CN209619165U - River and lake silt integrated treatment unit - Google Patents
River and lake silt integrated treatment unit Download PDFInfo
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- CN209619165U CN209619165U CN201920158844.7U CN201920158844U CN209619165U CN 209619165 U CN209619165 U CN 209619165U CN 201920158844 U CN201920158844 U CN 201920158844U CN 209619165 U CN209619165 U CN 209619165U
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- river
- flocculation basin
- dewaterer
- lake silt
- integrated treatment
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Abstract
The utility model relates to a kind of river and lake silt integrated treatment units.It specifically, is the integrated treatment unit quickly handled for the mud generated in the process to river and lake dredging.Its main feature is that include sorting mechanism, flocculation basin, dewaterer and curing, between sorting mechanism and flocculation basin, flocculation basin be connected by dredge pump between dewaterer, the dewaterer is connected by conveyer with curing.The river and lake silt handled using the utility model, can be used not only as engineering earth, avoids argillization again, eliminates the secondary pollution of environment, also can avoid the waste of land resource.
Description
Technical field
The utility model relates to a kind of device for treating sludge.It specifically, is for the mud generated during river and lake dredging
Starch the integrated treatment unit quickly handled.
Background technique
It is well known that a large amount of mud will necessarily be generated by carrying out dredging to river and lake.Currently, river and lake dredging is mainly using underwater
It stirs the methods of dry digging of suction, artificial hydraulicking or digging machine the sludge treatment in river and lake is debarked, and silt stockyard is selected to carry out heap
It puts, makes its natural consolidation.And it is greater than 30% from the mud of river and lake processing disembarkation in muddy, and the clay content less than 5 microns,
Partial size is small, this is just determined, and river and lake silt moisture content is high, consolidation rate is slow, and intensity is low after consolidation.In addition, some river and lake silts
In, also contain poisonous and harmful substances.
Due to using natural consolidation, consolidation rate is slow, occupies a large amount of soils, causes the waste of land resource.
Again since the mud intensity after consolidation is low, not only Exploiture of cropland utilization cannot be directly carried out in stockyard, can not also made
It is used for engineering earth.
In addition, after consolidation, meeting rain drop erosion due to containing poisonous and harmful substances in some river and lake silts, not only weighing
New argillization becomes mud again, and poisonous and harmful substances therein are easy exudation, can cause secondary pollution to environment.
Utility model content
Problem to be solved in the utility model is to provide a kind of river and lake silt integrated treatment unit.At this device
River and lake silt is managed, engineering earth is can be used not only as, avoids argillization again, eliminate the secondary pollution of environment, also can avoid soil money
The waste in source.
The above problem to be solved in the utility model is realized by the following technical scheme:
The river and lake silt integrated treatment unit feature of the utility model is: including sorting mechanism, flocculation basin, dewaterer and
Curing, between sorting mechanism and flocculation basin, flocculation basin be connected by dredge pump between dewaterer, the dewaterer is by conveyer
It is connected with curing.
The sorting mechanism is vibrating screen or drum screen, deposits mud sump below sorting mechanism, deposits Chi Kou and the screening of mud sump
Mechanism is corresponding on perpendicular direction.Described deposit is connected between mud sump and flocculation basin by a dredge pump.
The flocculation basin contains pond body and the first blender.
The dewaterer is high pressure plate and frame filter press or supercentrifuge.
The conveyer is screw conveyor or belt conveyor.
The curing contains storage hopper dredger and the second blender.
Since the river and lake silt integrated treatment unit of the utility model contains sorting mechanism, flocculation basin, dewaterer and consolidates
Change machine, between sorting mechanism and flocculation basin, flocculation basin be connected by dredge pump between dewaterer, the dewaterer by conveyer with
Curing is connected.By the utility model, the river and lake silt that can be come out in real time to dredging directly carries out integrated treatment.With background
River and lake silt, which is piled up stockyard, in technology allows its natural consolidation to compare, and consolidation rate is fast, does not have to silt stockyard, is not take up soil,
Avoid the waste of land resource.Again due to that can be screened, be flocculated to the river and lake silt of dredging by the utility model, be dehydrated
And solidification, river and lake silt after processing, can be used as backfill, dyke, road and greening soil, realize dredging and sludge treatment
Seamless interfacing will be that the river and lake silt of waste becomes useful soil resource originally.In addition, due to real using the utility model
The seamless interfacing for having showed dredging and sludge treatment is not required to silt stockyard, and chance water washes away mud again after not only can avoid silt consolidation
Change, become the generation of the case where mud again, and can avoid the exudation of the poisonous and harmful substances in yard sludge, to eliminate
Caused by environment secondary pollution.
Detailed description of the invention
Fig. 1 is the river and lake silt integrated treatment unit schematic diagram of the utility model.
Specific embodiment
The utility model is described in further details with reference to embodiments.
Embodiment one
As shown in Figure 1, the river and lake silt integrated treatment unit of the utility model contains sorting mechanism, flocculation basin, dehydration
Machine and curing, between sorting mechanism and flocculation basin, flocculation basin be connected by dredge pump between dewaterer, the dewaterer is by defeated
Machine is sent to be connected with curing.
The sorting mechanism can be vibrating screen, be also possible to drum screen.In the present embodiment, the sorting mechanism is vibration
Sieve.Mud sump is deposited in being arranged with for sorting mechanism.The river and lake silt sent by dredging work is starched after vibrating screen screens, and is eliminated
In, sand grains and rubbish greater than 2mm, mud, sand grains and rubbish of the partial size less than 2mm leaks into and deposits in mud sump.It is described deposit mud sump with
It is connected by pipeline with dredge pump between flocculation basin, dredge pump therein is that high pressure dredge pump will be screened by high pressure dredge pump and pipeline
Deposit in mud sump river and lake silt slurry be sent into flocculation basin in.
The flocculation basin contains pond body and the first blender.The pond body be cylindrical shape, first blender by motor,
Agitating shaft and the blade for being connected to agitating shaft lower part are constituted.The motor is mounted at the top of pond body by bracket, output shaft court
It is connected down and with agitating shaft upper end, agitating shaft connects vaned one end and protrudes into pond body.When work, added with flocculation in pond body
Agent, the blade for being driven by a motor agitating shaft and agitating shaft lower part rotate together, and the intracorporal river and lake silt slurry in pond and flocculant are mixed
It closes uniformly, merges river and lake silt slurry mutually with flocculant, form mud floc sedimentation.The flocculant be weight content be 3% it is poly-
Close cationic polyacrylamide (PAM) solution that aluminium oxide (PAC) solution and weight content are 0.15%.Wherein, every cubic metre of river
The quantity of polymer alumina (PAC) solution and cationic polyacrylamide (PAM) solution that are added in lake silt slurry is 15 respectively
It rises and 20 liters.
The dewaterer can be high pressure plate and frame filter press, be also possible to supercentrifuge.In the present embodiment, dehydration used
Machine is high pressure plate and frame filter press, filter area 500m2, it is 1.6Mpa into mud pressure, maximal pressure force value is 12.5Mpa, work
Making the period is 120 minutes.After being dehydrated by dewaterer to mud floc sedimentation, the moisture content of mud floc sedimentation is made to be down to 37%.
The conveyer is screw conveyor, is also possible to belt conveyor.In the present embodiment, conveyer used is spiral
Conveyer.By screw conveyor, the mud floc sedimentation that moisture content is 37 is sent into curing.
The curing contains storage hopper dredger and the second blender.The storage hopper dredger is cylindrical container, second stirring
Device is made of motor, agitating shaft and the blade being connected on agitating shaft.
When work, it is added with curing agent in storage hopper dredger, and the blade being driven by a motor on agitating shaft and agitating shaft revolves together
Turn, be uniformly mixed mud floc sedimentation with curing agent, mud walk is modified to available finished product soil.The curing agent contains
One curing agent, the second curing agent and third curing agent.First curing agent is according to cement: flyash: land plaster=30:65:
5 weight ratio mixes.Second curing agent is according to cement: flyash: blast furnace ground-slag: calcium oxide: land plaster=
The weight ratio of 30:30:30:5:5 mixes.The third curing agent is according to cement: flyash: blast furnace ground-slag: oxidation
Calcium: land plaster: sodium sulphate=30:20:35:10:4:1 weight ratio mixes.The cement can be portland cement,
It is also possible to sulphate aluminium cement, it is mixed can also be that portland cement and sulphate aluminium cement are mixed according to arbitrary proportion
Cement.In the present embodiment, cement used is portland cement.
Wherein:
It is mixed using the first curing agent with walk, the soil of finished product made of being modified can be used as backfill soil;
It is mixed using the second curing agent with walk, the soil of finished product made of being modified can be used as dyke soil;
It is mixed using third curing agent with walk, the soil of finished product made of being modified can be used as road soil.
In short, as needed, different curing agent can be selected.Any curing agent is specifically selected, is depended on the needs.At this
In embodiment, selection is the first curing agent, and after mixing with walk, the soil of finished product made of being modified can be used as backfill soil.
Embodiment two
As shown in Figure 1, the river and lake silt integrated treatment unit of the utility model contains sorting mechanism, flocculation basin, dehydration
Machine and curing, between sorting mechanism and flocculation basin, flocculation basin be connected by dredge pump between dewaterer, the dewaterer is by defeated
Machine is sent to be connected with curing.
The sorting mechanism can be vibrating screen, be also possible to drum screen.In the present embodiment, the sorting mechanism is vibration
Sieve.Mud sump is deposited in being arranged with for sorting mechanism.The river and lake silt sent by dredging work is starched after vibrating screen screens, and is eliminated
In, sand grains and rubbish greater than 2mm, mud, sand grains and rubbish of the partial size less than 2mm leaks into and deposits in mud sump.It is described deposit mud sump with
It is connected by pipeline with dredge pump between flocculation basin, dredge pump therein is that high pressure dredge pump will be screened by high pressure dredge pump and pipeline
Deposit in mud sump river and lake silt slurry be sent into flocculation basin in.
The flocculation basin contains pond body and the first blender.The pond body be cylindrical shape, first blender by motor,
Agitating shaft and the blade for being connected to agitating shaft lower part are constituted.The motor is mounted at the top of pond body by bracket, output shaft court
It is connected down and with agitating shaft upper end, agitating shaft connects vaned one end and protrudes into pond body.When work, added with flocculation in pond body
Agent, the blade for being driven by a motor agitating shaft and agitating shaft lower part rotate together, and the intracorporal river and lake silt slurry in pond and flocculant are mixed
It closes uniformly, merges river and lake silt slurry mutually with flocculant, form mud floc sedimentation.The flocculant be weight content be 4% it is poly-
Close cationic polyacrylamide (PAM) solution that aluminium oxide (PAC) solution and weight content are 0.20%.Wherein, every cubic metre of river
The quantity of polymer alumina (PAC) solution and cationic polyacrylamide (PAM) solution that are added in lake silt slurry is 20 respectively
It rises and 40 liters.
The dewaterer can be high pressure plate and frame filter press, be also possible to supercentrifuge.In the present embodiment, dehydration used
Machine is high pressure plate and frame filter press, filter area 500m2, it is 1.6Mpa into mud pressure, maximal pressure force value is 12.5Mpa, work
Making the period is 90 minutes.After being dehydrated by dewaterer to mud floc sedimentation, the moisture content of mud floc sedimentation is made to be down to 38%.
The conveyer is screw conveyor, is also possible to belt conveyor.In the present embodiment, conveyer used is spiral
Conveyer.By screw conveyor, the mud floc sedimentation that moisture content is 38 is sent into curing.
The curing contains storage hopper dredger and the second blender.The storage hopper dredger is cylindrical container, second stirring
Device is made of motor, agitating shaft and the blade being connected on agitating shaft.
When work, it is added with curing agent in storage hopper dredger, and the blade being driven by a motor on agitating shaft and agitating shaft revolves together
Turn, be uniformly mixed mud floc sedimentation with curing agent, mud walk is modified to available finished product soil.The curing agent contains
One curing agent, the second curing agent and third curing agent.First curing agent is according to cement: flyash: land plaster=30:65:
5 weight ratio mixes.Second curing agent is according to cement: flyash: blast furnace ground-slag: calcium oxide: land plaster=
The weight ratio of 30:30:30:5:5 mixes.The third curing agent is according to cement: flyash: blast furnace ground-slag: oxidation
Calcium: land plaster: sodium sulphate=30:20:35:10:4:1 weight ratio mixes.The cement can be portland cement,
It is also possible to sulphate aluminium cement, it is mixed can also be that portland cement and sulphate aluminium cement are mixed according to arbitrary proportion
Cement.In the present embodiment, the cement is sulphate aluminium cement.
Wherein:
It is mixed using the first curing agent with walk, the soil of finished product made of being modified can be used as backfill soil;
It is mixed using the second curing agent with walk, the soil of finished product made of being modified can be used as dyke soil;
It is mixed using third curing agent with walk, the soil of finished product made of being modified can be used as road soil.
In short, as needed, different curing agent can be selected.Any curing agent is specifically selected, is depended on the needs.At this
In embodiment, selection is the second curing agent, and after mixing with walk, the soil of finished product made of being modified can be used as dyke soil.
Embodiment three
As shown in Figure 1, the river and lake silt integrated treatment unit of the utility model contains sorting mechanism, flocculation basin, dehydration
Machine and curing, between sorting mechanism and flocculation basin, flocculation basin be connected by dredge pump between dewaterer, the dewaterer is by defeated
Machine is sent to be connected with curing.
The sorting mechanism can be vibrating screen, be also possible to drum screen.In the present embodiment, the sorting mechanism is vibration
Sieve.Mud sump is deposited in being arranged with for sorting mechanism.The river and lake silt sent by dredging work is starched after vibrating screen screens, and is eliminated
In, sand grains and rubbish greater than 2mm, mud, sand grains and rubbish of the partial size less than 2mm leaks into and deposits in mud sump.It is described deposit mud sump with
It is connected by pipeline with dredge pump between flocculation basin, dredge pump therein is that high pressure dredge pump will be screened by high pressure dredge pump and pipeline
Deposit in mud sump river and lake silt slurry be sent into flocculation basin in.
The flocculation basin contains pond body and the first blender.The pond body be cylindrical shape, first blender by motor,
Agitating shaft and the blade for being connected to agitating shaft lower part are constituted.The motor is mounted at the top of pond body by bracket, output shaft court
It is connected down and with agitating shaft upper end, agitating shaft connects vaned one end and protrudes into pond body.When work, added with flocculation in pond body
Agent, the blade for being driven by a motor agitating shaft and agitating shaft lower part rotate together, and the intracorporal river and lake silt slurry in pond and flocculant are mixed
It closes uniformly, merges river and lake silt slurry mutually with flocculant, form mud floc sedimentation.The flocculant be weight content be 5% it is poly-
Close cationic polyacrylamide (PAM) solution that aluminium oxide (PAC) solution and weight content are 0.25%.Wherein, every cubic metre of river
The quantity of polymer alumina (PAC) solution and cationic polyacrylamide (PAM) solution that are added in lake silt slurry is 25 respectively
It rises and 60 liters.
The dewaterer can be high pressure plate and frame filter press, be also possible to supercentrifuge.In the present embodiment, dehydration used
Machine is high pressure plate and frame filter press, filter area 500m2, it is 1.6Mpa into mud pressure, maximal pressure force value is 12.5Mpa, work
Making the period is 60 minutes.After being dehydrated by dewaterer to mud floc sedimentation, the moisture content of mud floc sedimentation is made to be down to 39%.
The conveyer is screw conveyor, is also possible to belt conveyor.In the present embodiment, conveyer used is spiral
Conveyer.By screw conveyor, the mud floc sedimentation that moisture content is 39 is sent into curing.
The curing contains storage hopper dredger and the second blender.The storage hopper dredger is cylindrical container, second stirring
Device is made of motor, agitating shaft and the blade being connected on agitating shaft.
When work, it is added with curing agent in storage hopper dredger, and the blade being driven by a motor on agitating shaft and agitating shaft revolves together
Turn, be uniformly mixed mud floc sedimentation with curing agent, mud walk is modified to available finished product soil.The curing agent contains
One curing agent, the second curing agent and third curing agent.First curing agent is according to cement: flyash: land plaster=30:65:
5 weight ratio mixes.Second curing agent is according to cement: flyash: blast furnace ground-slag: calcium oxide: land plaster=
The weight ratio of 30:30:30:5:5 mixes.The third curing agent is according to cement: flyash: blast furnace ground-slag: oxidation
Calcium: land plaster: sodium sulphate=30:20:35:10:4:1 weight ratio mixes.The cement can be portland cement,
It is also possible to sulphate aluminium cement, it is mixed can also be that portland cement and sulphate aluminium cement are mixed according to arbitrary proportion
Cement.In the present embodiment, the cement is with portland cement and sulphate aluminium cement and according to portland cement: sulphur aluminic acid
The blended cement that salt cement=1:1 weight ratio mixes.
Wherein:
It is mixed using the first curing agent with walk, the soil of finished product made of being modified can be used as backfill soil;
It is mixed using the second curing agent with walk, the soil of finished product made of being modified can be used as dyke soil;
It is mixed using third curing agent with walk, the soil of finished product made of being modified can be used as road soil.
In short, as needed, different curing agent can be selected.Any curing agent is specifically selected, is depended on the needs.At this
In embodiment, selection is third curing agent, and after mixing with walk, the soil of finished product made of being modified can be used as road soil.
Claims (6)
1. river and lake silt integrated treatment unit, it is characterised in that: including sorting mechanism, flocculation basin, dewaterer and curing, sieve
Select between mechanism and flocculation basin, flocculation basin is connected by dredge pump between dewaterer, the dewaterer is by conveyer and curing
It is connected.
2. river and lake silt integrated treatment unit as described in claim 1, it is characterised in that: the sorting mechanism is vibrating screen
Or mud sump is deposited in drum screen, sorting mechanism lower section, the Chi Kou for depositing mud sump is corresponding on perpendicular direction with sorting mechanism;It is described to deposit mud
It is connected between pond and flocculation basin by a dredge pump.
3. river and lake silt integrated treatment unit as described in claim 1, it is characterised in that: the flocculation basin contain pond body and
First blender.
4. river and lake silt integrated treatment unit as described in claim 1, it is characterised in that: the dewaterer is high pressure sheet frame
Filter press or supercentrifuge.
5. river and lake silt integrated treatment unit as described in claim 1, it is characterised in that: the conveyer is helical feed
Machine or belt conveyor.
6. river and lake silt integrated treatment unit as described in claim 1, it is characterised in that: the curing contains storage hopper dredger
With the second blender.
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109704540A (en) * | 2019-02-01 | 2019-05-03 | 江苏聚慧科技有限公司 | River and lake silt integral treatment method and device |
CN114057441A (en) * | 2021-12-21 | 2022-02-18 | 浙江理工大学 | Device and method for regenerating filling material by using solid waste |
-
2019
- 2019-02-01 CN CN201920158844.7U patent/CN209619165U/en active Active
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109704540A (en) * | 2019-02-01 | 2019-05-03 | 江苏聚慧科技有限公司 | River and lake silt integral treatment method and device |
CN114057441A (en) * | 2021-12-21 | 2022-02-18 | 浙江理工大学 | Device and method for regenerating filling material by using solid waste |
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