CN109534558A - Sodium dichromate method produces expansible graphite acid waste water processing equipment and technique - Google Patents

Sodium dichromate method produces expansible graphite acid waste water processing equipment and technique Download PDF

Info

Publication number
CN109534558A
CN109534558A CN201811607668.7A CN201811607668A CN109534558A CN 109534558 A CN109534558 A CN 109534558A CN 201811607668 A CN201811607668 A CN 201811607668A CN 109534558 A CN109534558 A CN 109534558A
Authority
CN
China
Prior art keywords
waste water
unit
reaction unit
expansible graphite
filter element
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201811607668.7A
Other languages
Chinese (zh)
Inventor
于大成
于明军
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shanghai Environmental Protection Group Polytron Technologies Inc
Original Assignee
Shanghai Environmental Protection Group Polytron Technologies Inc
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Shanghai Environmental Protection Group Polytron Technologies Inc filed Critical Shanghai Environmental Protection Group Polytron Technologies Inc
Priority to CN201811607668.7A priority Critical patent/CN109534558A/en
Publication of CN109534558A publication Critical patent/CN109534558A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/56Macromolecular compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/70Treatment of water, waste water, or sewage by reduction
    • C02F1/705Reduction by metals
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/121Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
    • C02F11/122Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering using filter presses
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • C02F2101/22Chromium or chromium compounds, e.g. chromates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/04Oxidation reduction potential [ORP]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH

Abstract

The invention discloses a kind of sodium dichromate methods to produce expansible graphite acid waste water processing equipment, comprising: for recycling the recycling graphite unit of expansible graphite particle;Adjusting unit for balanced water quality and quantity;For being the reduction reaction unit of trivalent chromium by the hexavalent chrome reduction in waste water;Neutralization reaction unit;The press filtration unit of dehydration and drying is carried out for the sludge to generation;Filtrate storage unit;For removing the filter element of the heavy metal particles object formed in waste water, suspended matter;Wherein, above-mentioned each unit is sequentially connected to.The invention also discloses a kind of sodium dichromate methods to produce expansible graphite process for treating acidic sewage.Wastewater treatment stably reaching standard of the present invention, processing load is high, processing cost is low.

Description

Sodium dichromate method produces expansible graphite acid waste water processing equipment and technique
Technical field
The present invention relates to field of waste water treatment, produce expansible graphite acid waste water more particularly, to a kind of sodium dichromate method Treatment process and equipment.
Background technique
The sodium dichromate method production existing wastewater processing technology of expansible graphite acid waste water mainly has chemical precipitation method, electricity wadding Solidifying oxidation-precipitation method.Chemical precipitation method processing expansible graphite acid waste water is carried out at neutralization with adding alkali to the diluted acid in waste water Reason is adjusted wastewater pH to a certain range using alkali, is reacted using alkali with heavy metal ion, utilize sedimentation basin separating beavy metal Hydroxide precipitating, but the chromium in waste water exists in the form of Cr VI and two kinds of trivalent chromium, trivalent chromium corresponding hydrogen easy to form Oxide precipitation and toxicity is smaller, Cr VI relative difficult forms corresponding hydroxide precipitating and toxicity is very big thus simple It goes to neutralize waste water with alkali, precipitate the heavy metal ion in waste water, there are the low deficiencies for the treatment of effeciency, it is difficult to meet emission request; Though electric flocculation oxidation-precipitation method processing expansible graphite acid waste water need to only add part lye and adjust waste water to certain pH, do not have to It adds the medicaments such as reducing agent, flocculant to handle waste water, but that there are pole plates is perishable, electricity consumption is big, and processing load is low, place It manages the defects of at high cost, limits its use to a certain degree.As described above, acid for sodium dichromate method production expansible graphite The processing of waste water, there is presently no being capable of stably reaching standard, the mature treatment process that processing load is high, processing cost is low.
Summary of the invention
The purpose of the present invention is to solve the above-mentioned problems, and it is acid to provide a kind of sodium dichromate method production expansible graphite Sewage treatment equipment, wastewater treatment stably reaching standard, processing load is high, processing cost is low.
To achieve the goals above, the present invention adopts the following technical scheme: a kind of sodium dichromate method produces expansible graphite Acid waste water processing equipment characterized by comprising for recycling the recycling graphite unit of expansible graphite particle;
Adjusting unit for balanced water quality and quantity;
For being the reduction reaction unit of trivalent chromium by the hexavalent chrome reduction in waste water;
Neutralization reaction unit;
The press filtration unit of dehydration and drying is carried out for the sludge to generation;
Filtrate storage unit;
For removing the filter element of the heavy metal particles object formed in waste water, suspended matter;
Wherein, above-mentioned each unit is sequentially connected to.
Optionally, the filter element is connected to clear water storage unit.
Optionally, the first pump of setting, the neutralization reaction unit and pressure between the adjusting unit and reduction reaction unit The second pump of setting between unit is filtered, third is set between the filtrate storage unit and filter element and is pumped.
Optionally, front end dosing mouth and rear end dosing mouth is respectively set on the water inlet pipe and outlet pipe of the third pump, it is preceding End dosing mouth is for adding flocculant PAC, and rear end dosing mouth is for adding flocculation aid PAM.
Optionally, ORP is set at the reduction reaction unit, instrument and reduction reaction unit automatic medicament feeding machine is monitored online.
Optionally, pH is set at the neutralization reaction unit, instrument and neutralization reaction unit automatic medicament feeding machine is monitored online.
On the other hand, a kind of sodium dichromate method produces expansible graphite process for treating acidic sewage, it is characterised in that: waste water Remaining fine particle expansible graphite in recycling graphite unit recycling waste water is initially entered, is then promoted to reduction with the first pump Reaction member;Ferrous sulfate is added and adjusts waste water ORP current potential, controls ORP current potential between 482-485mV, when ORP is monitored online When instrument monitors waste water current potential lower than 482mV, control unit issues the instruction for adding ferrous sulfate solution, when ORP is monitored online When instrument monitors that waste water current potential is higher than 485mV, control system issues the instruction for stopping adding ferrous sulfate solution, at this time in waste water Cr VI be all reduced to trivalent chromium;Waste water enters neutralization reaction unit, and pH on-line monitoring instrument is set in neutralization reaction unit, when When pH on-line monitoring instrument monitors wastewater pH lower than 7.5, control system issues the instruction of feeding lime cream, when instrument is monitored online in pH Monitor wastewater pH be higher than 8 when, control system issue stop feeding lime cream instruction, adjusting pH keep it in 7.5-8 it Between, the heavy metal ion such as trivalent chromium in waste water form fine suspension;Waste water with the second pump pumping to press filtration unit, in filtrate Containing impurity such as suspended matter, heavy metal hydroxides, filtrate is with third pumping into filter element;It is saturating that filter element goes out water colorless Bright, suspension content meets national emission standard lower than 10mg/l, content of beary metal, into clear water reserviors.
Optionally, flocculation aid PAM is added at the water inlet pipe of the filter element, the precipitating particle aggregation for that will generate increases Greatly.
Optionally, the sludge timing automatic-discharging in the filter element, the sludge of discharge enter neutralization reaction unit, warp Second is pumped into filter press dehydration, mud cake entrucking outward transport.
Compared with prior art, the invention has the following beneficial effects: respective reaction ponds in (1) technique to be equipped with on-line monitoring The number of dosage can be automatically adjusted, the dosage of medicament is reduced under the premise of ensureing treatment effect, operating cost is more for instrument Low, treatment effect is more stable.(2) technology controlling and process, automation degree of equipment are high, easy to operate, save artificial.Only when medicament deficiency When by being manually properly added, operation is simple.(3) in technique filter especially suitable for produce expansible graphite acid waste water Filtering, separating treatment after reaction, the filter media surface in filter have electrostatic, can effectively adsorb, in filtered wastewater Fine particulates carry out effective retention removal to heavy metal hydroxide.(4) technological design is scientific and reasonable, adapts to certain The load fluctuation and variation of degree, stable water outlet is up to standard, high degree of automation, and reaction is abundant and saves medicament, saves artificial, tool There is the advantage that other sodium dichromate method production expansible graphite process for treating acidic sewage are incomparable at present.
Detailed description of the invention
Fig. 1 is that sodium dichromate method produces expansible graphite acid waste water processing equipment structure chart.
Fig. 2 is that sodium dichromate method produces expansible graphite process for treating acidic sewage module map.
In figure, 101 recycling graphite units, 102 adjust unit, and 103 first pump, 104 reduction reaction units, in 105 and anti- Unit is answered, 106 second pump, 107 press filtration units, 108 filtrate storage units, and 109 thirds pump, 110 filter elements, 111 clear water are deposited Storage unit.
Specific embodiment
Embodiment 1: referring to Fig. 1, a kind of sodium dichromate method production expansible graphite acid waste water processing equipment, including be used for Recycle the recycling graphite unit (being recycling graphite pond in embodiment) of expansible graphite particle, for the adjusting of balanced water quality and quantity Unit (being conditioning tank in embodiment), for by reduction reaction unit (embodiment that the hexavalent chrome reduction in waste water is trivalent chromium In be reduction reaction pond), it is neutralization reaction unit (being neutralization reaction pond in embodiment), dry for carrying out dehydration to the sludge of generation The press filtration unit (being filter press in embodiment) of change, filtrate storage unit (being reservoir in embodiment), for removing in waste water The filter element of the heavy metal particles object suspended matter of formation (is filter in embodiment, equipment is the self-produced equipment of our company, specifically Can refer to ZL201220511324.8), above-mentioned each unit sequentially connects (connection).
The filter element is connected to clear water storage unit (being clear water reserviors in embodiment).The adjusting unit and reduction reaction The first pump of setting between unit, is arranged the second pump, the filtrate storage unit between the neutralization reaction unit and press filtration unit Third is arranged between filter element to pump.
Front end dosing mouth and rear end dosing mouth, front end dosing mouth is respectively set on the water inlet pipe and outlet pipe of the third pump For adding flocculant PAC (polymeric aluminum chlorides solution), (polyacrylamide is molten for adding flocculation aid PAM for rear end dosing mouth Liquid).
Be arranged at the reduction reaction unit ORP be monitored online instrument and reduction reaction unit automatic medicament feeding machine (Automatic Dosing, Can refer to the prior art), ORP on-line monitoring instrument and reduction reaction unit automatic medicament feeding machine are connected to control unit.
Be arranged at the neutralization reaction unit pH be monitored online instrument and neutralization reaction unit automatic medicament feeding machine (Automatic Dosing, Can refer to the prior art), pH on-line monitoring instrument and neutralization reaction unit automatic medicament feeding machine are connected to control unit.
The effect in recycling graphite pond is remaining subtle expansible graphite particle in recycling waste water, increases yield, simultaneously Reduce the processing load of back segment treatment process.
The effect of conditioning tank is storage waste water, and balanced water quality and quantity.
The effect of first pump is lifting waste water into reduction reaction pond, controls flow of inlet water.
The effect of reduction reaction pond is that ferrous sulfate is added sufficiently to carry out reduction reaction with waste water, makes the Cr VI in waste water It is reduced to trivalent chromium, Chi Zhongshe blender.
The effect of neutralization reaction pond is to adjust pH value, provides optimum reaction condition for neutralization reaction, improves sludge, Chi Zhongshe Blender.
Second pump effect be promotion neutralization reaction pond in sludge into filter press dehydration.
The effect of filter press is to carry out dehydration and drying to the sludge of generation, is readily transported.
The effect of reservoir is transfer, storage filtrate.
The effect of third pump is the filtrate in reservoir to be promoted to filter, while providing flocculant, flocculation aid and giving up The condition of water mixing, controls flow of inlet water.
The effect of filter is filtering, the separation for waste water, removes the heavy metal particles object formed in waste water, suspends Object.
Clear water of the clear water reserviors effect for storage after processed, is convenient for workshop reuse or qualified discharge.
Embodiment 2: the technique in the present embodiment is related to the equipment in embodiment 1, and referring to fig. 2, a kind of sodium dichromate method is raw Expansible graphite process for treating acidic sewage is produced, the acid waste water that workshop generates initially enters recycling graphite pond (recycling graphite list Member) remaining fine particle expansible graphite in waste water is recycled, then reduction reaction pond (reduction reaction list is promoted to the first pump Member);Ferrous sulfate is added and adjusts waste water ORP current potential, controls ORP current potential between 482-485mV, when ORP on-line monitoring instrument prison When measuring waste water current potential lower than 482mV, control system sending adds the instruction of ferrous sulfate solution (certainly by reduction reaction unit Dynamic chemicals feeder is realized), when ORP on-line monitoring instrument monitors that waste water current potential is higher than 485mV, control system, which issues, to be stopped adding sulphur The instruction of sour ferrous iron solution, the Cr VI in waste water is all reduced to trivalent chromium at this time;Waste water enters neutralization reaction pond and (neutralizes anti- Answer unit), instrument is monitored online in Chi Zhongshe pH, and when pH on-line monitoring instrument monitors wastewater pH lower than 7.5, control system, which issues, is thrown The instruction (being realized by neutralization reaction unit chemicals feeder) for adding milk of lime, when pH on-line monitoring instrument monitors that wastewater pH is higher than 8, Control system issues the instruction for stopping feeding lime cream, adjusts pH and keeps it between 7.5-8, the weight such as trivalent chromium in waste water Metal ion forms fine suspension, while flocculation aid PAM and flocculant PAC is added at water inlet pipe (water inlet pipe of filter), Increase the precipitating particle aggregation generated;Waste water with the second pumping to filter press (press filtration unit), in filtrate containing suspended matter, again The impurity such as metal hydroxides, with third pumping, into filter, (filter element, filter used in the present embodiment are our company Equipment of the Company can specifically refer to ZL201220511324.8);Filter water outlet is colorless and transparent, suspension content is lower than 10mg/ L, content of beary metal meet national emission standard, into clear water reserviors (clear water storage unit), can qualified discharge, also can be used as ground Flushing water is back to workshop;Sludge timing automatic-discharging in filter, the sludge of discharge enter neutralization reaction pond, through the second pump Be pumped into filter press dehydration, mud cake can entrucking outward transport, due to that, containing the calcium sulfate of high level, can also be sold in mud cake To neighbouring cement plant.
Yichang Xincheng Graphite Co., Ltd. and the great graphite Co., Ltd of the Longjiang Hei Sheng Bo have this technique at Function case.
The foregoing is merely the preferred embodiment of the present invention, protection scope of the present invention is not limited in above-mentioned embodiment party Formula, all technical solutions for belonging to the principle of the invention all belong to the scope of protection of the present invention.For those skilled in the art and Speech, several improvement carried out without departing from the principles of the present invention, these improvement also should be regarded as protection model of the invention It encloses.

Claims (9)

1. a kind of sodium dichromate method produces expansible graphite acid waste water processing equipment characterized by comprising
For recycling the recycling graphite unit of expansible graphite particle;
Adjusting unit for balanced water quality and quantity;
For being the reduction reaction unit of trivalent chromium by the hexavalent chrome reduction in waste water;
Neutralization reaction unit;
The press filtration unit of dehydration and drying is carried out for the sludge to generation;
Filtrate storage unit;
For removing the filter element of the heavy metal particles object formed in waste water, suspended matter;
Wherein, above-mentioned each unit is sequentially connected to.
2. equipment according to claim 1, which is characterized in that the filter element is connected to clear water storage unit.
3. equipment according to claim 1, which is characterized in that is arranged between the adjusting unit and reduction reaction unit The second pump is arranged, between the filtrate storage unit and filter element in one pump between the neutralization reaction unit and press filtration unit Third is arranged to pump.
4. equipment according to claim 3, which is characterized in that be respectively set on the water inlet pipe and outlet pipe of the third pump Front end dosing mouth and rear end dosing mouth, front end dosing mouth is for adding flocculant PAC, and rear end dosing mouth is for adding flocculation aid PAM。
5. equipment according to claim 1, which is characterized in that ORP is arranged at the reduction reaction unit, instrument is monitored online And reduction reaction unit automatic medicament feeding machine.
6. equipment according to claim 1, which is characterized in that at the neutralization reaction unit be arranged pH be monitored online instrument and Neutralization reaction unit automatic medicament feeding machine.
7. a kind of sodium dichromate method produces expansible graphite process for treating acidic sewage, it is characterised in that: waste water initially enters stone Remaining fine particle expansible graphite in black recovery unit recycling waste water, is then promoted to reduction reaction unit with the first pump; Ferrous sulfate is added and adjusts waste water ORP current potential, controls ORP current potential between 482-485mV, when ORP on-line monitoring instrument monitors When waste water current potential is lower than 482mV, control unit issues the instruction for adding ferrous sulfate solution, when ORP on-line monitoring instrument monitors When waste water current potential is higher than 485mV, control system issues the instruction for stopping adding ferrous sulfate solution, at this time the Cr VI in waste water All it is reduced to trivalent chromium;Waste water enters neutralization reaction unit, pH on-line monitoring instrument is set in neutralization reaction unit, when pH is supervised online When control instrument monitors wastewater pH lower than 7.5, control system issues the instruction of feeding lime cream, when pH on-line monitoring instrument monitors to give up When water pH is higher than 8, control system issues the instruction for stopping feeding lime cream, adjusts pH and keeps it between 7.5-8, in waste water The heavy metal ion such as trivalent chromium form fine suspension;Waste water the second pumping to press filtration unit, in filtrate containing suspended matter, The impurity such as heavy metal hydroxide, filtrate is with third pumping into filter element;Filter element water outlet is colorless and transparent, suspended matter contains Amount is lower than 10mg/l, into clear water reserviors.
8. technique according to claim 7, which is characterized in that flocculation aid PAM is added at the water inlet pipe of the filter element, Precipitating particle aggregation for that will generate increases.
9. technique according to claim 7, which is characterized in that the sludge timing automatic-discharging in the filter element, row Sludge out enters neutralization reaction unit, is pumped into filter press dehydration, mud cake entrucking outward transport through second.
CN201811607668.7A 2018-12-27 2018-12-27 Sodium dichromate method produces expansible graphite acid waste water processing equipment and technique Pending CN109534558A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811607668.7A CN109534558A (en) 2018-12-27 2018-12-27 Sodium dichromate method produces expansible graphite acid waste water processing equipment and technique

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811607668.7A CN109534558A (en) 2018-12-27 2018-12-27 Sodium dichromate method produces expansible graphite acid waste water processing equipment and technique

Publications (1)

Publication Number Publication Date
CN109534558A true CN109534558A (en) 2019-03-29

Family

ID=65856714

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811607668.7A Pending CN109534558A (en) 2018-12-27 2018-12-27 Sodium dichromate method produces expansible graphite acid waste water processing equipment and technique

Country Status (1)

Country Link
CN (1) CN109534558A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110040870A (en) * 2019-04-03 2019-07-23 东莞市三人行环境科技有限公司 A kind of method of painting wastewater processing
CN112551755A (en) * 2020-12-17 2021-03-26 黑龙江哈工石墨科技有限公司 Expandable graphite production wastewater treatment system and treatment method

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102344208A (en) * 2010-07-28 2012-02-08 中国环境科学研究院 Process for treating chromium-containing waste water produced in chromium slag pollution place
CN104401978A (en) * 2014-10-30 2015-03-11 宜昌新成石墨有限责任公司 Preparation method for sulfur-free expandable graphite
WO2015076773A1 (en) * 2013-11-21 2015-05-28 Олег Игоревич NOSOVSKYI OLEG I. ul. Nikolsko-Botanicheskaya 17/19 kv. 60 Kiev 01033 НОСОВСКИЙ Method for cleaning industrial water and wastewater of chromium compounds
CN105254076A (en) * 2015-11-16 2016-01-20 苏州南风优联环保工程有限公司 Simple and efficient nickel-containing wastewater treating process
CN108928971A (en) * 2018-07-20 2018-12-04 深圳市世清环保科技有限公司 A kind of processing system and its implementation of chromium-containing dyeing waste water

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102344208A (en) * 2010-07-28 2012-02-08 中国环境科学研究院 Process for treating chromium-containing waste water produced in chromium slag pollution place
WO2015076773A1 (en) * 2013-11-21 2015-05-28 Олег Игоревич NOSOVSKYI OLEG I. ul. Nikolsko-Botanicheskaya 17/19 kv. 60 Kiev 01033 НОСОВСКИЙ Method for cleaning industrial water and wastewater of chromium compounds
CN104401978A (en) * 2014-10-30 2015-03-11 宜昌新成石墨有限责任公司 Preparation method for sulfur-free expandable graphite
CN105254076A (en) * 2015-11-16 2016-01-20 苏州南风优联环保工程有限公司 Simple and efficient nickel-containing wastewater treating process
CN108928971A (en) * 2018-07-20 2018-12-04 深圳市世清环保科技有限公司 A kind of processing system and its implementation of chromium-containing dyeing waste water

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
徐志毅: "《环境保护技术与设备》", 31 December 1999, 上海交通大学出版社 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110040870A (en) * 2019-04-03 2019-07-23 东莞市三人行环境科技有限公司 A kind of method of painting wastewater processing
CN110040870B (en) * 2019-04-03 2021-11-16 东莞市三人行环境科技有限公司 Method for treating paint spraying wastewater
CN112551755A (en) * 2020-12-17 2021-03-26 黑龙江哈工石墨科技有限公司 Expandable graphite production wastewater treatment system and treatment method

Similar Documents

Publication Publication Date Title
CN102826686B (en) Double-membrane treatment method of iron and steel industrial wastewater
CN201722249U (en) Industrial sewage electrochemical treatment plant
CN204824453U (en) Desulfurization pretreatment of water device that gives up
CN202953895U (en) Electrocoagulation sewage treatment system
CN103073163B (en) Treatment and sludge reduction device and method of de-sizing wastewater
CN105439326A (en) Treatment method of chemical nickel-plating wastewater
CN202542980U (en) Industrial circulating water bypass filtration treatment device
CN110981000A (en) Method for treating silicon steel magnesium oxide wastewater
CN112142233A (en) Thermal power plant circulating water and sewage water full-membrane-process zero-emission treatment system and method
CN107285489A (en) A kind of device and method of desulfurization wastewater pretreatment
CN109534558A (en) Sodium dichromate method produces expansible graphite acid waste water processing equipment and technique
CN104743750A (en) Method for treating pulp papermaking industrial wastewater
CN102583809A (en) Silica and oil removing system for oily sewage
CN203440183U (en) Deep treatment system of mine gangue dredge discharged water recycling power plant
CN111072112A (en) Wastewater treatment method and system for zero discharge of desulfurization wastewater
CN106830455A (en) The electrochemistry in a kind of gas treatment ashing water or Heisui River removes hard turbidity removal integrated apparatus and its processing method and purposes
CN201971688U (en) System for removing silicon and oil of oily sewage
CN108892276A (en) A kind of waste water treatment system and its method of lead refinery
CN101948220A (en) Method for treating printing and dyeing wastewater
CN107640859A (en) The comprehensive treatment equipment and technique of high concentration COD waste browning liquid
CN211644723U (en) Wastewater treatment system with zero discharge of desulfurization wastewater
WO2018166480A1 (en) Nickel-containing waste water processing system
CN108439670A (en) A kind of waste water zero-emission device and technique
CN102863100B (en) Electrolytic copper foil production wastewater treatment process
CN210150887U (en) Processing system of high salt raffinate waste water of lithium cell recovery trade

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20190329

RJ01 Rejection of invention patent application after publication