CN106564998B - Regenerated plastics high concentration alkali water zero discharge treatment process - Google Patents
Regenerated plastics high concentration alkali water zero discharge treatment process Download PDFInfo
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- CN106564998B CN106564998B CN201610934992.4A CN201610934992A CN106564998B CN 106564998 B CN106564998 B CN 106564998B CN 201610934992 A CN201610934992 A CN 201610934992A CN 106564998 B CN106564998 B CN 106564998B
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 90
- 229920003023 plastic Polymers 0.000 title claims abstract description 46
- 239000004033 plastic Substances 0.000 title claims abstract description 46
- 238000000034 method Methods 0.000 title claims abstract description 14
- 208000028659 discharge Diseases 0.000 title claims abstract description 12
- 239000003513 alkali Substances 0.000 title claims abstract description 11
- 230000008569 process Effects 0.000 title claims abstract description 8
- 239000010802 sludge Substances 0.000 claims abstract description 58
- 238000004140 cleaning Methods 0.000 claims abstract description 23
- 239000000725 suspension Substances 0.000 claims abstract description 15
- 239000010865 sewage Substances 0.000 claims abstract description 13
- 238000011084 recovery Methods 0.000 claims abstract description 10
- 238000003825 pressing Methods 0.000 claims abstract description 7
- 108010010803 Gelatin Proteins 0.000 claims description 12
- 229920000159 gelatin Polymers 0.000 claims description 12
- 239000008273 gelatin Substances 0.000 claims description 12
- 235000019322 gelatine Nutrition 0.000 claims description 12
- 235000011852 gelatine desserts Nutrition 0.000 claims description 12
- 238000002156 mixing Methods 0.000 claims description 11
- 239000000203 mixture Substances 0.000 claims description 9
- 238000007789 sealing Methods 0.000 claims description 8
- 239000000843 powder Substances 0.000 claims description 6
- 238000004321 preservation Methods 0.000 claims description 6
- RSWGJHLUYNHPMX-UHFFFAOYSA-N Abietic-Saeure Natural products C12CCC(C(C)C)=CC2=CCC2C1(C)CCCC2(C)C(O)=O RSWGJHLUYNHPMX-UHFFFAOYSA-N 0.000 claims description 5
- 229920000168 Microcrystalline cellulose Polymers 0.000 claims description 5
- KHPCPRHQVVSZAH-HUOMCSJISA-N Rosin Natural products O(C/C=C/c1ccccc1)[C@H]1[C@H](O)[C@@H](O)[C@@H](O)[C@@H](CO)O1 KHPCPRHQVVSZAH-HUOMCSJISA-N 0.000 claims description 5
- 239000010425 asbestos Substances 0.000 claims description 5
- 239000004203 carnauba wax Substances 0.000 claims description 5
- 125000005456 glyceride group Chemical group 0.000 claims description 5
- 230000008676 import Effects 0.000 claims description 5
- 235000019813 microcrystalline cellulose Nutrition 0.000 claims description 5
- 239000003595 mist Substances 0.000 claims description 5
- 229910052895 riebeckite Inorganic materials 0.000 claims description 5
- KHPCPRHQVVSZAH-UHFFFAOYSA-N trans-cinnamyl beta-D-glucopyranoside Natural products OC1C(O)C(O)C(CO)OC1OCC=CC1=CC=CC=C1 KHPCPRHQVVSZAH-UHFFFAOYSA-N 0.000 claims description 5
- 210000002268 wool Anatomy 0.000 claims description 5
- ZXMGHDIOOHOAAE-UHFFFAOYSA-N 1,1,1-trifluoro-n-(trifluoromethylsulfonyl)methanesulfonamide Chemical class FC(F)(F)S(=O)(=O)NS(=O)(=O)C(F)(F)F ZXMGHDIOOHOAAE-UHFFFAOYSA-N 0.000 claims description 4
- 238000009825 accumulation Methods 0.000 claims description 4
- 239000008108 microcrystalline cellulose Substances 0.000 claims description 4
- 229940016286 microcrystalline cellulose Drugs 0.000 claims description 4
- 230000004048 modification Effects 0.000 claims description 4
- 238000012986 modification Methods 0.000 claims description 4
- 239000002006 petroleum coke Substances 0.000 claims description 4
- 239000000839 emulsion Substances 0.000 claims description 3
- 239000003921 oil Substances 0.000 claims description 3
- 235000019198 oils Nutrition 0.000 claims description 3
- 229920002037 poly(vinyl butyral) polymer Polymers 0.000 claims description 3
- 229920001296 polysiloxane Polymers 0.000 claims description 3
- 238000002360 preparation method Methods 0.000 claims description 3
- 235000019482 Palm oil Nutrition 0.000 claims description 2
- 239000002540 palm oil Substances 0.000 claims description 2
- 238000003672 processing method Methods 0.000 claims description 2
- 239000002994 raw material Substances 0.000 claims description 2
- 238000001816 cooling Methods 0.000 claims 2
- 239000003795 chemical substances by application Substances 0.000 claims 1
- 239000000571 coke Substances 0.000 claims 1
- 239000003208 petroleum Substances 0.000 claims 1
- 229920005989 resin Polymers 0.000 claims 1
- 239000011347 resin Substances 0.000 claims 1
- 239000004575 stone Substances 0.000 claims 1
- 238000004073 vulcanization Methods 0.000 claims 1
- 239000002245 particle Substances 0.000 abstract description 7
- 238000012545 processing Methods 0.000 abstract description 7
- 239000010797 grey water Substances 0.000 abstract description 5
- 238000004062 sedimentation Methods 0.000 abstract description 5
- 238000000926 separation method Methods 0.000 abstract description 4
- 229920000426 Microplastic Polymers 0.000 abstract description 3
- 238000000151 deposition Methods 0.000 abstract description 2
- 238000010790 dilution Methods 0.000 description 7
- 239000012895 dilution Substances 0.000 description 7
- 238000003756 stirring Methods 0.000 description 4
- 230000002776 aggregation Effects 0.000 description 2
- 238000004220 aggregation Methods 0.000 description 2
- BGOFCVIGEYGEOF-UJPOAAIJSA-N helicin Chemical compound O[C@@H]1[C@@H](O)[C@H](O)[C@@H](CO)O[C@H]1OC1=CC=CC=C1C=O BGOFCVIGEYGEOF-UJPOAAIJSA-N 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- -1 DEG C Acid imide Chemical class 0.000 description 1
- AXNBHOOQHIIQFA-UHFFFAOYSA-N [S].C(F)(F)F Chemical compound [S].C(F)(F)F AXNBHOOQHIIQFA-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000007667 floating Methods 0.000 description 1
- 230000003311 flocculating effect Effects 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 238000005984 hydrogenation reaction Methods 0.000 description 1
- 230000002209 hydrophobic effect Effects 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 238000011017 operating method Methods 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5263—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using natural chemical compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5272—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using specific organic precipitants
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/54—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/54—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
- C02F1/56—Macromolecular compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/121—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
- C02F11/122—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering using filter presses
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/34—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
- C02F2103/36—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds
- C02F2103/38—Polymers
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Mechanical Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
The invention discloses a kind of regenerated plastics high concentration alkali water zero discharge treatment process, it is related to regenerated plastics processing technique field, by obtaining clear water using filter press filters pressing after the sedimentation separation of settling tank, and the sludge in sedimentation bottom of pond portion is overstock with clear water backwash, so that sludge pumps out.Sewage water treatment method of the present invention is suitable for the processing of recycled plastic granules cleaning sullage, easy to operate, by the way that obtained clear water is re-used for down batch particle cleaning after separation suspension plastic grain and sludge, to save cleaning water consumption;And by the use of agglomerator, the rate of recovery of suspension plastic grain is improved, while secondary pollution will not be caused to sewage;It is backwashed additionally by clear water, prevents from being difficult to pump out due to sludge is serious because depositing.
Description
Technical field:
The present invention relates to regenerated plastics processing technique fields, and in particular to regenerated plastics high concentration alkali water zero discharge handles work
Skill.
Background technique:
Recycled plastic granules are belonged in this scope of plastic grain, and regenerated plastics are then exactly that recycling is used new
The plastics that material or discarded plastics are produced by Luo bar machine, then a kind of granular plastics are cut by pelleter
Grain.Due to containing dust and greasy dirt etc. in salvage material, it is therefore desirable to be cleaned to plastic grain.Common buck carries out clear
It washes, but the sewage after cleaning, due to containing alkaline matter, environmental pollution is serious, therefore is unable to direct emission.And due to modeling
Expect that particle cleaning hourly water consumption is larger, if will directly clean the sewage discharge of a plastic grain, it will increase cleaning
With water cost.Current simplest sewage water treatment method be exactly the sludge for utilizing natural sedimentation, but being deposited in bottom be easy because
It seriously overstocks and is difficult to pump out, Treatment of Sludge is given to increase difficulty.
Summary of the invention:
It is a kind of by being incited somebody to action after separation suspension plastic grain and sludge technical problem to be solved by the present invention lies in providing
To clear water be re-used for down batch particle cleaning, save cleaning water consumption to play simultaneously and sewage neutral and alkali substance avoided to pollute
The regenerated plastics high concentration alkali water zero discharge treatment process of environment.
The following technical solution is employed for the technical problems to be solved by the invention to realize:
A kind of regenerated plastics high concentration alkali water zero discharge treatment process, including following operating procedure:
(1) alkaline sewage after cleaning plastic grain is pumped into settling tank, and agglomerator is added, and is stood after being sufficiently stirred
Layering, to form the three-decker of upper layer suspension plastic grain, middle layer clear water and lower layer's sludge, suspension plastic grain in upper layer is logical
Filter screen is removed, and the related middle layer clear water of lower layer's sludge is discharged into sludge transporting pipeline by settling the mud mouth of bottom of pond portion;
(2) sludge water in sludge transporting pipeline is sent into filter press through sludge delivery pump, and the clear water after filters pressing flows into
Clear water reserviors, sludge accumulation in filter press is to drawing off after a certain amount of;
(3) on the one hand in clear water reserviors clear water passes through clear water delivery pump and is pumped into clear water recovery channel to carry out down criticizing plastics
On the other hand the cleaning of grain is pumped into sludge by clear water delivery pump and dilutes water pipeline, by the clear water import for settling bottom of pond portion
It is pumped into settling tank to dilute the sludge for being difficult to pump out;
The agglomerator is made of the raw material of following parts by weight: 10 parts of microcrystalline cellulose, 3 parts of haloflex, hydrogenation
2 parts of rosin glycerides, 1 part of Brazil wax, 0.5 part of gelatin, 0.5 part of C5 Petropols, 0.5 part of lanonol, asbestos wool 0.5
Part, 0.3 part of petroleum coke micro mist, 0.3 part of double trifluoromethanesulfonimides, preparation method are as follows: add into hydrogenated rosin glyceride
Enter Brazil wax and gelatin, after being sufficiently mixed under microwave frequency 2450MHz, power 700W microwave treatment 5min, add
C5 Petropols and petroleum coke micro mist, continue microwave treatment 5min after mixing, and gained mixture is transferred to 0-5 DEG C of environment immediately
Then haloflex and lanonol is added in middle sealing and standing 3h, and be heated to 120-130 DEG C of heat preservation mixing 10min, then certainly
It so cools, microcrystalline cellulose, asbestos wool and double trifluoromethanesulfonimides, heat preservation is added after temperature is down to 70-80 DEG C
10min is mixed, gained mixture is placed in sealing and standing 3h in -5-0 DEG C of environment, powder finally is made using micronizer.
The dosage of the agglomerator is that every liter of cleaning sullage uses 0.05-0.1g.
By the way that agglomerator not soluble in water is added, is flocculating and is making the plastic grain to suspend aggregation agglomerating under suction-operated,
In order to remove the lesser plastic grain of granularity by strainer;And agglomerator is removed together with plastic grain, to keep away
Exempt from secondary pollution.
The gelatin passes through modification, processing method using preceding are as follows: 0.5 part of hydrogenated palm is added into 15 parts of gelatin
Oil and 0.5 part of sulfurized lard, after being sufficiently mixed under microwave frequency 2450MHz, power 700W microwave treatment 5min, stand
Then 0.5 part of silicone emulsion and 0.3 part of polyvinyl butyral is added, after mixing in microwave treatment 3min again after 30min
Microwave treatment 5min again, gained mixture are placed in sealing and standing 3h in -5-0 DEG C of environment, are finally made using micronizer
Powder.
It is hydrophobic while improving its absorption to suspension plastic grain to enhance its after above-mentioned modification for gelatin
Property.
It is a further object to provide a kind of regenerated plastics high concentration alkali water zero discharge processing units, by settling
Pond, sludge transporting pipeline, sludge delivery pump, filter press, clear water recovery channel, sludge dilution water pipeline and clear water convey pump group
At the sedimentation bottom of pond portion is equipped with mud mouth and clear water import, and the upper layer suspension plastic grain in settling tank is carried out by strainer
It removes, the related middle layer clear water of lower layer's sludge is discharged into sludge transporting pipeline by mud mouth, and is sent into filters pressing through sludge delivery pump
In machine, the filters pressing motor spindle is equipped with clear water reserviors, and the clear water after filters pressing flows into clear water reserviors, the sludge accumulation in filter press to one
It is drawn off after quantitative, on the one hand the clear water in clear water reserviors is pumped into clear water recovery channel to carry out down batch plastics by the clear water delivery pump
On the other hand clear water is pumped into sludge dilution water pipeline, is pumped into settling tank by clear water import to dilute by the cleaning of particle
It is difficult to the sludge pumped out.
Bottom side is transversely provided with spiral helicine stirring blade inside the settling tank.Stirring blade fits through sludge dilution and send
The clear water rapid dilution sludge that waterpipe is sent into, to save the water consumption of dilution sludge.
The settling tank internal vertical is equipped with multiple mud rooms, the corresponding mud mouth of each mud room.Pass through multiple dirts
The velocity of discharge of sludge water is accelerated in the setting of mud room and mud mouth, and sludge is prevented to be difficult to pump out because long-time is overstock.
The mud room is the structure that longitudinal section is in inverted trapezoidal.By the design of inverted trapezoidal, convenient for making by gravity
Sludge is quickly discharged.
The arc-shaped structure of strainer, is fixed by the connecting rod in the shaft for being mounted on and rotation being driven by motor.Utilize electricity
Machine band electric filter is rotated to remove upper layer suspension plastic grain automatically, reduces human input.
Valve is equipped on the sludge transporting pipeline, clear water recovery channel and sludge dilution water pipeline.
The beneficial effects of the present invention are: sewage water treatment method of the present invention is suitable for recycled plastic granules cleaning sullage
Processing, it is easy to operate, by the way that obtained clear water is re-used for down batch particle cleaning after separation suspension plastic grain and sludge, with
Save cleaning water consumption;And by the use of agglomerator, the rate of recovery of suspension plastic grain is improved, while sewage will not be made
At secondary pollution;It is backwashed additionally by clear water, prevents from being difficult to pump out due to sludge is serious because depositing.
Detailed description of the invention:
Fig. 1 is apparatus of the present invention structure top view;
Fig. 2 is apparatus of the present invention structure rearview;
Wherein: 1- settling tank;2- sludge transporting pipeline;3- sludge delivery pump;4- filter press;5- clear water recovery channel;6-
Sludge dilutes water pipeline;7- clear water delivery pump;8- mud mouth;9- clear water import;10- strainer;11- clear water reserviors;12- stirring slurry
Leaf;13- mud room;14- connecting rod;15- motor;16- shaft;17- valve.
Specific embodiment:
In order to be easy to understand the technical means, the creative features, the aims and the efficiencies achieved by the present invention, tie below
Conjunction is specifically illustrating and embodiment, and the present invention is further explained.
(1) alkaline sewage after cleaning plastic grain is pumped into settling tank 1, and agglomerator is added, and is sufficiently stirred rear quiet
Layering is set, so that the three-decker of upper layer suspension plastic grain, middle layer clear water and lower layer's sludge is formed, upper layer suspension plastic grain
It is removed by strainer 10, the related middle layer clear water of lower layer's sludge is discharged into sludge transporting pipeline 2 by the mud mouth 8 of sedimentation bottom of pond portion;
(2) sludge water in sludge transporting pipeline is sent into filter press 4 through sludge delivery pump 3, the clear water stream after filters pressing
Enter clear water reserviors 11, the accumulation of sludge in filter press is to drawing off after a certain amount of;
(3) on the one hand in clear water reserviors clear water passes through clear water delivery pump 7 and is pumped into clear water recovery channel 5 to carry out down criticizing plastics
The cleaning of particle, on the other hand by clear water delivery pump be pumped into sludge dilute water pipeline 6, by settle bottom of pond portion clear water into
Mouth 9 is pumped into settling tank to dilute the sludge for being difficult to pump out.
Bottom side is transversely provided with spiral helicine stirring blade 12 inside settling tank, and settling tank internal vertical is equipped with multiple mud rooms
13, the corresponding mud mouth of each mud room, mud room is the structure that longitudinal section is in inverted trapezoidal.The arc-shaped structure of strainer,
By connecting rod 14 be fixedly mounted on by motor 15 driving rotation shaft 16 on, sludge transporting pipeline, clear water recovery channel and
It is equipped with valve 17 on sludge dilution water pipeline, as depicted in figs. 1 and 2.
Agglomerator is added into settling tank using the amount of 0.05g agglomerator according to every liter of cleaning sullage, upper layer is promoted to suspend
Particle aggregation is agglomerating, in order to strainer removing.
Agglomerator the preparation method comprises the following steps: 1 part of Brazil wax and 0.5 part of gelatin are added into 2 parts of hydrogenated rosin glycerides,
After being sufficiently mixed under microwave frequency 2450MHz, power 700W microwave treatment 5min, add 0.5 part of C5 Petropols and 0.3
Part petroleum coke micro mist, continues microwave treatment 5min after mixing, and gained mixture is transferred to sealing and standing in 0-5 DEG C of environment immediately
Then 3 parts of haloflexes and 0.5 part of lanonol is added in 3h, and be heated to 120-130 DEG C of heat preservation mixing 10min, then nature
It cools, 10 parts of microcrystalline celluloses, 0.5 part of asbestos wool and 0.3 part of double fluoroform sulphur is added after temperature is down to 70-80 DEG C
Acid imide, heat preservation mixing 10min, gained mixture are placed in sealing and standing 3h in -5-0 DEG C of environment, finally utilize micronizer
Powder is made.
The modification of gelatin: 0.5 part of hydrogenated palm oil and 0.5 part of sulfurized lard being added into 15 parts of gelatin, sufficiently mixed
After conjunction under microwave frequency 2450MHz, power 700W microwave treatment 5min, stand microwave treatment 3min again after 30min, then
0.5 part of silicone emulsion and 0.3 part of polyvinyl butyral is added, after mixing microwave treatment 5min again, gained mixture
It is placed in sealing and standing 3h in -5-0 DEG C of environment, powder finally is made using micronizer.
Processing result shows, after handling cleaning sullage using above-mentioned processing system, suspension plastic grain in sewage and outstanding
The clearance rate of floating mud granule reaches 99% or more, and the clear water of acquisition can be re-used for down the cleaning of batch plastic grain.
The above shows and describes the basic principles and main features of the present invention and the advantages of the present invention.The technology of the industry
Personnel are it should be appreciated that the present invention is not limited to the above embodiments, and the above embodiments and description only describe this
The principle of invention, without departing from the spirit and scope of the present invention, various changes and improvements may be made to the invention, these changes
Change and improvement all fall within the protetion scope of the claimed invention.The claimed scope of the invention by appended claims and its
Equivalent thereof.
Claims (3)
1. regenerated plastics high concentration alkali water zero discharge treatment process, which comprises the steps of:
(1) alkaline sewage after cleaning plastic grain is pumped into settling tank, and agglomerator is added, and is stood and is divided after being sufficiently stirred
Layer, to form the three-decker of upper layer suspension plastic grain, middle layer clear water and lower layer's sludge, upper layer suspension plastic grain passes through
Strainer is removed, and the related middle layer clear water of lower layer's sludge is discharged into sludge transporting pipeline by settling the mud mouth of bottom of pond portion;
(2) sludge water in sludge transporting pipeline is sent into filter press through sludge delivery pump, and the clear water after filters pressing flows into clear water
Pond, sludge accumulation in filter press is to drawing off after a certain amount of;
(3) on the one hand in clear water reserviors clear water passes through clear water delivery pump and is pumped into clear water recovery channel to carry out down criticizing plastic grain
On the other hand cleaning is pumped into sludge by clear water delivery pump and dilutes water pipeline, the clear water import by settling bottom of pond portion is pumped into
To dilute the sludge for being difficult to pump out in settling tank;
The agglomerator is made of the raw material of following parts by weight: 10 parts of microcrystalline cellulose, 3 parts of haloflex, hydrogenated rosin
2 parts of glyceride, 1 part of Brazil wax, 0.5 part of gelatin, 0.5 part of C5 Petropols, 0.5 part of lanonol, 0.5 part of asbestos wool, stone
0.3 part of oil coke micro mist, 0.3 part of double trifluoromethanesulfonimides, preparation method are as follows: Brazil is added into hydrogenated rosin glyceride
Palm wax and gelatin, after being sufficiently mixed under microwave frequency 2450MHz, power 700W microwave treatment 5min, add C5 petroleum
Resin and petroleum coke micro mist, continue microwave treatment 5min after mixing, and gained mixture is transferred in 0-5 DEG C of environment immediately and seals
3h is stood, haloflex and lanonol is then added, and is heated to 120-130 DEG C of heat preservation mixing 10min, subsequent natural cooling
Microcrystalline cellulose, asbestos wool and double trifluoromethanesulfonimides, heat preservation mixing is added in cooling after temperature is down to 70-80 DEG C
10min, gained mixture are placed in sealing and standing 3h in -5-0 DEG C of environment, powder finally are made using micronizer.
2. regenerated plastics high concentration alkali water zero discharge treatment process according to claim 1, it is characterised in that: the reunion
The dosage of agent is that the alkaline sewage after every liter of plastic grain cleaning uses 0.05-0.1g.
3. regenerated plastics high concentration alkali water zero discharge treatment process according to claim 1, it is characterised in that: the gelatin
Pass through modification, processing method using preceding are as follows: 0.5 part of hydrogenated palm oil and 0.5 part of vulcanization pig are added into 15 parts of gelatin
Oil, after being sufficiently mixed under microwave frequency 2450MHz, power 700W microwave treatment 5min, stand microwave treatment again after 30min
Then 0.5 part of silicone emulsion and 0.3 part of polyvinyl butyral is added in 3min, after mixing microwave treatment 5min again, institute
It obtains mixture and is placed in sealing and standing 3h in -5-0 DEG C of environment, powder finally is made using micronizer.
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| CN201610934992.4A CN106564998B (en) | 2016-11-01 | 2016-11-01 | Regenerated plastics high concentration alkali water zero discharge treatment process |
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Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101948671A (en) * | 2010-09-17 | 2011-01-19 | 中科院广州化学有限公司 | Adhesive for precision machining and environment-friendly cleaning method thereof |
| CN201769295U (en) * | 2010-07-07 | 2011-03-23 | 甘肃大禹节水股份有限公司 | Waste plastic water floating device |
| CN105290312A (en) * | 2015-10-21 | 2016-02-03 | 和县科嘉阀门铸造有限公司 | Foamed plastic binder for lost foam casting of valve |
| CN105368383A (en) * | 2015-10-21 | 2016-03-02 | 安徽埃斯克制泵有限公司 | Foamed plastic binder for centrifugal pump lost foam casting |
-
2016
- 2016-11-01 CN CN201610934992.4A patent/CN106564998B/en active Active
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN201769295U (en) * | 2010-07-07 | 2011-03-23 | 甘肃大禹节水股份有限公司 | Waste plastic water floating device |
| CN101948671A (en) * | 2010-09-17 | 2011-01-19 | 中科院广州化学有限公司 | Adhesive for precision machining and environment-friendly cleaning method thereof |
| CN105290312A (en) * | 2015-10-21 | 2016-02-03 | 和县科嘉阀门铸造有限公司 | Foamed plastic binder for lost foam casting of valve |
| CN105368383A (en) * | 2015-10-21 | 2016-03-02 | 安徽埃斯克制泵有限公司 | Foamed plastic binder for centrifugal pump lost foam casting |
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| CN106564998A (en) | 2017-04-19 |
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Denomination of invention: Zero-discharge treatment process of recycled plastic high-concentration alkaline water Effective date of registration: 20191225 Granted publication date: 20190514 Pledgee: The development of small and medium-sized enterprises financing Company Limited by Guarantee Jieshou City Pledgor: Anhui Huanjia Tianyi Regeneration Resource Co.,Ltd. Registration number: Y2019980001282 |