CN212640259U - Sludge deep dehydration and drying treatment equipment - Google Patents
Sludge deep dehydration and drying treatment equipment Download PDFInfo
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- CN212640259U CN212640259U CN201922338406.1U CN201922338406U CN212640259U CN 212640259 U CN212640259 U CN 212640259U CN 201922338406 U CN201922338406 U CN 201922338406U CN 212640259 U CN212640259 U CN 212640259U
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- 239000010802 sludge Substances 0.000 title claims abstract description 89
- 230000018044 dehydration Effects 0.000 title claims abstract description 10
- 238000006297 dehydration reaction Methods 0.000 title claims abstract description 10
- 238000001035 drying Methods 0.000 title claims description 39
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 102
- 238000010438 heat treatment Methods 0.000 claims abstract description 96
- 239000007788 liquid Substances 0.000 claims abstract description 20
- 238000001125 extrusion Methods 0.000 claims abstract description 5
- 238000000926 separation method Methods 0.000 claims abstract description 4
- 238000001816 cooling Methods 0.000 claims description 56
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 42
- 239000003546 flue gas Substances 0.000 claims description 42
- 239000007789 gas Substances 0.000 claims description 32
- 239000000779 smoke Substances 0.000 claims description 9
- 238000000746 purification Methods 0.000 claims description 4
- 230000002093 peripheral effect Effects 0.000 claims description 3
- 238000007789 sealing Methods 0.000 claims description 3
- 230000000149 penetrating effect Effects 0.000 claims 1
- 239000004744 fabric Substances 0.000 abstract description 3
- 239000003595 mist Substances 0.000 abstract description 2
- 238000003825 pressing Methods 0.000 description 6
- 238000003756 stirring Methods 0.000 description 6
- 239000002918 waste heat Substances 0.000 description 6
- 239000010815 organic waste Substances 0.000 description 5
- 239000002912 waste gas Substances 0.000 description 5
- 238000002485 combustion reaction Methods 0.000 description 3
- 238000000034 method Methods 0.000 description 3
- 230000008569 process Effects 0.000 description 3
- WYTGDNHDOZPMIW-RCBQFDQVSA-N alstonine Natural products C1=CC2=C3C=CC=CC3=NC2=C2N1C[C@H]1[C@H](C)OC=C(C(=O)OC)[C@H]1C2 WYTGDNHDOZPMIW-RCBQFDQVSA-N 0.000 description 2
- 238000004891 communication Methods 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 238000005265 energy consumption Methods 0.000 description 2
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- 230000001580 bacterial effect Effects 0.000 description 1
- 238000010170 biological method Methods 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000000084 colloidal system Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 239000000498 cooling water Substances 0.000 description 1
- 238000004134 energy conservation Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 238000007667 floating Methods 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 239000010954 inorganic particle Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
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- 239000005416 organic matter Substances 0.000 description 1
- 239000013618 particulate matter Substances 0.000 description 1
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- 231100000331 toxic Toxicity 0.000 description 1
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- 238000001291 vacuum drying Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 238000004804 winding Methods 0.000 description 1
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- Treatment Of Sludge (AREA)
- Drying Of Solid Materials (AREA)
Abstract
The utility model discloses a sludge deep dehydration and mummification treatment facility, include the vacuum heating unit and burn the unit, wherein, the vacuum heating unit includes: the heating tank body, locate the mist outlet of the roof of the heating tank body, locate the mud entry of a lateral wall of the heating tank body, locate the mud export of another lateral wall of the heating tank body, wear to locate the inner chamber of the heating tank body and both ends correspond to the spiral extrusion device between mud entry and the mud export respectively, locate the heating body inner chamber of the heating tank body and be the heating body of snakelike coiled cloth, and locate the gas-liquid separation device between heating body and the roof of the heating tank body, the outer wall of the heating tank body is located respectively to the water inlet and the delivery port of heating body, the heating body forms the tube-shape and centers on spiral extrusion device and arranges.
Description
Technical Field
The utility model relates to a sludge treatment system, in particular to sludge drying treatment system.
Background
Sludge is a solid precipitate generated from water and sewage treatment processes, and is considered to be a precipitate, particulate matter, and floating matter generated when wastewater is treated by physical, chemical, physicochemical, biological methods, or the like, and is a very complicated heterogeneous body composed of organic debris, bacterial cells, inorganic particles, colloids, and the like. The main characteristics of the sludge are high water content (up to more than 99 percent), high organic matter content, easy decomposition and stink generation, fine particles, small specific gravity and colloidal liquid state.
In the existing sludge drying process, the direct contact area of the inside sludge and hot air is small, so that the drying speed of the sludge is slow, and secondly, when water in the sludge is evaporated, the evaporated water is directly discharged to the outside, the peculiar smell carried in the sludge can cause certain pollution to air, a large amount of heat energy is wasted, and meanwhile, the environment is also greatly subjected to heat burden and harm.
For example, the chinese patent application CN105645733A discloses a sludge drying incineration system and an incineration process thereof, the sludge drying incineration system includes a sludge ash mixer, a sludge granulator, a preheater, a sludge drying bed, a multi-stage incinerator, a steam-water separator and a waste gas purification device; the sludge-ash mixer is connected with the sludge granulator through a first sludge feeding device, the sludge granulator is connected with the preheater through a material conveying machine, the preheater is connected with the sludge drying bed through a second sludge feeding device and a sludge spreading machine in sequence, and the sludge drying bed is connected with the multi-section incinerator through a spiral conveying type feeder; the air outlet of the multi-section incinerator, the air inlet of the preheater and the air inlet of the sludge drying bed are connected through pipelines, the air outlet of the preheater and the air outlet of the sludge drying bed are connected with the air inlet of the steam-water separator through pipelines, and the air outlet of the steam-water separator, the air inlet of the multi-section incinerator and the air inlet of the waste gas purification device are connected through pipelines. However, the sludge drying incineration system and the incineration process thereof have the following disadvantages or shortcomings: (1) the preheater and the sludge drying bed need a large amount of heat energy provided by the outside; (2) the waste heat energy of the exhaust gas is not fully utilized.
Also as disclosed in chinese patent application CN107162379A, a disc sludge drying system based on energy gradient utilization includes a disc drying system and a filter-press drying system, the disc drying system includes a housing, a stirring shaft is installed in the housing, disc pieces are installed on the stirring shaft at intervals, a sludge inlet and a steam outlet are provided at the top of the housing, a dry sludge outlet is provided at the bottom of the housing, the stirring shaft is driven by a stirring motor at one end, the stirring shaft is of a hollow structure, and a condensed water delivery pipe is inserted into one end of the stirring shaft as a hot steam inlet; the filter-pressing drying system comprises a filter-pressing system, a sludge inlet system, a vacuumizing system, a hot water circulating system and a sludge output system, wherein the sludge inlet system is connected with the sludge inlet end of the filter-pressing system, the sludge output system is connected with the sludge outlet end of the filter-pressing system, the vacuumizing system is used for keeping the filter-pressing system in a negative pressure state when the filter-pressing system filters sludge, and the hot water circulating system is connected with a steam outlet of the disc drying system. However, the disc sludge drying system based on energy cascade utilization has the following disadvantages or shortcomings: (1) the disc drying system needs high-temperature hot steam for sludge drying, and the energy consumption is large during sludge drying; (2) and toxic and harmful gases in waste gas in the sludge are not effectively separated.
Therefore, the deep dehydration and drying treatment equipment for sludge, which can effectively improve the drying degree of sludge, has low energy consumption and low pollution, is a problem to be solved urgently in the industry.
Disclosure of Invention
The utility model aims at providing a sludge deep dehydration and mummification treatment facility, its organic waste gas in can the abundant separation sludge anhydration steam that volatilizees, when decomposing and eliminating its environmental pollution through burning, the comdenstion water that separates in to mud of the heat that utilizes waste gas burning to produce carries out the heat exchange, the hot water alright utilize lower temperature vacuum drying mud of formation.
In order to achieve the above object, the utility model provides a sludge deep dehydration and mummification treatment facility, include: vacuum heating unit, incineration unit and vacuum cooling unit, vacuum cooling unit includes: the cooling device comprises a cooling tank body, a high-temperature gas inlet arranged on the top wall of the cooling tank body, a condensed water outlet arranged on the bottom wall of the cooling tank body, a low-temperature gas outlet and a liquid inlet arranged on one side of the cooling tank body, a liquid outlet arranged on the other side of the cooling tank body, a cooling pipe which is arranged in the cooling tank body in a serpentine disc manner, two ends of the cooling pipe are respectively connected between the liquid inlet and the liquid outlet, and a vacuum pump communicated with the low-temperature gas outlet, wherein the high-temperature gas inlet of a vacuum cooling unit is communicated with a mixed gas outlet of a vacuum; the incineration unit includes: the incinerator comprises an incinerator body, an incineration gas inlet, a condensate water inlet and a smoke discharge port, wherein the incineration gas inlet is formed in the wall of the incinerator body, and is communicated with an exhaust port of a vacuum pump of the vacuum cooling unit.
The gas discharged from the mixed gas outlet of the vacuum heating unit is mixed gas comprising water vapor, VOC organic waste gas and the like, and after being treated by the vacuum cooling unit, the gas flow is controlled by using a vacuum pump, and the VOC gas is introduced into the incinerator for combustion and decomposition.
Optionally, the vacuum heating unit is barrel-partitioned heating, the vacuum heating unit comprising: the heating tank body, locate the mist export of the roof of the heating tank body, locate the sludge inlet of a lateral wall of the heating tank body, locate the sludge outlet of another lateral wall of the heating tank body, wear to locate the inner chamber of the heating tank body and both ends and correspond to the spiral extrusion device between sludge inlet and the sludge outlet respectively, locate the heating body inner chamber of the heating tank body and be the heating body of snakelike coiled cloth, and locate the gas-liquid separation device between heating body and the roof of the heating tank body, the outer wall of the heating tank body is located respectively to the water inlet and the delivery port of heating body. The heating pipe body is formed in a cylindrical shape and arranged around the screw extrusion device.
Wherein the sludge is spirally extruded in the vacuum heating unit. The heating pipe body is set to 2-10 atmospheric pressures, and the temperature of hot water in the pipe is set to 100-180 ℃, for example, about 150 ℃. The heating tank body is vacuum, so that water in the sludge can be boiled into steam at 40-60 ℃, is separated from the sludge and is discharged out of the vacuum heating unit. Therefore, the sludge can be dried by using low-temperature hot water at about 150 ℃, and energy conservation and emission reduction are realized.
Optionally, the sludge inlet and the sludge outlet are respectively provided with a closed sealing cover, so that when the system is started, vacuum can be formed in the heating tank body; when the system normally operates, the closed sealing cover is opened, and the sludge inlet and the sludge outlet are always filled with continuous sludge, so that the heating tank body can always keep vacuum.
Optionally, the incineration unit further comprises a flue gas cooling device, the flue gas cooling device comprising: the cooling device comprises a cooling main body, a hot flue gas inlet, a cold flue gas outlet, a cold heat conduction oil inlet and a heat conduction oil outlet, wherein the hot flue gas inlet, the cold flue gas outlet, the cold heat conduction oil inlet and the heat conduction oil outlet are arranged on the peripheral wall of the cooling main body, the cold flue gas outlet is communicated with a chimney, and the hot flue gas inlet is communicated with a flue gas discharge port of the incinerator, so that flue gas enters the flue gas cooling device to heat cold heat conduction.
Optionally, the waste heat utilization unit comprises a first heat exchange device, the first heat exchange device is provided with a heat conduction oil inlet, a cold conduction oil outlet, a medium temperature water inlet and a high temperature water outlet, the heat conduction oil inlet is communicated with the heat conduction oil outlet of the flue gas cooling device, the cold conduction oil outlet is communicated with the cold conduction oil inlet of the flue gas cooling device, the medium temperature water inlet is communicated with the liquid outlet of the vacuum cooling unit, and the high temperature water outlet is communicated with the water inlet of the heating pipe body of the vacuum heating unit.
Optionally, the waste heat utilization unit further comprises a second heat exchange device, the second heat exchange device comprises a low-temperature water inlet, a medium-temperature water outlet, a hot air inlet and a cold air outlet, the low-temperature water inlet is communicated with the liquid outlet of the vacuum cooling unit, the medium-temperature water outlet is communicated with the medium-temperature water inlet of the first heat exchange device, the hot air inlet is communicated with the air compressor, and the cold air outlet is communicated with the compressed air storage tank to be used by a user.
Optionally, a first drain pipe and a second drain pipe are arranged at a water outlet of the heating pipe body of the vacuum heating unit, the first drain pipe is communicated with a low-temperature water inlet of the second heat exchange device, and the second drain pipe is communicated with a hot water user.
Therefore, after organic gas in sludge is incinerated and decomposed, heat of the discharged high-temperature flue gas is converted into heat conduction oil at the flue gas cooling device, the temperature of the heat conduction oil can reach about 300 ℃, the heat conduction oil converts the heat into condensed water discharged from the vacuum cooling unit at the first heat exchange device, the condensed water is heated into hot water at 100-180 ℃, and the hot water is conveyed into a heating pipe body of the vacuum heating unit for drying the sludge, and recycling of energy is achieved. Meanwhile, after the sludge is dried, the water in the heating pipe body is cooled to about 50 ℃, the water is discharged out of the vacuum heating unit from the water outlet of the heating pipe body, one part of the water is supplied to the low-temperature water inlet of the second heat exchange device through the first water discharge pipe, and the other part of the water is supplied to a user needing hot water, such as a boiler, through the second water discharge pipe.
Optionally, the water outlet of the heating pipe body of the vacuum heating unit can be only provided with a second water outlet pipe, so that all hot water is supplied to a user for use; or the water outlet of the heating pipe body of the vacuum heating unit can be only provided with the first water drainage pipe, and all hot water is conveyed to the low-temperature water inlet of the second heat exchange device to form water circulation.
Optionally, the condensed water outlet of the vacuum cooling unit is communicated with the condensed water inlet of the incineration unit, and the condensed water inlet of the incineration unit is provided with an atomizing nozzle for atomizing and burning the condensed water discharged from the vacuum cooling unit to remove harmful components therein.
Optionally, a flue gas purification device is arranged between the flue gas cooling device and the chimney.
Optionally, the liquid inlet and the liquid outlet of the vacuum cooling unit are respectively provided with a valve.
Optionally, a control water pump for introducing the medium-temperature water into the first heat exchange device is arranged on a pipeline between the medium-temperature water inlet of the first heat exchange device and the medium-temperature water outlet of the second heat exchange device.
Optionally, the first and/or second heat exchange device used in the present invention may be a dividing wall type heat exchange device, such as a coil heat exchanger or a shell-and-tube heat exchanger; or heat pipe type heat exchange equipment.
The utility model has the advantages that: (1) the sludge is dried at low temperature in a vacuum state in the vacuum heating unit, so that the use and discharge amount of heat energy are effectively reduced; (2) the vacuum cooling unit can separate steam discharged in the sludge drying process to form condensed water and organic waste gas, and the organic waste gas is conveyed to the incineration unit for combustion, so that the waste gas in the sludge is completely decomposed and purified, and the discharged gas is ensured to meet the environmental emission standard; (3) the heat of the flue gas generated by the combustion of the organic waste gas is utilized to carry out heat exchange on the cooling water discharged by the vacuum cooling unit to form water vapor, and the water vapor is conveyed to the vacuum heating unit to carry out sludge drying, so that the self-sufficiency of energy is realized, and the energy utilization rate is improved; (4) the system can fully utilize other surrounding heat sources as a second heat exchange device for heat exchange, and meanwhile, water cooled after the sludge is dried can be recycled or supplied to users needing hot water, so that energy is fully utilized, and the whole system is more energy-saving and environment-friendly.
Drawings
FIG. 1 is a schematic view showing the construction of an apparatus for deep sludge dewatering and drying treatment according to the present invention.
Fig. 2 shows a schematic view of the arrangement structure of the heating pipe of the vacuum heating unit of the present invention.
Fig. 3 shows a schematic cross-sectional structure of the heating pipe body of the vacuum heating unit of the present invention.
Detailed Description
Reference will now be made in detail to embodiments of the present invention, examples of which are illustrated in the accompanying drawings, wherein like reference numerals refer to the same or similar elements or elements having the same or similar function throughout. The embodiments described below with reference to the drawings are exemplary and intended to be used for explaining the present invention, and should not be construed as limiting the present invention.
Referring to fig. 1, according to a non-limiting embodiment of the present invention, an apparatus for deep dewatering and drying sludge includes: a vacuum heating unit 10, a vacuum cooling unit 20, an incineration unit 30, and a waste heat utilization unit 40.
Wherein the vacuum heating unit 10 includes: a heating tank 110, a mixed gas outlet 120, a sludge inlet 130, a sludge outlet 140, a screw conveyor 150, a heating pipe 160, and a gas-liquid separator 170.
The vacuum cooling unit 20 includes: a cooling tank 210, a high-temperature gas inlet 220, a condensed water outlet 230, a low-temperature gas outlet 240, a liquid inlet 250, a liquid outlet 260, a cooling pipe 270, and a vacuum pump 280. The high-temperature gas inlet 220 of the vacuum cooling unit 20 is communicated with the mixed gas outlet 120 of the vacuum heating unit 10, the liquid inlet 250 is communicated with the cold water source L1, and the liquid inlet 250 and the liquid outlet 260 are respectively provided with a valve V.
The incineration unit 30 includes: the incinerator 310, an incineration gas inlet 3101 provided in the incinerator 310, a condensed water inlet 3102, a flue gas discharge port 3103, and a burner 3105, wherein the incineration gas inlet 3101 is communicated with an exhaust port of a vacuum pump 280 of the vacuum cooling unit 20.
As shown in fig. 1, the vacuum heating unit 10 is a barrel-shaped partition wall type heating, the screw conveyor 150 is inserted into the inner cavity of the heating tank 110, and has two ends corresponding to the sludge inlet 130 and the sludge outlet 140, respectively, the gas-liquid separator 170 is disposed between the heating tube 160 and the top wall of the heating tank 110, and the water inlet 1601 and the water outlet 1602 of the heating tube 160 are disposed on the outer wall of the heating tank 110, respectively.
As shown in fig. 2, the heating pipe 160 is formed into a cylindrical shape by winding a serpentine cloth around the heating tank 110 in the longitudinal direction, and as shown in fig. 3, a gap S is provided between two adjacent sections of the pipe 160L and 160R (i.e., two sections of the pipe in which the water flows in opposite directions), so as to facilitate the discharge of moisture in the sludge from the gap space. In this non-limiting embodiment, the gap S is set to 10 to 100 mm, such as 20 mm.
In this non-limiting embodiment, as shown in figure 1, the incineration unit 30 further comprises a flue gas cooling device 320, the flue gas cooling device 320 comprising: the cooling body 3201, the hot flue gas inlet 3202, the cold flue gas outlet 3203, the cold heat conduction oil inlet 3204 and the heat conduction oil outlet 3205 which are arranged on the peripheral wall of the cooling body 3201, wherein the cold flue gas outlet 3203 is communicated with the chimney 50, and the hot flue gas inlet 3202 is communicated with the flue gas discharge port 3103 of the incinerator 310, so that the flue gas enters the flue gas cooling device 320 to heat the cold heat conduction oil from the cold heat conduction oil inlet 3204 into the heat conduction oil.
As shown in fig. 1, the waste heat utilization unit 40 includes a first heat exchange device 410, the first heat exchange device 410 is provided with a heat conduction oil inlet 4101, a cold conduction oil outlet 4102, a medium temperature water inlet 4103, and a high temperature water outlet 4104, wherein the heat conduction oil inlet 4101 is communicated with a heat conduction oil outlet 3205 of the flue gas cooling device 320, the heat conduction oil in the flue gas cooling device 320 is introduced into the first heat exchange device 410 through an oil pump O, the cold conduction oil outlet 4102 is communicated with the cold conduction oil inlet 3204 of the flue gas cooling device 320, and the high temperature water outlet 4104 is communicated with a water inlet 1601 of the heating pipe 160 of the vacuum heating unit 10.
As another non-limiting embodiment, the waste heat utilization unit 40 further includes a second heat exchange device 420, and the second heat exchange device 420 includes: a low-temperature water inlet port 4201, a medium-temperature water outlet port 4202, a hot air inlet port 4203, and a cold air outlet port 4204, the low-temperature water inlet port 4201 being communicated with the liquid outlet port 260 of the vacuum cooling unit 20, the medium-temperature water outlet port 4202 being communicated with the medium-temperature water inlet port 4103 of the first heat exchanging device 410, the hot air inlet port 4203 being communicated with the air compressor 4206, and the cold air outlet port 4204 being communicated with the compressed air storage tank 4205, whereby compressed air is supplied to a user. Wherein, the hot wind from the air compressor 4206 turns the heat into cold wind after being released in the second heat exchanging device 420 and delivers the cold wind to the user.
In this non-limiting embodiment, as shown in fig. 1, the water outlet 1602 of the heating pipe body 160 of the vacuum heating unit 10 is provided with a first water outlet pipe W1 and a second water outlet pipe W2, the first water outlet pipe W1 may be in communication with the low-temperature water inlet 4201 of the second heat exchanging device 420 (not shown), and the second water outlet pipe W2 is in communication with a hot water user (not shown).
As a further non-limiting embodiment, the condensed water outlet 230 of the vacuum cooling unit 20 is communicated with the condensed water inlet 3102 of the incineration unit 30, and an atomizing nozzle N is provided at the condensed water inlet 3102 of the incineration unit 30 to atomize and burn the condensed water discharged from the vacuum cooling unit 20 to remove harmful components therein.
In order to protect the environment and prevent the smoke from having substances polluting the atmosphere, as shown in fig. 1, a smoke purifying device 60 is further disposed between the smoke cooling device 320 and the chimney 50, so that the smoke discharged by the smoke purifying device 60 is correspondingly filtered and purified, and the smoke reaches the emission standard, and the temperature of the discharged smoke is about 200 ℃.
Further, as shown in fig. 1, a control water pump P for introducing the medium temperature water into the first heat exchange device 410 is provided on a line between the medium temperature water inlet 4103 of the first heat exchange device 410 and the medium temperature water outlet 4202 of the second heat exchange device 420.
In the description herein, references to the description of the term "one embodiment," "some embodiments," "an example," "a specific example," or "some examples," etc., mean that a particular feature, structure, or characteristic described in connection with the embodiment or example is included in at least one embodiment or example of the present invention. In this specification, the schematic representations of the terms used above are not necessarily intended to refer to the same embodiment or example. Furthermore, various embodiments or examples and features of different embodiments or examples described in this specification can be combined and combined by one skilled in the art without contradiction.
Although embodiments of the present invention have been shown and described, it is understood that the above embodiments are exemplary and should not be construed as limiting the present invention, and that variations, modifications, substitutions and alterations can be made to the above embodiments by those of ordinary skill in the art without departing from the scope of the present invention.
Claims (8)
1. A sludge deep dehydration and drying treatment device comprises: vacuum heating unit and incineration unit, its characterized in that: the vacuum heating unit includes: the device comprises a heating tank body, a mixed gas outlet arranged on the top wall of the heating tank body, a sludge inlet arranged on one side wall of the heating tank body, a sludge outlet arranged on the other side wall of the heating tank body, a spiral extrusion device which is arranged in an inner cavity of the heating tank body in a penetrating manner and two ends of which are respectively corresponding to the sludge inlet and the sludge outlet, a heating pipe body which is arranged in the inner cavity of the heating tank body and is distributed in a snake-shaped disc shape, and a gas-liquid separation device arranged between the heating pipe body and the top wall of the heating tank body, wherein a water inlet and a water outlet of the heating pipe body are respectively arranged on the; the incineration unit includes: the incinerator comprises an incinerator body, an incineration gas inlet, a condensate water inlet and a smoke discharge port, wherein the incineration gas inlet is formed in the wall of the incinerator body, and is communicated with the mixed gas outlet of the vacuum heating unit.
2. The apparatus for deep dewatering and drying treatment of sludge according to claim 1, wherein the incineration unit further comprises a flue gas cooling device, the flue gas cooling device comprising: the cooling device comprises a cooling main body, a hot flue gas inlet, a cold flue gas outlet, a cold heat conduction oil inlet and a heat conduction oil outlet, wherein the hot flue gas inlet, the cold flue gas outlet, the cold heat conduction oil inlet and the heat conduction oil outlet are arranged on the peripheral wall of the cooling main body, the cold flue gas outlet is communicated with a chimney, and the hot flue gas inlet is communicated with a flue gas discharge port of the incinerator.
3. The sludge deep dehydration and drying treatment device as claimed in claim 1, wherein the water outlet of the heating pipe body of the vacuum heating unit is provided with a first drain pipe and a second drain pipe.
4. The sludge deep dehydration and drying treatment device as claimed in claim 1, wherein the water outlet of the heating pipe body of the vacuum heating unit is provided with a first drainage pipe.
5. The sludge deep dehydration and drying treatment device as claimed in claim 2, characterized in that a flue gas purification device is further arranged between the flue gas cooling device and the chimney.
6. The apparatus for deep dewatering and drying of sludge according to claim 1, wherein the heating pipe body is formed in a cylindrical shape and arranged around the screw extruding means.
7. The apparatus for deep dewatering and drying of sludge according to claim 1, wherein the sludge inlet and the sludge outlet are respectively provided with a sealing cover.
8. The apparatus for deep dewatering and drying of sludge according to claim 1, wherein the vacuum heating unit is a barrel-shaped dividing wall type heating device.
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201922338406.1U CN212640259U (en) | 2019-12-23 | 2019-12-23 | Sludge deep dehydration and drying treatment equipment |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201922338406.1U CN212640259U (en) | 2019-12-23 | 2019-12-23 | Sludge deep dehydration and drying treatment equipment |
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| CN212640259U true CN212640259U (en) | 2021-03-02 |
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111039535A (en) * | 2019-12-23 | 2020-04-21 | 广州和瑞节能环保科技有限公司 | Sludge deep dehydration and drying treatment system |
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111039535A (en) * | 2019-12-23 | 2020-04-21 | 广州和瑞节能环保科技有限公司 | Sludge deep dehydration and drying treatment system |
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