CN107601799A - River bottom mud administering method on the spot - Google Patents
River bottom mud administering method on the spot Download PDFInfo
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- CN107601799A CN107601799A CN201711099341.9A CN201711099341A CN107601799A CN 107601799 A CN107601799 A CN 107601799A CN 201711099341 A CN201711099341 A CN 201711099341A CN 107601799 A CN107601799 A CN 107601799A
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- Prior art keywords
- river bottom
- mud
- packing layer
- sludge
- bed mud
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Abstract
The present invention proposes a kind of river bottom mud administering method on the spot, comprises the following steps：River bottom mud is extracted, river bottom mud is inactivated by inactivating device, kills the poisonous and harmful substance in river bottom mud；Bed mud after inactivation is mixed according to a certain percentage with adjuvant, bed mud mixture is made, adjuvant is used to adjust carbon-nitrogen ratio；By the packing layer in mixed bed mud mixture injection sludge filtration pond, put and stand a couple of days in the sun, muddy water and beavy metal impurity in bed mud mixture penetrate down into packing layer due to gravity, beavy metal impurity in packing layer absorption bed mud mixture, filtering is realized, the water being then discharged out after filtering；After standing a couple of days, the content of beary metal of the sludge above packing layer is detected, and prepares the compost of plant.The present invention is by the way of the administration way of physical absorption is compared and administered using chemical reaction, and more environmentally friendly, safer, cost is lower.
Description
Technical field
The present invention relates to river regulation technical field, more particularly to a kind of river bottom mud administering method on the spot.
Background technology
With《City black and odorous water renovation guide》Issue, the improvement of black and odorous water in China exists
In progress like a raging fire, the areas such as bigger Haikou, Foochow are especially influenceed in recent years.In governance process, desilting is dredged
The river bottom mud for dredging out increasingly attracts people's attention.The polluted bed mud quantity in waters is quite big, and constant real estate
It is raw, if do not cleared up, it will gradually spread whole river course waters.It is contemplated that forthcoming years river lake and offshore waters comprehensive improvement
And substantial amounts of Dredged bed mud will be produced in water environment engineering turn into and be difficult to the reality avoided.
Because the riverbed sludge moisture content of dredging out is high, low intensity, also contain poisonous and harmful substance sometimes, its is rational
Processing is increasingly paid close attention to by each side.With the horizontal raising of urban industry and resident, river, channel, pipeline, lake,
In the waters such as reservoir and coastal waters import sewage quantity increase year by year, carried in these sewage many heavy metals, organic matter, N,
The pollutants such as P, under a series of physical chemical thermogenesis, a part of accumulation of pollutants causes bed mud dirty into riverbed sludge
Dye.When being handled using conventional method the river bottom mud that these dredge out, the poisonous and harmful substance that bed mud contains is such as
What is killed, and how the heavy metal pollution problem in river bottom mud is controlled, and is increasingly taken seriously.
The content of the invention
The purpose of the present invention is intended at least solve one of described technological deficiency.
Therefore, it is an object of the invention to propose a kind of river bottom mud administering method on the spot, solves river training bed mud
The problem of refractory reason, effectively administered on the spot.
To achieve these goals, the present invention provides a kind of river bottom mud administering method on the spot, comprises the following steps：
Step S1, river bottom mud is extracted, river bottom mud is inactivated by inactivating device, kill having in river bottom mud
Malicious harmful substance；
Step S2, the bed mud after inactivation is mixed according to a certain percentage with adjuvant, bed mud mixture is made, adjuvant is used
In regulation carbon-nitrogen ratio, promote microorganism growth, and increase bed mud gap, contribute to the drainage of water；Adjuvant comprise at least stalk,
One or more in sawdust；
Step S3, the packing layer that mixed bed mud mixture is injected in sludge filtration pond, puts and stands number in the sun
My god, muddy water and beavy metal impurity in bed mud mixture penetrate down into packing layer, packing layer absorption bed mud mixing due to gravity
Beavy metal impurity in thing, filtering is realized, the water being then discharged out after filtering；
After standing a couple of days, the content of beary metal of the sludge above packing layer is detected；
If content of beary metal is not up to national standard, return in step S1, by below standard sludge, with extraction
After river bottom mud mixing, then inactivated by inactivating device, then detect content of beary metal again after step S2-S3 processing successively,
Untill being up to state standards；
If content of beary metal is up to state standards, the sludge above packing layer is separated with packing layer, for preparing
The compost of plant.
Further, inactivating device is at least from the one or more in sterilizer, medicament antivirus equipment；
When from sterilizer, inactivation regulation temperature >=121 DEG C, pressure >=1.05kg/cm3, inactivation time >=30min；
When drug of choice agent kill virus equipment when, medicament antivirus equipment use into bed mud add lime inactivated, bed mud with
The ratio of lime is 1：1~10:1, stirring at normal temperature 20min~1h.
Further, the bed mud after inactivation with adjuvant according to weight than 5：1~10:1 ratio mixing.
Further, the packing layer in sludge filtration pond is at least by one kind in haydite, cinder, volcanic rock, activated carbon or several
Kind material mixing forms.
Further, the volume that packing layer adds filler is the 1/10~1/3 of sludge filtration pond body product.
Further, the time of repose after the packing layer in mixed bed mud mixture injection sludge filtration pond is 3~7
My god.
Further, the packing layer in sludge filtration pond regularly change and clear up.
Further, the top in sludge filtration pond is provided with packing layer, and the lower section in sludge filtration pond is provided with waste water collection device,
Waste water collection device is connected with water pump, for excluding the water after filtering.
Further, sludge filtration pond using it is removable, can on-site consolidation structure；After reaching the spot, scene overlap joint sludge
Filtering ponds；After Treatment of Sludge, cleaning dismounting sludge filtration pond, packing and transporting.
The invention has the advantages that：
1st, the present invention is inactivated river bottom mud using inactivating device is existing, kills the venomous injurant in river bottom mud
Matter, help to eliminate the stink of river bottom mud, good working environment is provided for subsequent job personnel.
2nd, the present invention mixes the bed mud after inactivation with adjuvant according to a certain percentage, and adding the benefit of adjuvant is：1)
Carbon-nitrogen ratio can be adjusted, promotes microorganism growth, passes through the polluter in microbial digestion bed mud；2) because adjuvant uses
The material compositions such as stalk, sawdust, after being mixed with bed mud, bed mud gap can be increased, contribute to the drainage of water, be advantageous to bed mud
In water quickly penetrate down into during packing layer filtered, shorten time of repose, and then shorten the sludge handling time, at raising
Manage efficiency.
3rd, packing layer of the invention uses the mixture of one or more of materials such as haydite, cinder, volcanic rock, activated carbon,
Acted on using their absorption heavy metal, adsorb the heavy metal in bed mud, reach the purpose of river bottom mud improvement, the present invention uses
The administration way of physical absorption compares the mode administered using chemical reaction, and more environmentally friendly, safer, cost is lower.
4th, the river bottom mud after improvement can be prepared into compost by the present invention, for planting plants, can be turned waste into wealth,
Reach the recycling of sludge resource.
5th, sludge filtration pond of the invention using it is removable, can on-site consolidation structure, be readily transported and scene administered.
6th, the method that river bottom mud of the invention is administered on the spot, it is easy to accomplish, can be according to by the actual feelings in improvement river course
Condition chooses adjuvant on the spot；Governance efficiency can be greatly improved, shortens and administers the time, reduces difficulty of governance.
7th, the river bottom mud after the present invention administers is to dry the bed mud after standing filtering a couple of days, and its moisture greatly reduces, by force
Degree greatly enhances, it is easier to transports, solves the problems, such as the difficult transport of the bed mud after traditional river regulation.
The additional aspect of the present invention and advantage will be set forth in part in the description, and will partly become from the following description
Obtain substantially, or recognized by the practice of the present invention.
Brief description of the drawings
The above-mentioned and/or additional aspect and advantage of the present invention will become in the description from combination accompanying drawings below to embodiment
Substantially and it is readily appreciated that, wherein：
Fig. 1 is the broad flow diagram of the present invention；
Embodiment
Embodiments of the invention are described below in detail, the example of the embodiment is shown in the drawings, wherein from beginning to end
Same or similar label represents same or similar element or the element with same or like function.Below with reference to attached
The embodiment of figure description is exemplary, it is intended to for explaining the present invention, and is not considered as limiting the invention.
The present invention provides a kind of river bottom mud administering method on the spot, shown in refer to the attached drawing 1, comprises the following steps：
Step S1, river bottom mud is extracted, river bottom mud is inactivated by inactivating device, kill having in river bottom mud
Malicious harmful substance；Contribute to the stink of elimination river bottom mud, good working environment is provided for subsequent job personnel.
Inactivating device is at least from the one or more in sterilizer, medicament antivirus equipment；It can also be gone out using others
Removable mounting is put.
When from sterilizer, inactivation regulation temperature >=121 DEG C, pressure >=1.05kg/cm3, inactivation time >=30min.
When drug of choice agent kill virus equipment when, medicament antivirus equipment use into bed mud add lime inactivated, bed mud with
The ratio of lime is 1：1~10:1, stirring at normal temperature 20min~1h.
Step S2, the bed mud after inactivation is mixed according to a certain percentage with adjuvant, bed mud mixture is made, adjuvant is used
In regulation carbon-nitrogen ratio, promote microorganism growth, moreover it is possible to increase bed mud gap, contribute to the drainage of water.Adjuvant comprises at least straw
One or more in stalk, sawdust, can also carry out choosing other according to scene can increase the adjuvant of carbon-nitrogen ratio.Be advantageous to
Water in bed mud is quickly penetrated down into during packing layer filtered, and shortens time of repose, and then shortens the sludge handling time, is carried
High treatment efficiency.
Bed mud after inactivation is with adjuvant according to weight than 5：1~10:1 ratio mixing.
Step S3, the packing layer that mixed bed mud mixture is injected in sludge filtration pond, puts and stands number in the sun
My god, muddy water and beavy metal impurity in bed mud mixture penetrate down into packing layer, packing layer absorption bed mud mixing due to gravity
Beavy metal impurity in thing, filtering is realized, the water being then discharged out after filtering；Wherein, the packing layer in sludge filtration pond is at least by making pottery
One or more of material mixings in grain, cinder, volcanic rock, activated carbon form.And the volume of packing layer addition filler is sludge
The 1/10~1/3 of filtering ponds volume.
During standing, the heavy metal in bed mud mixture precipitate at first haydite in filled layer, cinder, volcanic rock,
The materials such as activated carbon adsorb；After standing a couple of days, the content of beary metal of the sludge above packing layer is detected；
If content of beary metal is not up to national standard, return in step S1, by below standard sludge, with extraction
After river bottom mud mixing, then inactivated by inactivating device, then detect content of beary metal again after step S2-S3 processing successively,
Untill being up to state standards.
If content of beary metal is up to state standards, the sludge above packing layer is separated with packing layer, for preparing
The compost of plant.Compost can be used for planting the plants such as tomato, cactus with globular, gardenia.
In addition, the time of repose after packing layer in mixed bed mud mixture injection sludge filtration pond is 3~7 days.
The top in sludge filtration pond is provided with packing layer, and the lower section in sludge filtration pond is provided with waste water collection device, wastewater collection
Device is connected with water pump, for discharging the water after filtering.And the packing layer in sludge filtration pond regularly change and clear up.
Sludge filtration pond using it is removable, can on-site consolidation structure；After reaching the spot, sludge filtration pond is overlapped at the scene,
After Treatment of Sludge, cleaning dismounting sludge filtration pond, packing and transporting.
Illustrate such scheme below by three embodiments：
Embodiment one
The process that river bottom mud after being dredged to certain city of northern China is administered is as follows：
First, river bottom mud is extracted, the poisonous and harmful substance in bed mud is inactivated by sterilizer.Then after inactivating
Bed mud and sawdust according to 7:1 ratio mixing, turns into bed mud mixture.Load 1/8 in packed layer in sludge filtration pond
The cinder of sludge filtration pond body product.Bed mud mixture is injected in the packed layer in sludge filtration pond again.After 5 days being stood under sunlight,
The content of beary metal in sludge is detected, if be up to state standards, the sludge above packed layer is separated with packing layer, is prepared
Into the compost of plant, if not up to national standard, after being mixed again with river bottom mud, inactivated, then according to upper
State step to handle again, untill the content of beary metal in the sludge of detection is up to state standards.
Embodiment two
The process administered to the river bottom mud after southern certain city dredging is as follows：
First, river bottom mud is extracted, the poisonous and harmful substance in bed mud is inactivated by sterilizer.Bed mud after inactivation
With stalk according to 5:1 ratio mixing, turns into bed mud mixture.Load the haydite of 1/5 volume in sludge filtration pond.Bed mud
In mixture injection sludge filtration pond.After standing 7 days under sunlight, the content of beary metal in sludge is detected, if reaching national mark
Standard, then the sludge above packed layer is separated with packing layer, be prepared into the compost of plant, if not up to national standard,
After being mixed again with river bottom mud, inactivated, then handled again according to above-mentioned steps, the huge sum of money in the sludge of detection
Untill category content is up to state standards.
Embodiment three
The process administered to the river bottom mud after southern certain city dredging is as follows：
First, river bottom mud is extracted, the poisonous and harmful substance in bed mud is inactivated by sterilizer.Sludge after inactivation
With stalk according to 8:1 ratio mixing, turns into bed mud mixture.Load the volcanic rock of 1/7 volume in sludge filtration pond.The bottom of
In mud mixture injection sludge filtration pond.7 days are stood under sunlight.The content of beary metal in sludge is detected, if reaching national mark
Standard, then the sludge above packed layer is separated with packing layer, be prepared into the compost of plant, if not up to national standard,
After being mixed again with river bottom mud, inactivated, then handled again according to above-mentioned steps, the huge sum of money in the sludge of detection
Untill category content is up to state standards.
The packing layer of the present invention is using the mixture of one or more of materials such as haydite, cinder, volcanic rock, activated carbon, profit
Acted on their absorption heavy metal, adsorb the heavy metal in bed mud, reach the purpose of river bottom mud improvement, the present invention uses thing
The administration way of reason absorption compares the mode administered using chemical reaction, and more environmentally friendly, safer, cost is lower, and administration way is more
Simply.
Although embodiments of the invention have been shown and described above, it is to be understood that above-described embodiment is example
Property, it is impossible to limitation of the present invention is interpreted as, one of ordinary skill in the art is not departing from the principle and objective of the present invention
In the case of above-described embodiment can be changed within the scope of the invention, change, replace and modification.The scope of the present invention
By appended claims and its equivalent limit.
Claims (9)
1. a kind of river bottom mud administering method on the spot, it is characterised in that comprise the following steps：
Step S1, river bottom mud is extracted, river bottom mud is inactivated by inactivating device, kill poisonous having in river bottom mud
Evil material；
Step S2, the bed mud after inactivation is mixed according to a certain percentage with adjuvant, bed mud mixture is made, adjuvant is used to adjust
Carbon-nitrogen ratio is saved, promotes microorganism growth, and increases bed mud gap, contributes to the drainage of water；Adjuvant comprises at least stalk, sawdust
In one or more；
Step S3, the packing layer that mixed bed mud mixture is injected in sludge filtration pond, puts and stands a couple of days in the sun, bottom
Muddy water and beavy metal impurity in mud mixture are because gravity penetrates down into packing layer, in packing layer absorption bed mud mixture
Beavy metal impurity, filtering is realized, the water being then discharged out after filtering；
After standing a couple of days, the content of beary metal of the sludge above packing layer is detected；
If content of beary metal is not up to national standard, return in step S1, by below standard sludge, the river course with extraction
After bed mud mixing, then inactivated by inactivating device, then detect content of beary metal again after step S2-S3 processing successively, until
Untill being up to state standards；
If content of beary metal is up to state standards, the sludge above packing layer is separated with packing layer, for preparing plant
Compost.
2. river bottom mud as claimed in claim 1 administering method on the spot, it is characterised in that：Inactivating device is at least from sterilizing
One or more in device, medicament antivirus equipment；
When from sterilizer, inactivation regulation temperature >=121 DEG C, pressure >=1.05kg/cm3, inactivation time >=30min；
When equipment is killed virus in drug of choice agent, medicament antivirus equipment uses the addition lime into bed mud to be inactivated, bed mud and lime
Ratio be 1：1~10:1, stirring at normal temperature 20min~1h.
3. river bottom mud as claimed in claim 1 administering method on the spot, it is characterised in that：Bed mud after inactivation is pressed with adjuvant
According to weight than 5：1~10:1 ratio mixing.
4. river bottom mud as claimed in claim 1 administering method on the spot, it is characterised in that：The packing layer in sludge filtration pond is at least
Formed by one or more of material mixings in haydite, cinder, volcanic rock, activated carbon.
5. river bottom mud as described in claim 1 or 4 administering method on the spot, it is characterised in that：Packing layer adds the body of filler
Product is the 1/10~1/3 of sludge filtration pond body product.
6. river bottom mud as claimed in claim 1 administering method on the spot, it is characterised in that：Mixed bed mud mixture injection
The time of repose after packing layer in sludge filtration pond is 3~7 days.
7. river bottom mud as claimed in claim 1 administering method on the spot, it is characterised in that：Packing layer in sludge filtration pond enters
Row is regularly changed and cleared up.
8. river bottom mud as claimed in claim 1 administering method on the spot, it is characterised in that：The top in sludge filtration pond is provided with and filled out
The bed of material, the lower section in sludge filtration pond are provided with waste water collection device, and waste water collection device is connected with water pump, after discharging filtering
Water.
9. river bottom mud as claimed in claim 1 administering method on the spot, it is characterised in that：Sludge filtration pond using it is removable,
Can on-site consolidation structure；After reaching the spot, scene overlap joint sludge filtration pond；After Treatment of Sludge, cleaning dismounting sludge filtration pond,
Packing and transporting.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711099341.9A CN107601799A (en) | 2017-11-09 | 2017-11-09 | River bottom mud administering method on the spot |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711099341.9A CN107601799A (en) | 2017-11-09 | 2017-11-09 | River bottom mud administering method on the spot |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN107601799A true CN107601799A (en) | 2018-01-19 |
Family
ID=61086026
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201711099341.9A Pending CN107601799A (en) | 2017-11-09 | 2017-11-09 | River bottom mud administering method on the spot |
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110156288A (en) * | 2019-05-31 | 2019-08-23 | 中运建设控股有限公司 | A kind of administering method of river and lake sludge |
| CN110642486A (en) * | 2019-11-01 | 2020-01-03 | 界首市官星环保科技有限公司 | Sludge treatment method |
Citations (5)
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|---|---|---|---|---|
| JP2003236597A (en) * | 2002-02-20 | 2003-08-26 | Fuji Eng Kk | Method for filtering water which contains heavy metal when mud which contains heavy metal is dehydrated |
| JP2006231285A (en) * | 2005-02-28 | 2006-09-07 | Toyo Constr Co Ltd | Gravity filtration apparatus |
| JP2007326090A (en) * | 2006-06-06 | 2007-12-20 | Sawada Shoji | Water purifying and activating method in closed water area putting natural material to practical use and construction method therefor |
| CN101828512A (en) * | 2010-05-26 | 2010-09-15 | 北京师范大学 | Method of using lake sediment and coal slag as compost |
| CN105481221A (en) * | 2016-01-14 | 2016-04-13 | 上海交通大学 | Method for realizing anti-shrinkage recarburization sludge drying |
-
2017
- 2017-11-09 CN CN201711099341.9A patent/CN107601799A/en active Pending
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2003236597A (en) * | 2002-02-20 | 2003-08-26 | Fuji Eng Kk | Method for filtering water which contains heavy metal when mud which contains heavy metal is dehydrated |
| JP2006231285A (en) * | 2005-02-28 | 2006-09-07 | Toyo Constr Co Ltd | Gravity filtration apparatus |
| JP2007326090A (en) * | 2006-06-06 | 2007-12-20 | Sawada Shoji | Water purifying and activating method in closed water area putting natural material to practical use and construction method therefor |
| CN101828512A (en) * | 2010-05-26 | 2010-09-15 | 北京师范大学 | Method of using lake sediment and coal slag as compost |
| CN105481221A (en) * | 2016-01-14 | 2016-04-13 | 上海交通大学 | Method for realizing anti-shrinkage recarburization sludge drying |
Non-Patent Citations (2)
| Title |
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| 王学刚等: "《水处理工程 下》", 31 January 2015, 中国环境科学出版社 * |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110156288A (en) * | 2019-05-31 | 2019-08-23 | 中运建设控股有限公司 | A kind of administering method of river and lake sludge |
| CN110156288B (en) * | 2019-05-31 | 2022-10-28 | 中运建设控股有限公司 | Treatment method of river and lake sludge |
| CN110642486A (en) * | 2019-11-01 | 2020-01-03 | 界首市官星环保科技有限公司 | Sludge treatment method |
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Application publication date: 20180119 |