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CN109879568A - Low energy consumption mud or sludge drying or cured method - Google Patents

Low energy consumption mud or sludge drying or cured method Download PDF

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Publication number
CN109879568A
CN109879568A CN201711259340.6A CN201711259340A CN109879568A CN 109879568 A CN109879568 A CN 109879568A CN 201711259340 A CN201711259340 A CN 201711259340A CN 109879568 A CN109879568 A CN 109879568A
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CN
China
Prior art keywords
mud
sludge
desiccation
drainage
drainage pipe
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.)
Pending
Application number
CN201711259340.6A
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Chinese (zh)
Inventor
李�权
缪卫良
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Guangdong Hengyuan Construction Group Co Ltd
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Guangdong Hengyuan Construction Group Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Guangdong Hengyuan Construction Group Co Ltd filed Critical Guangdong Hengyuan Construction Group Co Ltd
Priority to CN201711259340.6A priority Critical patent/CN109879568A/en
Publication of CN109879568A publication Critical patent/CN109879568A/en
Pending legal-status Critical Current

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Abstract

The present invention discloses a kind of low energy consumption mud or sludge drying or cured method, includes following steps: (1) desiccation or solidifying pool construction;(2) setting of drainage system;(3) mud or sludge are discharged into;(4) accelerate desiccation or solidification equipment;(5) treatment effect measure is improved.It is easy to operate by installing drainage system in flat desiccation or solidifying pool, save artificial, bamboo raft, machinery needed for saving the construction of conventional vacuum prestressing technology etc.;In desiccation or solidification bottom of pond portion, good leak tightness, saving vacuum efficiency caused by gas leakage is reduced for drainage pipe setting;Using the water for being higher than port in discharge drainage pipe is directed out by port, power consumption is greatly saved.Operation of the present invention is simple, cheap, mud or sludge dehydrating and drying or solidification effect are good, and decrement is obvious.

Description

Low energy consumption mud or sludge drying or cured method
Technical field
The present invention relates to mud and sludge reduction processing technology field, refers in particular to a kind of low energy consumption mud or sludge is dry Change or cured method.
Background technique
Technique of soft soil foundation treatment is the widely applied skill for mud/sludge drying or in terms of solidify in China in recent years Art.Vacuum preloading is that plastic draining board is vertically plugged in mud/sludge, and top hand connector is by drain bar and vacuum-pumping tube Net is connected, and woven cloth and geotextiles is laid on mud face, again with the sealing of air-locked sealing film, makes an enclosed area, so Afterwards by the gas and water fluid in pumped vacuum systems pump drainage enclosed area, keep the inside and outside generation certain pressure of sealing film poor, this pressure difference is To be applied to mud/Sludge Surface external load.Mud/sludge is with the increase of pressure difference and the extension of squeeze time, hole In water be constantly discharged and consolidated, thus make mud intensity increase, compressibility reduce.
Vacuum preloading can generally reach the prefabricating load of 70-80KPa, have it is easy to operate, it is excellent without secondary pollution etc. Point has certain desiccation or solidification effect.But its disadvantage is it is also obvious that existing vacuum preloading is all arranged using upper row's formula Water, to overcome during draining water from gravity and filter cloth, water draining pass to the drag effect of water, and later period desiccation or Solidification reaches a certain level rear effect and tends to stop, and energy consumption is high, and 70% or more mud containing rate, the sludge of mud are not achieved toward contact 58% or more mud containing rate, sludge volume reduces compared with nature and 60%, sludge volume is not achieved subtracts compared with nature 50% is not achieved less.
Summary of the invention
In view of this, in view of the deficiencies of the prior art, the present invention aims to provide a kind of low energy consumption mud Or sludge drying or cured method, it can effectively solve existing mud/sludge drying or curing method there are energy consumptions and is high, dry The problem of change or solidification effect.
To achieve the above object, the present invention is using following technical solution:
A kind of low energy consumption mud or sludge drying or cured method, include following steps:
(1) desiccation or solidifying pool construction: building desiccation or solidifying pool in flat place, desiccation or solidifying pool be on the spot fill dam or It is made of steel construction;
(2) setting of drainage system: it is laid with drainage pipe in desiccation or solidification bottom of pond portion, the drainage pipe connects vertical drainage Device;Drainage pipe connect to form drainage channel with vertical drainage device lower part;Extend desiccation in the port of the drainage pipe Or outside solidifying pool;
(3) mud or sludge are discharged into: it is discharged into mud or sludge in the desiccation or solidifying pool that step (2) lays drainage system, Water in mud or sludge enters drainage pipe by vertical drainage device, and the water level of vertical drainage device is higher than drainage pipe When port, water is directly flowed out from port, and when the water level of vertical drainage device is lower than the port of drainage pipe, port and draining pump connect It connects, the water in drainage pipe is excluded by power, until anhydrous discharge in drainage pipe;
(4) accelerate desiccation or solidification equipment: after the completion of step (3) is discharged into mud or sludge, to accelerate in mud or sludge The wirerope or vertical bar of fixed vertical drainage arrangement are removed in water discharge, and sealing film sealing is laid on mud face;Drainage pipe port It is controlled to a vacuum pump, by vacuumizing draining to drainage system, until the surface of mud or sludge when being decreased obviously variation without stopping It only vacuumizes, removal sealing film;
(5) improve treatment effect measure: after the completion of step (3) or step (4), drainage pipe port is blown into drying with air blower Air or 20-100 DEG C of heating air accelerate dry air or heat flowing of the air in vertical drainage device, and take out of Moisture keeps the mud or sludge fast dewatering close to vertical drainage device dry and cracked, increases and air-dry surface area, until mud or sludge Mud containing rate reach predetermined value.
Preferably, in the step (5) mud containing rate of mud up to 70% or more;The mud containing rate of sludge is up to 58% or more.
Preferably, sludge volume reduces 60% compared with nature in the step (5);Sludge volume and nature Compared to reduction 50%.
Preferably, the pumpdown time is 20-100 days in the step (4), vacuum degree 70-90kPa.
Preferably, vertical drainage device uses plastic draining board or percolating pipe in the step (2).
Preferably, vertical drainage device is fixed using wirerope drawing in the step (2) or vertical bar binding and fixing are arranged; The drainage pipe passes through desiccation or the dykes and dams of solidifying pool are led to outside desiccation or solidifying pool.
The present invention has obvious advantages and beneficial effects compared with the existing technology, specifically, by above-mentioned technical proposal Known to:
(1) it reduces project cost: drainage system being installed in flat desiccation or solidifying pool, it is easy to operate, save artificial, saving Bamboo raft, machinery needed for the construction of conventional vacuum prestressing technology etc.;Drainage pipe setting is in desiccation or solidification bottom of pond portion, airtightness Good, saving vacuum efficiency caused by gas leakage reduces;The water for being higher than port in drainage pipe is discharged using directing out by port, Power consumption is greatly saved.
(2) desiccation or curing rate are fast: drainage pipe can be opened while mud or sludge are discharged into desiccation or solidifying pool Begin to drain outward, saves later period desiccation or curing time;On the other hand, the water in conventional vacuum prestressing technology drainage system is not It can empty, the water in this technology desiccation or solidification process drainage system can empty the leaching rate for improving water immediately.
(3) desiccation or solidification effect are good: desiccation or solidification later period drainage pipe port with air blower be blown into dry air or Air is heated, dry air is accelerated or heats flowing of the air in drainage arrangement, and takes moisture out of, is made close to drainage arrangement Mud or sludge fast dewatering are dry and cracked, increase and air-dry surface area, and desiccation or curing efficiency improve, and make mud/sludge mud containing rate Further promoted.
(3) realize minimizing: the river and lake silt that handles through the invention, domestic sludge volume can be with compared with nature 50%-65% is reduced, the stockyard of waste is reduced.
(4) innoxious: treatment process does not add any chemical substance and curing materials, and secondary pollution will not occur.
In order to explain the structural features and functions of the invention more clearly, come with reference to the accompanying drawing with specific embodiment to the present invention into Row is described in detail.
Detailed description of the invention
Fig. 1 is the first state schematic diagram of the preferred embodiments of the invention;
Fig. 2 is the second status diagram of the preferred embodiments of the invention;
Fig. 3 is the third state schematic diagram of the preferred embodiments of the invention.
Description of drawing identification.
1, flat place 2, dykes and dams
3, drainage pipe 4, connector
5, vertical drainage device 6, fixed device
7, film 8, vacuum pump are sealed
9, air blower.
Specific embodiment
It please refers to shown in Fig. 1 to Fig. 3, that show present invention discloses a kind of low energy consumption mud or sludge drying or admittedly The method of change, includes following steps:
(1) desiccation or solidifying pool construction: building desiccation or solidifying pool in flat place, desiccation or solidifying pool be on the spot fill dam or It is made of steel construction.
(2) setting of drainage system: it is laid with drainage pipe in desiccation or solidification bottom of pond portion, the drainage pipe connection is vertical Drainage arrangement, drainage pipe connect to form drainage channel with vertical drainage device lower part;Extend the port of the drainage pipe Outside desiccation or solidifying pool.Specifically, vertical drainage device uses plastic draining board or percolating pipe;Vertical drainage device uses steel Cord drawing is fixed or vertical bar binding and fixing are arranged;The drainage pipe passes through desiccation or the dykes and dams of solidifying pool lead to desiccation or solid Change outside pond.
(3) mud or sludge are discharged into: being discharged into mud or dirt in the desiccation or solidifying pool that step (2) lays drainage system Water in mud, mud or sludge enters drainage pipe by vertical drainage device, and the water level of vertical drainage device is higher than drainage tube When the port in road, water is directly flowed out from port, when the water level of vertical drainage device is lower than the port of drainage pipe, port and draining Pump connection excludes the water in drainage pipe by power, until anhydrous discharge in drainage pipe.
(4) accelerate desiccation or solidification equipment: after the completion of step (3) is discharged into mud or sludge, to accelerate mud or sludge In water discharge, remove the wirerope or vertical bar of fixed vertical drainage arrangement, sealing film sealing be laid on mud face;Drainage pipe Port is controlled to a vacuum pump, by vacuumizing draining to drainage system, until the surface of mud or sludge without be decreased obviously variation When stop vacuumize, removal sealing film.Pumpdown time is 20-100 days, vacuum degree 70-90kPa.
(5) improve treatment effect measure: after the completion of step (3) or step (4), drainage pipe port is blown into air blower Dry air or 20-100 DEG C of heating air accelerate dry air or heat flowing of the air in vertical drainage device, and Take moisture out of, make close to vertical drainage device mud or sludge fast dewatering it is dry and cracked, increase air-dry surface area, until mud or The mud containing rate of sludge reaches predetermined value.The mud containing rate of mud is up to 70% or more;The mud containing rate of sludge is up to 58% or more.Sludge volume with Nature is compared to reduction 60%;Sludge volume reduces 50% compared with nature.
With multiple embodiments, invention is further described in detail below:
Embodiment 1:
In the present embodiment, the volume of desiccation or solidifying pool is 1000m3, specific steps are as follows:
(1) as shown in Figure 1, desiccation or solidifying pool are built in fill dam 2 on flat place 1.
(2) desiccation or solidification bottom of pond portion are laid with drainage pipe 3 as shown in Figure 1;Drainage pipe 3 connects vertical row with connector 4 Water installations 5, form closed drainage channel, and the vertical drainage device 5 is plastic draining board or percolating pipe;Vertical drainage device 5 is fixed using fixed device 6, and the fixed device 6 is that wirerope pulls fixed or setting vertical bar binding and fixing;The drainage tube The port in road 3 passes through desiccation or solidifying pool dykes and dams 2 are led to outside desiccation or solidifying pool.
(3) mud is discharged into desiccation or solidifying pool;Water in mud enters drainage pipe 3 by vertical drainage device 5, hangs down When the water level of in line water installations 5 is higher than the port of drainage pipe 3, water is directly flowed out from port.
(4) mud is all discharged into after desiccation or solidifying pool 15 days as shown in Figure 2, and it is bright that the port of drainage pipe 3 goes out water speed Show slack-off, 5 periphery mud of vertical drainage device has been consolidated into pillar shape, removes fixed device 6, it is close that sealing film 7 is laid on mud face Envelope;The port of drainage pipe 3 is connect with vacuum pump 8, vacuumizes draining by the port to drainage pipe 3.
(5) surface of 60 days mud is vacuumized as shown in Figure 3 without being decreased obviously, and vacuum pump 8 is not also discharged substantially, is stopped It vacuumizes, removal sealing film 7;Drainage pipe port air blower 9 is blown into dry air, and the mud close to vertical drainage device is fast Speed dehydration is dry and cracked, and crack is spread rapidly around, and experiment in 30 days terminates.
The present embodiment design parameter is as shown in table 1.
Table 1
The starting mud containing rate of mud Within 20%
Mud be all discharged into it is dry (Gu) change the average mud containing rate in pond 15 days 45%
Vacuumize water discharge time 60 days
Draining vacuum degree (kPa) is vacuumized to drainage system 70-90
Average mud containing rate after vacuumizing 66.8%
Air blower is blown into the dry air time 30 days
The final mud containing rate of mud 70.3%
Embodiment 2:
In the present embodiment, the volume of desiccation or solidifying pool is 1000m3, specific steps are as follows:
(1) desiccation or solidifying pool are built in fill dam 2 on flat place 1 as shown in Figure 1.
(2) desiccation or solidification bottom of pond portion are laid with drainage pipe 3 as shown in Figure 1;Drainage pipe 3 connects vertical row with connector 4 Water installations 5, form closed drainage channel, and the vertical drainage device 5 is plastic draining board or percolating pipe;Vertical drainage device 5 is fixed using fixed device 6, and the fixed device 6 is that wirerope pulls fixed or setting vertical bar binding and fixing;The drainage tube The port in road 3 passes through desiccation or solidifying pool dykes and dams 2 are led to outside desiccation or solidifying pool.
(3) sludge is discharged into desiccation or solidifying pool;Water in sludge enters drainage pipe 3 by vertical drainage device 5, hangs down When the water level of in line water installations 5 is higher than the port of drainage pipe 3, water is directly flowed out from port.
(4) such as Fig. 2 sludge is all discharged into after desiccation or solidifying pool 30 days, and the port of drainage pipe 3 goes out water speed and obviously becomes Slowly, 5 periphery sludge of vertical drainage device has been consolidated into pillar shape, removes fixed device 6, and sealing film 7 is laid on mud face and is sealed;Draw The port in flow tube road 3 is connect with vacuum pump 8, vacuumizes draining by the port to drainage pipe 3.
(5) as Fig. 3 vacuumizes the surface of 90 days sludge without being decreased obviously, vacuum pump 8 is not also discharged substantially, stops taking out true Sky, removal sealing film 7;Drainage pipe port air blower 9 is blown into dry air, and the sludge fast dewatering close to drainage arrangement is dry It splits, crack is spread rapidly around, and experiment in 60 days terminates.
The present embodiment design parameter is as shown in table 2.
Table 2
The starting mud containing rate of sludge Within 18%
Sludge be all discharged into it is dry (Gu) change the average mud containing rate in pond 30 days 31.7%
Vacuumize water discharge time 90 days
Draining vacuum degree (kPa) is vacuumized to drainage system 70-90
Average mud containing rate after vacuumizing 46.8%
Air blower is blown into the dry air time 60 days
The final mud containing rate of sludge 58.1%
The technical principle of the invention is described above in combination with a specific embodiment.These descriptions are intended merely to explain original of the invention Reason, and shall not be construed in any way as a limitation of the scope of protection of the invention.Based on the explanation herein, those skilled in the art Member can associate with other specific embodiments of the invention without creative labor, these modes fall within this Within the protection scope of invention.

Claims (6)

1. a kind of low energy consumption mud or sludge drying or cured method, it is characterised in that: include following steps:
(1) desiccation or solidifying pool construction: building desiccation or solidifying pool in flat place, desiccation or solidifying pool be on the spot fill dam or It is made of steel construction;
(2) setting of drainage system: it is laid with drainage pipe in desiccation or solidification bottom of pond portion, the drainage pipe connects vertical drainage Device;Drainage pipe connect to form drainage channel with vertical drainage device lower part;Extend desiccation in the port of the drainage pipe Or outside solidifying pool;
(3) mud or sludge are discharged into: it is discharged into mud or sludge in the desiccation or solidifying pool that step (2) lays drainage system, Water in mud or sludge enters drainage pipe by vertical drainage device, and the water level of vertical drainage device is higher than drainage pipe When port, water is directly flowed out from port, and when the water level of vertical drainage device is lower than the port of drainage pipe, port and draining pump connect It connects, the water in drainage pipe is excluded by power, until anhydrous discharge in drainage pipe;
(4) accelerate desiccation or solidification equipment: after the completion of step (3) is discharged into mud or sludge, to accelerate in mud or sludge The wirerope or vertical bar of fixed vertical drainage arrangement are removed in water discharge, and sealing film sealing is laid on mud face;Drainage pipe port It is controlled to a vacuum pump, by vacuumizing draining to drainage system, until the surface of mud or sludge when being decreased obviously variation without stopping It only vacuumizes, removal sealing film;
(5) improve treatment effect measure: after the completion of step (3) or step (4), drainage pipe port is blown into drying with air blower Air or 20-100 DEG C of heating air accelerate dry air or heat flowing of the air in vertical drainage device, and take out of Moisture keeps the mud or sludge fast dewatering close to vertical drainage device dry and cracked, increases and air-dry surface area, until mud or sludge Mud containing rate reach predetermined value.
2. low energy consumption mud as described in claim 1 or sludge drying or cured method, it is characterised in that: the step (5) mud containing rate of mud is up to 70% or more in;The mud containing rate of sludge is up to 58% or more.
3. low energy consumption mud as described in claim 1 or sludge drying or cured method, it is characterised in that: the step (5) sludge volume reduces 60% compared with nature in;Sludge volume reduces 50% compared with nature.
4. low energy consumption mud as described in claim 1 or sludge drying or cured method, it is characterised in that: the step (4) pumpdown time is 20-100 days in, vacuum degree 70-90kPa.
5. low energy consumption mud as described in claim 1 or sludge drying or cured method, it is characterised in that: the step (2) vertical drainage device uses plastic draining board or percolating pipe in.
6. low energy consumption mud as described in claim 1 or sludge drying or cured method, it is characterised in that: the step (2) vertical drainage device is fixed using wirerope drawing in or vertical bar binding and fixing are arranged;The drainage pipe pass through desiccation or The dykes and dams of solidifying pool are led to outside desiccation or solidifying pool.
CN201711259340.6A 2017-12-04 2017-12-04 Low energy consumption mud or sludge drying or cured method Pending CN109879568A (en)

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CN201711259340.6A CN109879568A (en) 2017-12-04 2017-12-04 Low energy consumption mud or sludge drying or cured method

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113144682A (en) * 2021-04-23 2021-07-23 龙海市仁吉建材有限公司 Settling post-treatment method for stone powder residues after stone processing

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101229951A (en) * 2008-02-22 2008-07-30 南水北调东线江苏水源有限责任公司 Bottom soft vacuum method for pumping surface water of sullage yard
CN103866757A (en) * 2014-04-10 2014-06-18 宜兴市良旭焊接瓷件有限公司 Soil dehydration desiccation or solidification method
CN103936254A (en) * 2014-04-10 2014-07-23 江苏江达市政园林建设有限公司 Method for drying silt or sludge
CN104711968A (en) * 2015-03-23 2015-06-17 程义吉 Negative-pressure three-dimensional flow-guiding disturbance impact solidification dredger filling method
CN106638542A (en) * 2016-11-09 2017-05-10 浙江水利水电学院 Consolidation and drainage system for hydraulic fill soil and rapid reinforcement method for hydraulic fill soil

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101229951A (en) * 2008-02-22 2008-07-30 南水北调东线江苏水源有限责任公司 Bottom soft vacuum method for pumping surface water of sullage yard
CN103866757A (en) * 2014-04-10 2014-06-18 宜兴市良旭焊接瓷件有限公司 Soil dehydration desiccation or solidification method
CN103936254A (en) * 2014-04-10 2014-07-23 江苏江达市政园林建设有限公司 Method for drying silt or sludge
CN104711968A (en) * 2015-03-23 2015-06-17 程义吉 Negative-pressure three-dimensional flow-guiding disturbance impact solidification dredger filling method
CN106638542A (en) * 2016-11-09 2017-05-10 浙江水利水电学院 Consolidation and drainage system for hydraulic fill soil and rapid reinforcement method for hydraulic fill soil

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113144682A (en) * 2021-04-23 2021-07-23 龙海市仁吉建材有限公司 Settling post-treatment method for stone powder residues after stone processing

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Application publication date: 20190614