CN107150064B - A kind of processing system and method for oxide scale residue - Google Patents
A kind of processing system and method for oxide scale residue Download PDFInfo
- Publication number
- CN107150064B CN107150064B CN201710582760.1A CN201710582760A CN107150064B CN 107150064 B CN107150064 B CN 107150064B CN 201710582760 A CN201710582760 A CN 201710582760A CN 107150064 B CN107150064 B CN 107150064B
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- Prior art keywords
- waste water
- oxide
- oxide scale
- scale residue
- residue
- 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.)
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- 238000000034 method Methods 0.000 title abstract description 10
- 239000002351 wastewater Substances 0.000 claims abstract description 88
- 239000002893 slag Substances 0.000 claims abstract description 50
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 18
- 238000003672 processing method Methods 0.000 claims abstract description 7
- 229910000831 Steel Inorganic materials 0.000 claims description 54
- 239000010959 steel Substances 0.000 claims description 54
- 239000002699 waste material Substances 0.000 claims description 19
- 210000002421 cell wall Anatomy 0.000 claims description 11
- 230000004888 barrier function Effects 0.000 claims description 10
- 238000005096 rolling process Methods 0.000 claims description 9
- 239000002994 raw material Substances 0.000 claims description 8
- 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 claims description 7
- 230000003014 reinforcing effect Effects 0.000 claims description 5
- 239000002689 soil Substances 0.000 claims description 5
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 3
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 3
- 239000004568 cement Substances 0.000 claims description 3
- 230000008859 change Effects 0.000 claims description 3
- 239000004571 lime Substances 0.000 claims description 3
- 229910052760 oxygen Inorganic materials 0.000 claims description 3
- 239000001301 oxygen Substances 0.000 claims description 3
- 239000011347 resin Substances 0.000 claims description 3
- 229920005989 resin Polymers 0.000 claims description 3
- 239000004575 stone Substances 0.000 claims description 3
- 230000008595 infiltration Effects 0.000 claims description 2
- 238000001764 infiltration Methods 0.000 claims description 2
- 238000005406 washing Methods 0.000 claims 1
- 238000011010 flushing procedure Methods 0.000 abstract description 5
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 20
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 16
- 229910000519 Ferrosilicon Inorganic materials 0.000 description 8
- 229910052742 iron Inorganic materials 0.000 description 7
- 230000003647 oxidation Effects 0.000 description 5
- 238000007254 oxidation reaction Methods 0.000 description 5
- 238000004519 manufacturing process Methods 0.000 description 4
- 239000000843 powder Substances 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 241000251468 Actinopterygii Species 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- SZVJSHCCFOBDDC-UHFFFAOYSA-N ferrosoferric oxide Chemical compound O=[Fe]O[Fe]O[Fe]=O SZVJSHCCFOBDDC-UHFFFAOYSA-N 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 238000007670 refining Methods 0.000 description 2
- 230000032258 transport Effects 0.000 description 2
- 206010013786 Dry skin Diseases 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 229910045601 alloy Inorganic materials 0.000 description 1
- 239000000956 alloy Substances 0.000 description 1
- 229910052796 boron Inorganic materials 0.000 description 1
- 230000001413 cellular effect Effects 0.000 description 1
- 238000010924 continuous production Methods 0.000 description 1
- 230000001351 cycling effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 239000002932 luster Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B5/00—Operations not covered by a single other subclass or by a single other group in this subclass
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The present invention provides the processing system and its processing method of a kind of oxide scale residue, comprising: water flushing system, oxide skin waste water slag collecting tank, oxide scale residue stack slot, discharge of wastewater pipeline, the waste water circulatory system, oxide skin and shift forklift, Gang Zhao transportation system.Processing system and method provided by the invention can solve oxide scale residue existing in the prior art salvage mode is inconvenient, the oxide skin removal waste water period is long, wastewater trough is easily rupturable, not environmentally the problems such as.
Description
Technical field
The present invention relates to a kind of processing system of oxide scale residue and method more particularly to oxide scale residue drainings and transfer
System and method.
Background technique
Oxide skin is also known as iron scale, iron scale, is in heat steel and the operation of rolling, since surface is aoxidized and shape
At iron oxide layer, the fish scale-shaped object to get off is peeled off, external appearance characteristic is rigid gray pieces and grey black fine particle and powder, broken
Metallic luster is presented in piece, enbrittles, and fracture is in cellular.The main component of iron oxide is FeO, and contains a small amount of Fe3O4,
Sample main component is Fe 70.20%, Mn 0.49%, Ca 0.52%, Al 0.02%, Ti 0.02%, Cu 0.04%, and oxide skin
It is to necessarily lead in heat steel and the operation of rolling, does not can avoid, since its Fe content is higher, usually can be used as ferrosilicon
The raw materials for production of alloy or ferro-boron, the part that also can be used as blast furnace ironmaking add raw material.
It is mainly in the prior art that waste water for flushing collects oxide scale residue for the processing mode of oxide skin, it is then naturally dry
It is dry, when iron oxide water content is lower than 5% or less, it is just conveyed to raw material of the ferrosilicon factory as Antaciron, then due to steel heat
The process of rolling is usually whole day continuous production, can endlessly generate iron scale, and iron scale is usually mixed with waste water, defeated
It send to wastewater trough, wherein the content of waste water is up to 70 ~ 80%, accumulation after then salvaging the iron oxide waste residue in wastewater trough,
Oxide skin/(oxide skin+waste water) ratio is also up to 20 ~ 30%, and the way of usual steel rolling mill is heap after salvaging iron oxide waste residue
It puts, spontaneously dries evaporating waste water or by seeping waste water naturally, after usually standing 1 ~ 2 week, the water content of waste residue can just be lower than
5%, it is too long to stand the water removal time cycle.And for steel rolling mill, the iron oxide waste residue monthly generated is up to 1000 ~ 2000
Ton is such as handled not in time, can seriously be accumulated, and occupies workshop position, wastes land resource, and the oxide skin stacked be easy to cause powder
Dustiness dye (for the size of usual iron scale between 1mm ~ 5cm, wherein powder be easy to cause pollution, and wastes iron resource), this
Outside, other than natural evaporation, dry waste water, waste water can also penetrate into soil, cause land pollution, due to permeating for a long time, very
Be easy to cause the collapsing of wastewater trough, bring security risk (place that usual oxide scale residue is stacked close to wastewater trough, thousands of tons of
Waste residue will cause wastewater trough groove body rupture), i.e., existing processing iron oxide waste residue when have the following problems: (1) oxide skin dry
Period is too long;(2) oxide skin, which is stacked, occupies a large amount of soils;(3) seep to oxide skin waste water that there are security risks;(4) period is stacked
It is too long to will lead to dust pollution, iron resource waste;(4) oxide skin salvaging is mainly salvaged manually.
In addition, the departments such as State Environmental Protection Administration in No. 11 bulletins of publication in 2008 " limiting inlet class is available
Make the solid waste catalogue of raw material " in list the oxide skin of Rolling production, therefore oxide skin belongs to the solid of limiting inlet
Waste, value as it can be seen that it is reported that, in the production process of ferrosilicon, iron oxide as main raw materials requirement amount it is continuous on
It rises, the ferrosilicon of usual 75# is at 5000-7000 yuan/ton, and the price of oxide skin is at 400 ~ 900 yuan/ton, and ferrosilicon factory is for oxidation
The requirement of skin is that iron-content is higher than 65%, and water content is lower than 5%, and at this moment, there have been obvious problems: the iron oxide of steel plant contains
Water is excessively high, cannot dry and accumulate, the oxide skin that ferrosilicon factory needs largely to dry again in time, and steel plant cannot use specially
Drying equipment dries oxide skin waste water slag, and (mainly since water content is excessively high, and the oxide skin of thousands of tons of is set using drying
Standby dry, increased costs are 100 ~ 200 yuan/ton), therefore steel plant would generally handle oxidation using the method spontaneously dried
Skin, to restrict the production of ferrosilicon.
Summary of the invention
The purpose of the present invention is to provide a kind of processing system of oxide scale residue and methods, can solve with expectation existing
Oxide scale residue present in technology salvages that mode is inconvenient, the oxide skin removal waste water period is long, wastewater trough is easily rupturable, not environmentally etc.
Problem.
The technical solution used in the present invention is: a kind of processing system of oxide scale residue is provided, the oxide scale residue
Processing system includes: water flushing system, oxide skin waste water slag collecting tank, oxide scale residue stacking slot, discharge of wastewater pipeline, waste water
The circulatory system, oxide skin shift forklift, Gang Zhao transportation system.
Wherein, oxide skin waste water slag collecting tank be located at ground level hereinafter, slot bottom include by lime and plain local soil type at slot bottom
Layer, with a thickness of 20 ~ 25cm;Then it is laid with the impervious barrier being made of blinding and resin, on slot bottom layer with a thickness of 15 ~ 20cm;
Stone, cement, husky molecular concrete layer are finally poured on impervious barrier, cell wall is the concrete layer of steel reinforcing, oxidation
Skin waste water slag collecting tank is in upside-down trapezoid or square, and sink 15 ~ 20m of depth, sink, which is open, is not less than 15m*15m, and close to
Oxide scale residue stacks slot, and cell wall is equipped with several drainage holes, and drainage hole is located above slot bottom at 10 ~ 15m.
Wherein, oxide scale residue stacks slot close to oxide skin waste water slag collecting tank, and oxide scale residue stacks the cell wall of slot
Including concrete water mud layer, impervious barrier, the slot bottom of oxide skin waste water slag collecting tank is arc, and slot bottom is equipped with several useless with oxide skin
The drainage hole that grain slag collecting tank communicates.
Wherein, the aperture of drainage hole is 0.5-1.5cm, drainpipe PVC, PP or modified PVC, MODIFIED PP tubing.
Wherein, Gang Zhao transportation system includes the steel with waste water slag collecting tank to matched serpentine track, below track
Fortune of the steel pawl and steel pawl of the connection structure of pawl and steel pawl and track, crawl and release oxide scale residue in serpentine track
It is dynamic to be manipulated by computer terminal.
The present invention also provides a kind of processing methods of oxide scale residue: (1) when oxide scale residue that steel rolling generate excessive,
Oxide scale residue is washed away through chute to oxide skin waste water slag collecting tank using waste water;(2) timing controlled is using steel pawl along snakelike
It is moved on track, decentralization steel pawl is in groove body waste water slag, being closed steel pawl, and grabbing groove bottom waste water slag, rise steel pawl, steel pawl is with track
It is moved to oxide scale residue to stack above slot, transfers steel pawl, open steel pawl, discharge waste water slag, rise steel pawl, return, repeatedly will
The waste water slag of oxide skin waste water slag collecting tank, which is transported to oxide scale residue, stacks slot;(3) oxide scale residue stacks the oxidation in slot
Skin is separated with waste water, and waste water returns to oxide skin waste water slag collecting tank through pipeline along the drainage hole that oxide scale residue stacks slot slot bottom;
(4) oxide scale residue is shifted using oxide skin transfer forklift, the raw material as Antaciron refining;(5) oxide skin waste water slag
Upper layer waste water in collecting tank can be recycled in water flushing system.
The beneficial effects of adopting the technical scheme are that
(1) cell wall of oxide skin waste water slag collecting tank is the concrete layer of steel reinforcing, and oxide scale residue is stacked under slot
The reason of portion is equipped with impervious barrier, will not be because of infiltration, causes oxide skin waste water slag to collect the rupture of groove groove wall;
(2) waste water returns to oxide skin waste water slag collecting tank through pipeline along the drainage hole that oxide scale residue stacks slot slot bottom, adds
The speed separation of oxide scale residue and waste water, separation cycle are 1 ~ 2 day, the water content of oxide scale residue within the scope of 3 ~ 5wt.%,
It can directly transport to ferrosilicon factory;
(3) it is equipped with snakelike conveying track in the top of oxide skin waste water slag collecting tank, steel pawl is allow to transfer to oxide skin
Any corner of waste water slag collecting tank, and steel pawl is entirely grabbing, and transports, is controlled during release by computer terminal, drops
Low manpower consumption is, it can be achieved that continuously fish out slag process;
(4) since oxide skin and waste water separation cycle shorten significantly, reduce waste residue occupied area, and be beneficial to prevent ring
Border pollution;
(5) cycling utilization of wastewater reduces water resource waste, realizes reusing of energy source, can not only economize on resources, but also can reduce pair
The pollution of environment.
Detailed description of the invention
Fig. 1 is the processing system schematic diagram of oxide scale residue.Appended drawing reference: 1 serpentine track;2 steel pawls;3 waste water chutes;4
The concrete layer of steel reinforcing;5 impervious barriers;6 oxide scale residues;7 waste water;8 drainage pipelines;9 forklifts;10 concrete layers.
Fig. 2 is the drainage hole enlarged drawing of the cell wall of oxide skin waste water slag collecting tank.
Fig. 3 is a kind of processing system flow chart of oxide scale residue.
Specific embodiment
A kind of processing system of oxide scale residue, the processing system of the oxide scale residue include: water flushing system, oxide skin
Waste water slag collecting tank, oxide scale residue stack slot, discharge of wastewater pipeline, the waste water circulatory system, oxide skin transfer forklift, steel pawl fortune
Defeated system.Wherein oxide skin waste water slag collecting tank be located at ground level hereinafter, slot bottom include by lime and plain local soil type at slot bottom layer,
With a thickness of 20 ~ 25cm;Then it is laid with the impervious barrier being made of blinding and resin, on slot bottom layer with a thickness of 15 ~ 20cm;Most
Stone, cement, husky molecular concrete layer are poured on impervious barrier afterwards, cell wall is the concrete layer of steel reinforcing, oxide skin
Waste water slag collecting tank is in upside-down trapezoid or square, sink 15 ~ 20m of depth, and sink opening is not less than 15m*15m, and close to oxygen
Change skin waste residue and stack slot, cell wall is equipped with several drainage holes, and drainage hole is located above slot bottom at 10 ~ 15m.Oxide scale residue is stacked
Slot is close to oxide skin waste water slag collecting tank, and it includes concrete water mud layer, impervious barrier, oxidation that oxide scale residue, which stacks the cell wall of slot,
The slot bottom of skin waste water slag collecting tank is arc, and slot bottom is equipped with several drainage holes communicated with oxide skin waste water slag collecting tank, draining
The aperture in hole is 0.5-1.5cm, drainpipe PVC, PP or modified PVC, MODIFIED PP tubing;Gang Zhao transportation system includes and waste water
To matched serpentine track, the connection structure of steel pawl and steel pawl and track below track is grabbed and is released slag collecting tank
The movement of the steel pawl and steel pawl of oxide scale residue in serpentine track is put to be manipulated by computer terminal.
A kind of processing method of oxide scale residue, (1) when the oxide scale residue that steel rolling generates is excessive, using waste water by oxygen
Change skin waste residue to wash away through chute to oxide skin waste water slag collecting tank;(2) timing controlled is moved in serpentine track using steel pawl, under
Steel pawl is put in groove body waste water slag, closure steel pawl, grabbing groove bottom waste water slag rises steel pawl, and steel pawl is moved to oxide skin with track
Waste residue is stacked above slot, and steel pawl is transferred, and opens steel pawl, discharges waste water slag, rises steel pawl, is returned, repeatedly by oxide skin waste water slag
The waste water slag of collecting tank, which is transported to oxide scale residue, stacks slot;(3) oxide skin that oxide scale residue is stacked in slot is separated with waste water,
Waste water returns to oxide skin waste water slag collecting tank through pipeline along the drainage hole that oxide scale residue stacks slot slot bottom, and oxide scale residue is stood
After 1 ~ 2 day, the water content in waste residue is within the scope of 3 ~ 5wt.%;(4) oxide scale residue is shifted using oxide skin transfer forklift,
Raw material as Antaciron refining;(5) the upper layer waste water in oxide skin waste water slag collecting tank, which can be recycled to wash away in water, is
System.
Specific embodiments of the present invention are described in detail above, but it is merely an example, the present invention is simultaneously unlimited
It is formed on particular embodiments described above.To those skilled in the art, any couple of present invention carries out equivalent modifications and
Substitution is also all among scope of the invention.Therefore, without departing from the spirit and scope of the invention made by equal transformation and
Modification, all should be contained within the scope of the invention.
Claims (4)
1. a kind of processing method of oxide scale residue, it is characterised in that the following steps are included: (1) is useless when the oxide skin that steel rolling generates
When slag is excessive, oxide scale residue is washed away through chute to oxide skin waste water slag collecting tank using waste water;(2) control steel pawl is in snakelike
It is moved on track, for decentralization steel pawl in groove body oxide scale residue, closure steel pawl, grabbing groove bottom oxide scale residue rises steel pawl, steel
Pawl is moved to oxide scale residue along track and stacks above slot, transfers steel pawl, opens steel pawl, discharge oxide scale residue, rises steel pawl,
It returns, repeatedly the oxide scale residue of oxide skin waste water slag collecting tank is transported to oxide scale residue and stacks slot stacking;(3) oxide skin
The oxide scale residue that waste residue is stacked in slot is separated with waste water, and waste water is returned along the drainage hole that oxide scale residue stacks slot slot bottom through pipeline
It is back to oxide skin waste water slag collecting tank;(4) oxide scale residue is shifted using oxide skin transfer forklift, is refined as Antaciron
Raw material;(5) upper layer waste water in oxide skin waste water slag collecting tank is recycled in washing away oxide scale residue through chute to oxygen
Change skin waste water slag collecting tank, wherein oxide skin waste water slag collecting tank is located at ground level hereinafter, slot bottom includes by lime and plain local soil type
At slot bottom layer, with a thickness of 20 ~ 25cm;Then the impervious barrier being made of blinding and resin is laid on slot bottom layer, with a thickness of
15~20cm;Stone, cement, husky molecular concrete layer are finally poured on impervious barrier, cell wall is the concrete of steel reinforcing
Layer, oxide skin waste water slag collecting tank are in upside-down trapezoid or square, and sink 15 ~ 20m of depth, sink, which is open, is not less than 15m*15m,
And slot is stacked close to oxide scale residue, cell wall is equipped with several drainage holes, and drainage hole is located above slot bottom at 10 ~ 14m, oxide skin
Waste residue stacks slot close to oxide skin waste water slag collecting tank, and the cell wall of oxide scale residue stacking slot includes concrete water mud layer, prevents
Infiltration layer, the slot bottom that oxide scale residue stacks slot is arc, and slot bottom is equipped with several drainings communicated with oxide skin waste water slag collecting tank
Hole.
2. a kind of processing method of oxide scale residue as described in claim 1, it is characterised in that the aperture of drainage hole is 0.5-
1.5cm, pipeline PVC, PP, modified PVC or MODIFIED PP tubing.
3. a kind of processing method of oxide scale residue as claimed in claim 2, it is characterised in that crawl and release oxide skin are useless
Movement of the steel pawl and steel pawl of slag in serpentine track is manipulated by computer terminal.
4. a kind of processing method of oxide scale residue as described in claim 1, it is characterised in that the oxide skin after forklift transfer
The water content of waste residue is 3 ~ 5wt.%.
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CN201710582760.1A CN107150064B (en) | 2017-07-17 | 2017-07-17 | A kind of processing system and method for oxide scale residue |
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CN201710582760.1A CN107150064B (en) | 2017-07-17 | 2017-07-17 | A kind of processing system and method for oxide scale residue |
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CN107150064A CN107150064A (en) | 2017-09-12 |
CN107150064B true CN107150064B (en) | 2019-12-03 |
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---|---|---|---|---|
NL174642C (en) * | 1975-04-07 | 1984-07-16 | Estel Hoogovens Bv | METHOD AND APPARATUS FOR GRANULATING MAIN OVEN SNAIL. |
JPS60141655A (en) * | 1983-12-29 | 1985-07-26 | 日本鋼管株式会社 | Manufacture of water granulated slag |
CN1384211A (en) * | 2001-05-01 | 2002-12-11 | 重庆钢铁设计研究院 | Blast furnace slag treating system |
CN103331046A (en) * | 2013-07-19 | 2013-10-02 | 中冶南方工程技术有限公司 | Novel efficient dewatering bin and dewatering method |
CN203304268U (en) * | 2013-05-13 | 2013-11-27 | 天津康斯明节能环保科技有限公司 | Equipment for treating household garbage incinerating power generation furnace slag |
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CN205313582U (en) * | 2016-01-28 | 2016-06-15 | 包钢集团设计研究院(有限公司) | Secondary dewatering device |
CN206069906U (en) * | 2016-08-31 | 2017-04-05 | 云南德胜钢铁有限公司 | A kind of blast-furnace slag processing system |
Family Cites Families (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN202912386U (en) * | 2012-11-22 | 2013-05-01 | 福建省工业设备安装有限公司 | Impulse type boiler slag-flushing system without dust and discharge water |
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2017
- 2017-07-17 CN CN201710582760.1A patent/CN107150064B/en not_active Expired - Fee Related
Patent Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
NL174642C (en) * | 1975-04-07 | 1984-07-16 | Estel Hoogovens Bv | METHOD AND APPARATUS FOR GRANULATING MAIN OVEN SNAIL. |
JPS60141655A (en) * | 1983-12-29 | 1985-07-26 | 日本鋼管株式会社 | Manufacture of water granulated slag |
CN1384211A (en) * | 2001-05-01 | 2002-12-11 | 重庆钢铁设计研究院 | Blast furnace slag treating system |
CN203304268U (en) * | 2013-05-13 | 2013-11-27 | 天津康斯明节能环保科技有限公司 | Equipment for treating household garbage incinerating power generation furnace slag |
CN103331046A (en) * | 2013-07-19 | 2013-10-02 | 中冶南方工程技术有限公司 | Novel efficient dewatering bin and dewatering method |
CN203683563U (en) * | 2013-12-17 | 2014-07-02 | 秦冶工程技术(北京)有限责任公司 | Bottom filtering device for flushing slag of blast furnace |
CN205313582U (en) * | 2016-01-28 | 2016-06-15 | 包钢集团设计研究院(有限公司) | Secondary dewatering device |
CN206069906U (en) * | 2016-08-31 | 2017-04-05 | 云南德胜钢铁有限公司 | A kind of blast-furnace slag processing system |
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