as absorption heavy metal in flue gas and Dioxins.Through purified gas, can discharge atmosphere, environmental pollution is few.
Below only with regard to the utility model preferred embodiment, be described, but can not be interpreted as it is limitations on claims.The utility model is not only confined to above embodiment, and its concrete structure allows to change.In a word, all various variations of doing in the protection domain of the utility model independent claim are all in protection domain of the present utility model.
Claims (6)
1. a sewage sludge advanced treatment apparatus, comprise filter-pressing device (1), shredder assembly (2), drying installation (3), incinerator (16) and waste heat boiler (17), filter-pressing device (1) carries out by shredder assembly (2), carrying out break process after press filtration processing to mud, after sludge crushing, enter drying installation (3) and carry out drying treatment, dried mud granule is sent in incinerator (16) and is burned, and burns the high-temperature flue gas producing and enters waste heat boiler (17); It is characterized in that:
Described sewage sludge advanced treatment apparatus also comprises mud freezing container (4) and lyophilize energy cycle system, described lyophilize energy cycle system comprises compressor (5), vaporizer (6), condenser (7) and is arranged at the First Heat Exchanger (8) in mud freezing container (4), the outlet side of compressor (5) is connected with condenser (7), condenser (7) is connected with vaporizer (6) through throttling element (9), and vaporizer (6) is connected with the inlet end of compressor (5) through First Heat Exchanger (8); Described condenser (7) is connected with drying installation (3) bottom by gas pipeline (10), vaporizer (6) is connected with drying installation (3) top by gas pipeline (10), and described condenser (7) is connected by gas pipeline (10) with vaporizer (6) simultaneously;
In described waste heat boiler (17), be provided with heat-conducting oil pipes (18), heat-conducting oil pipes (8) carries out heat with air and transmits air heating, air after heating is inputted respectively drying installation (3) and mud freezing container (4), for drying sludge and thawing.
2. sewage sludge advanced treatment apparatus according to claim 1, it is characterized in that: waste heat boiler (17) is extended at the two ends of heat-conducting oil pipes (18), and be connected with the second interchanger (19), thermal oil enters the second interchanger (19) and transfers heat to air; Air after the device (7) that is condensed heating enters into the second interchanger (19) and continues to absorb heat, form high temperature air, high temperature air, after blower fan (24) pressurization, enters drying installation (3) and mud freezing container (4) by hot gas duct (20) respectively.
3. sewage sludge advanced treatment apparatus according to claim 1, it is characterized in that: described mud freezing container (4) is for a plurality of, First Heat Exchanger (8) is corresponding one by one with mud freezing container (4), the two ends of the First Heat Exchanger (8) in a plurality of mud freezing containers (4) are connected with compressor (5) with vaporizer (6) by working medium reversing valve (11) respectively, the bottom of mud freezing container (4) is provided with filtration (12), the bottom of a plurality of mud freezing containers (4) is passed through liquid reversing valve (13) and is communicated with filter-pressing device (1) through fluid pipeline (14), mud after thawing pumps into filter-pressing device (1) by rotor pump (15) from mud freezing container (4).
4. sewage sludge advanced treatment apparatus according to claim 1 and 2, it is characterized in that: described drying installation (3) comprises loft drier (3.1) and mud panel turnover mechanism (3.2), described mud panel turnover mechanism, level is arranged on the vertical height of difference in loft drier (3.1), described mud panel turnover mechanism (3.2) is staggered, and a mud panel turnover mechanism (3.2) of bottommost layer stretches out outside loft drier (3.1).
5. sewage sludge advanced treatment apparatus according to claim 1 and 2, it is characterized in that: described filter-pressing device (1) is plate-and-frame filter press, plate-and-frame filter press comprises a plurality of sheet frames (1.1), in sheet frame (1.1) below, be provided with drawing-plate mechanism, described drawing-plate mechanism comprises polylith guiding piece (1.2) and slide plate (1.3), between adjacent two guiding pieces (1.2), be provided with articulated linkage (1.4), and under every guiding piece (1.2), be equipped with roller (1.5), described polylith guiding piece (1.2) is placed on slide plate (1.3), and can roll and be connected with slide plate (1.3) by roller (1.5).
6. sewage sludge advanced treatment apparatus according to claim 2, it is characterized in that: described waste heat boiler (17) is provided with smoke eliminator (21), described smoke eliminator (21) removes the sour gas in flue gas and traps the particulate matter in flue gas.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201420437914.XU CN203999290U (en) | 2014-08-04 | 2014-08-04 | Sewage sludge advanced treatment apparatus |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201420437914.XU CN203999290U (en) | 2014-08-04 | 2014-08-04 | Sewage sludge advanced treatment apparatus |
Publications (1)
Publication Number | Publication Date |
---|---|
CN203999290U true CN203999290U (en) | 2014-12-10 |
Family
ID=52039320
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201420437914.XU Withdrawn - After Issue CN203999290U (en) | 2014-08-04 | 2014-08-04 | Sewage sludge advanced treatment apparatus |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN203999290U (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104098241A (en) * | 2014-08-04 | 2014-10-15 | 饶宾期 | Sewage sludge advanced treatment device |
CN104628238A (en) * | 2015-01-30 | 2015-05-20 | 山东宏力热泵能源股份有限公司 | Sludge drying equipment |
-
2014
- 2014-08-04 CN CN201420437914.XU patent/CN203999290U/en not_active Withdrawn - After Issue
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104098241A (en) * | 2014-08-04 | 2014-10-15 | 饶宾期 | Sewage sludge advanced treatment device |
CN104098241B (en) * | 2014-08-04 | 2015-12-02 | 中国计量学院 | Sewage sludge advanced treatment apparatus |
CN104628238A (en) * | 2015-01-30 | 2015-05-20 | 山东宏力热泵能源股份有限公司 | Sludge drying equipment |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN104098242B (en) | Sewage sludge deep treatment method | |
CN104140188B (en) | Energy-saving sewage sludge method for innocent treatment | |
CN104098241B (en) | Sewage sludge advanced treatment apparatus | |
CN104098239B (en) | sewage sludge treatment method | |
CN104785515B (en) | The indirect thermal desorption device of two-part auger | |
CN110127984B (en) | Sludge low-temperature heat pump drying equipment | |
CN109399891B (en) | Energy-saving belt type sludge low-temperature drying device | |
CN101671106B (en) | Method and device for sludge filter cake aerobic air drying | |
CN103771680B (en) | Sequencing batch waste heat recovery vacuum drying device | |
CN103708702B (en) | Energy-saving sludge drying device by utilizing recovery waste heat of vapor compression | |
CN102674655A (en) | Sludge harrow type drying method and device | |
WO2011094904A1 (en) | Air-drying device for sludge | |
CN103708690A (en) | Sludge treatment device | |
CN103723902A (en) | Sludge drying method and apparatus thereof | |
CN105271628A (en) | Low-temperature drying system and method of sludge | |
CN104150732A (en) | Two-stage sludge drying system | |
CN104098240B (en) | Sewage sludge treatment unit | |
CN203999290U (en) | Sewage sludge advanced treatment apparatus | |
CN105693049B (en) | A kind of sewage sludge deep treatment method | |
CN104180607B (en) | A kind of brown coal multistage drying and upgrading system | |
CN205874171U (en) | Mud resourceful treatment device | |
CN203999289U (en) | Sewage sludge treatment unit | |
CN106854031A (en) | A kind of recycling handles method for dirty mire and its processing system | |
CN202671370U (en) | Sludge rake-type drying device | |
CN211284125U (en) | Multi-effect short-distance heat transfer drying system |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
AV01 | Patent right actively abandoned |
Granted publication date: 20141210 Effective date of abandoning: 20151202 |
|
C25 | Abandonment of patent right or utility model to avoid double patenting |