[go: up one dir, main page]

CN109052594A - Be suitble to coking wastewater containing phenol and cyanide removes cyanogen drop nitrogen decolorising agent and preparation, application method - Google Patents

Be suitble to coking wastewater containing phenol and cyanide removes cyanogen drop nitrogen decolorising agent and preparation, application method Download PDF

Info

Publication number
CN109052594A
CN109052594A CN201810926647.5A CN201810926647A CN109052594A CN 109052594 A CN109052594 A CN 109052594A CN 201810926647 A CN201810926647 A CN 201810926647A CN 109052594 A CN109052594 A CN 109052594A
Authority
CN
China
Prior art keywords
parts
cyanogen
cyanide
wastewater containing
containing phenol
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.)
Granted
Application number
CN201810926647.5A
Other languages
Chinese (zh)
Other versions
CN109052594B (en
Inventor
张柏鸿
胡文军
孙辉
李红
李俊峰
王坤鹏
张宇
张冲
陈奇
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.)
Anshan Iron And Steel Plant Bake Lucky Buddhist Nun's Water Treatment Co Ltd
Original Assignee
Anshan Iron And Steel Plant Bake Lucky Buddhist Nun's Water Treatment Co Ltd
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 Anshan Iron And Steel Plant Bake Lucky Buddhist Nun's Water Treatment Co Ltd filed Critical Anshan Iron And Steel Plant Bake Lucky Buddhist Nun's Water Treatment Co Ltd
Priority to CN201810926647.5A priority Critical patent/CN109052594B/en
Publication of CN109052594A publication Critical patent/CN109052594A/en
Application granted granted Critical
Publication of CN109052594B publication Critical patent/CN109052594B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/286Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
    • 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
    • C02F1/50Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
    • 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
    • C02F1/5263Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using natural chemical 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
    • C02F1/52Treatment 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
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/18Cyanides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32

Landscapes

  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

The present invention provides a kind of suitable coking wastewater containing phenol and cyanides except cyanogen drop nitrogen decolorising agent and preparation, application method, except cyanogen drop its constituent of nitrogen decolorising agent and mass fraction are as follows: 45-55 parts of polyion network cyanogen agent, 15-25 parts of graft starch, 5-10 parts of polydimethyl diallyl ammonium chloride, 2-8 parts of composite diatomite white vitriol, 1-5 parts of sodium tripolyphosphate, 0.1-1 parts of isopropanol, remaining be water.The present invention is directed to wastewater containing phenol and cyanide bio-chemical effluent, drops one barrel of change scheme of nitrogen decolorising agent using except cyanogen, makes to be discharged be up to state standards emission limit, and the operation that system can be maintained well stable.

Description

Be suitble to coking wastewater containing phenol and cyanide removes cyanogen drop nitrogen decolorising agent and preparation, application method
Technical field
The present invention relates to the cyanogen that removes of water-treatment technology field more particularly to suitable coking wastewater containing phenol and cyanide to drop nitrogen decolorising agent and system Standby, application method.
Background technique
Wastewater containing phenol and cyanide is mainly derived from coking, gas purification and coal chemical industry product processing, especially with the generation of ammonia still process process Remained ammonia be main source.Remained ammonia mainly by the hygroscopic moisture on furnace coal surface, the shove charge dry distillation of coal generate water of constitution, It is added into the oil-containing technique waste water three parts composition inhaled in gas piping and gas collecting tube circulation oxygen water pump.Wastewater containing phenol and cyanide yield Greatly, pollutant load is high and many kinds of, serious to environmental hazard.Wherein cyanide, NH3- N and polycyclic aromatic hydrocarbon, heterocyclic compound Object more bio-refractory, difficulty of governance is very big, and regulation effect is poor.Most of research at present all concentrates on the processing dress of wastewater containing phenol and cyanide Set the research with processing method.[CN 207016558U] discloses a kind of efficient wastewater containing phenol and cyanide processing unit. [CN105174549A] discloses a kind of method of advanced treating wastewater containing phenol and cyanide, elaborate with light chemical oxidization method, multi-effect adsorption, Flocculation etc., finally make wastewater containing phenol and cyanide water outlet COD be down to 60mg/L, coloration be down to 30 times or less, cyanide be down to 0.2mg/L with Under.In [CN 103449684A], Jigang Group Co., Ltd Zhao Pei, which is built, et al. is disclosed at a kind of high toxicity coking wastewater containing phenol and cyanide Manage reclaiming system and wastewater treatment and renovation method, by pretreatment-biological decarbonization denitrogenation-High-rate sedimentation-Fenton advanced oxidation and Five processes of sludge dewatering, final outflow water COD is 65mg/L, cyanide 0.12mg/L, ammonia nitrogen 2.7mg/L.
The treatment research of wastewater containing phenol and cyanide is concentrated mainly at present in the selection of processing method and processing unit, wastewater containing phenol and cyanide Processing method mainly have physical method, chemical method, biochemical method.Physical method processing wastewater containing phenol and cyanide is at high cost, and practical value is smaller;Change Method treatment effect is preferable, but relatively low for ammonia nitrogen removal frank;For biochemical method because big to wastewater treatment capacity, processing cost is low, without two Secondary pollution, and become the main methods of wastewater containing phenol and cyanide.But after the biochemical method processing wastewater containing phenol and cyanide applied at present, in water outlet The pollutants such as total cyanogen, ammonia nitrogen and COD removal it is unsatisfactory, coloration is also relatively high.Especially country has promulgated " coking Chemical industrial pollution discharge standard " after (GB16171-2012), Pollutant emission concentration is controlled stringenter.It is required that ammonia nitrogen 10mg/L, COD 80mg/L, cyanide 0.2mg/L hereinafter, the processing of wastewater containing phenol and cyanide with greater need for optimized treatment method and optimization Medicament.
Summary of the invention
The object of the present invention is to provide a kind of suitable coking wastewater containing phenol and cyanides except cyanogen drop nitrogen decolorising agent and preparation, user Method drops one barrel of change scheme of nitrogen decolorising agent using except cyanogen, so that water outlet is up to state standards and discharge limit for wastewater containing phenol and cyanide bio-chemical effluent Value, and the operation that system can be maintained well stable.
To achieve the above object, the present invention is implemented with the following technical solutions:
It is suitble to the cyanogen that removes of coking wastewater containing phenol and cyanide to drop nitrogen decolorising agent, constituent and mass fraction are as follows: polyion network cyanogen agent 45-55 parts, 15-25 parts of graft starch, 5-10 parts of polydimethyl diallyl ammonium chloride, composite diatomite white vitriol 2-8 Part, 1-5 parts of sodium tripolyphosphate, 0.1-1 parts of isopropanol, remaining be water.
It is suitble to the cyanogen that removes of coking wastewater containing phenol and cyanide to drop nitrogen decolorising agent, constituent and mass fraction are preferred are as follows: polyion network 48-53 parts of cyanogen agent, 18-22 parts of graft starch, 6-8 parts of polydimethyl diallyl ammonium chloride, composite diatomite white vitriol 4-6 parts, 2-4 parts of sodium tripolyphosphate, 0.5-1 parts of isopropanol, remaining be water.
The polyion network cyanogen agent is mixed by following raw materials example in mass ratio: Na2Fe04: polymeric aluminium ferrum silicate: Poly- phosphorus iron chloride: dicyandiamide formaldehyde resin: ferrous citrate=(4~5): (3~4): (2~3): (0.5~1): (1~1.5).
The mass ratio of diatomite and white vitriol in the composite diatomite white vitriol are as follows: diatomite: seven water sulphur Sour zinc=0.4:1~1:1.
It is suitble to the preparation method for removing cyanogen drop nitrogen decolorising agent of coking wastewater containing phenol and cyanide, the specific method is as follows:
1) diatomite and white vitriol are put into four-hole boiling flask according to mass ratio 0.4:1~1:1, according to solid-liquid quality Be added proper amount of clear water than 1:5, then with 1-2ml/ minute speed be added dropwise concentration for 30% sulfuric acid in flask, in 40-45 DEG C, It is reacted 2-2.5 hours under the stirring condition of 80r/min;Reactant is filtered, is dry, is placed in Muffle furnace at 400-450 DEG C Roasting 4-5 hours, calcining matter coolant seal is spare, and gained preparation is composite diatomite white vitriol.
2) polyion network cyanogen agent is put into reaction kettle, distilled water is added according to the mass ratio of solute and water 1:2.2-3.2, After stirring 20-25 minutes with the speed of 150-180r/min, composite diatomite white vitriol is put into, is continued with 100-150r/ The speed of min stirs, and stirring adds 15-25 parts of graft starch, polydimethyl diallyl ammonium chloride 5- after liquid phase is homogeneous 10 parts, 1-5 parts of sodium tripolyphosphate, 0.1-1 parts of isopropanol, are stirred with 120-150r/min, after stirring 15-20 minutes, then with 50- The speed of 80r/min stirs 15-20 minutes, is made after mixing except nitrogen decolorising agent drops in cyanogen.
It is suitble to the application method for removing cyanogen drop nitrogen decolorising agent of coking wastewater containing phenol and cyanide, the dosage that nitrogen decolorising agent is dropped except cyanogen Are as follows:
T=170 × CT-N CCOD≤350mg/L
In formula: except nitrogen decolorising agent dosage, mg/L drop in cyanogen in T- wastewater containing phenol and cyanide;
CT-NTotal cyanide content in wastewater containing phenol and cyanide, mg/L;
CCODCOD content in wastewater containing phenol and cyanide, mg/L.
Polyion network cyanogen agent is one of the host agent except cyanogen drop nitrogen decolorising agent.Na2Fe04 in waste water COD, BOD and TOC etc. has good removal and coagulation, and a series of organic pollutant in the water that can effectively degrade.Na2Fe04 and water In pollutant effect when, the intermediate state of different charges is had via sexavalence to trivalent, generating has excellent flocculating function The iron hydroxide of ferric ion and suction-operated, can show simultaneously in water oxidation, flocculation, absorption, it is coprecipitated, sterilization, The effects of disinfection, and it is without secondary pollution.Polymeric aluminium ferrum silicate, poly- phosphorus iron chloride, dicyandiamide formaldehyde resin, ferrous citrate connection Close use, not only overcome the disadvantage that aluminium salt wadding body is loose, frangible, sinking speed is slow, but overcome molysite wadding body it is smaller, processing after The deeper disadvantage of coloration, so that the floc sedimentation that flocculation is formed is not only compact, closely knit, sinking speed is fast, supernatant coloration reduces.Simultaneously The pH value use scope of polyion network cyanogen agent is wider, generally 5-11, and 6-9 effect is best.Polyion network cyanogen agent energy and water are to appoint The mixing of meaning ratio, coagulation effect is good, and can effectively reduce each pollutant.Number of the component in complexing agent is 45- 55 parts, preferably 48-53 parts.
Graft starch is the two of the host agent of the complexing agent, and starch graft copolymer structure is as follows
A represents the dehydrated glucose unit among starch;M indicates the repeated monomer being grafted in graft copolymerization, such as CH2=CHCOOH, CH2=CHCONH2、CH2=CHCOOCH2NR3One of, starch-grafted obtained copolymer is water solubility Copolymer has double action of adsorbing and flocculate.It can effectively adsorb hazardous contaminant, especially have to difficult to degrade Machine pollutant adsorption effect is more preferable, decolourizes, except cyanogen drop nitrogen goes COD effect obvious.Content of the component in complexing agent is 15-25 Part, preferably 18-22 parts.
Polydimethyl diallyl ammonium chloride is the three of the host agent of complexing agent, safe and nontoxic, soluble easily in water, decoloration effect Fruit is splendid and facilitates flocculation sedimentation, and water pollutant and organic matter is enable to reduce to greatest extent.The component is in complexing agent In content be 5-10 parts, preferably 6-8 parts.
Diatomite contains multistage, a large amount of, ordered arrangement micropores, and it is many excellent that this unique structure imparts diatomite Performance;Chemical property is stable, porosity is big, large specific surface area, strong adsorption.The pollutant in waste water can effectively be adsorbed Matter purifies water.Work as composite diatomite white vitriol and Na2Fe04, polymeric aluminium ferrum silicate, poly- phosphorus iron chloride, lemon simultaneously After sour ferrous and graft starch, polydimethyl diallyl ammonium chloride collective effect, diatomite surface and internal surface of hole distribution A large amount of silicone hydroxyl, this special mechanism are conducive to the progress of flocculating setting, and various pollutants in water can be made to be able to maximum The removal of limit.Diatomite and Zinc vitriol is compound according to mass ratio 0.4:1-1:1, and compounding ingredients are in complexing agent Number is 2-8 parts, preferably 4-6 parts.
Sodium tripolyphosphate can effectively adjust pH value, so that each substance is played good synergistic effect, the component is in complexing agent In be 1-5 parts, preferably 2-4 parts.
Isopropanol is stabilizer, makes to stablize except cyanogen drop nitrogen decolorising agent property, period of storage increases, and the component is in complexing agent It is 0.1-1 parts, preferably 0.5-1 parts.
Compared with prior art, the beneficial effects of the present invention are:
1) between complexing agent component of the invention have good concertedness, mutually rush property, property stablize, belong to green, Environmental protection, degradable material, it is environmentally friendly, be not easily decomposed.
2) complexing agent of the invention is easy to operate, it is easy to accomplish one barrel of change scheme, it can without adding other assistant medicaments Reach ideal wastewater containing phenol and cyanide Effluent criteria.
3) of the invention except nitrogen decolorising agent drops in cyanogen, with it is excellent except cyanogen, drop nitrogen, remove COD, decolorizing effect;Applied to coke It is up to standard and stable to change wastewater containing phenol and cyanide effluent index, is worthy to be popularized.
4) of the invention except cyanogen drop nitrogen decolorising agent is at low cost, it is good to be easy compounding, stability;Application method is simple, is easy to grasp Make.
5) complexing agent applicable pH range of the invention is extensive, especially good with effect within the scope of 6-9.
6) guarantee effluent characteristics, stable water outlet reduces the construction of subsequent structures.
7) feature big for wastewater containing phenol and cyanide change of water quality except cyanogen drop nitrogen decolorising agent of the invention, this complexing agent embodies superior Performance, guarantee stable water outlet and meet the requirement of environmental protection, can be promoted the use of in wastewater containing phenol and cyanide.
Specific embodiment
The present invention is described in detail below, it should be noted that implementation of the invention embodiment party not limited to the following Formula.
It is suitble to the cyanogen that removes of coking wastewater containing phenol and cyanide to drop nitrogen decolorising agent, constituent and mass fraction are as follows: polyion network cyanogen agent 45-55 parts, 15-25 parts of graft starch, 5-10 parts of polydimethyl diallyl ammonium chloride, composite diatomite white vitriol 2-8 Part, 1-5 parts of sodium tripolyphosphate, 0.1-1 parts of isopropanol, remaining be water.
It is suitble to the cyanogen that removes of coking wastewater containing phenol and cyanide to drop nitrogen decolorising agent, constituent and mass fraction are preferred are as follows: polyion network 48-53 parts of cyanogen agent, 18-22 parts of graft starch, 6-8 parts of polydimethyl diallyl ammonium chloride, composite diatomite white vitriol 4-6 parts, 2-4 parts of sodium tripolyphosphate, 0.5-1 parts of isopropanol, remaining be water.
The polyion network cyanogen agent is mixed by following raw materials example in mass ratio: Na2Fe04: polymeric aluminium ferrum silicate: Poly- phosphorus iron chloride: dicyandiamide formaldehyde resin: ferrous citrate=(4~5): (3~4): (2~3): (0.5~1): (1~1.5).
The mass ratio of diatomite and white vitriol in the composite diatomite white vitriol are as follows: diatomite: seven water sulphur Sour zinc=0.4:1~1:1.
It is suitble to the preparation method for removing cyanogen drop nitrogen decolorising agent of coking wastewater containing phenol and cyanide, the specific method is as follows:
1) diatomite and white vitriol are put into four-hole boiling flask according to mass ratio 0.4:1~1:1, according to solid-liquid quality Be added proper amount of clear water than 1:5, then with 1-2ml/ minute speed be added dropwise concentration for 30% sulfuric acid in flask, by four-hole boiling flask It is placed on digital display intelligent temperature control magnetic stirring apparatus, is reacted 2-2.5 hours under 40-45 DEG C, the stirring condition of 80r/min;It will Reactant filters, is dry, is placed in Muffle furnace and roasts 4-5 hours at 400-450 DEG C, calcining matter coolant seal is spare, institute Obtaining preparation is composite diatomite white vitriol.
2) polyion network cyanogen agent is put into reaction kettle, distilled water is added according to the mass ratio of solute and water 1:2.2-3.2, After stirring 20-25 minutes with the speed of 150-180r/min, composite diatomite white vitriol is put into, is continued with 100-150r/ The speed of min stirs, and stirring adds 15-25 parts of graft starch, polydimethyl diallyl ammonium chloride 5- after liquid phase is homogeneous 10 parts, 1-5 parts of sodium tripolyphosphate, 0.1-1 parts of isopropanol, are stirred with 120-150r/min, after stirring 15-20 minutes, then with 50- The speed of 80r/min stirs 15-20 minutes, is made after mixing except nitrogen decolorising agent drops in cyanogen.
It is suitble to the application method for removing cyanogen drop nitrogen decolorising agent of coking wastewater containing phenol and cyanide, the dosage that nitrogen decolorising agent is dropped except cyanogen Are as follows:
T=170 × CT-N CCOD≤350mg/L
In formula: except nitrogen decolorising agent dosage, mg/L drop in cyanogen in T- wastewater containing phenol and cyanide;
CT-NTotal cyanide content in wastewater containing phenol and cyanide, mg/L;
CCODCOD content in wastewater containing phenol and cyanide, mg/L.
The present invention does not base oneself upon in the research of wastewater containing phenol and cyanide processing unit and processing method, but is to base oneself upon from medicament angle Point is made the compound cyanogen that removes and drops nitrogen decolorising agent, is used in combination with biochemical method, to reach better treatment effect.Cyanogen is removed simultaneously It drops nitrogen decolorising agent and uses one barrel of change scheme, i.e., the multicomponent chemical substance of different role is reached into component by various processing methods Between stabilization coexist, and give full play to collaboration, mutual rush acts on, preferably reach except cyanogen, drop nitrogen, remove COD, decolorizing effect.
Except cyanogen drop nitrogen decolorising agent is added among bio-chemical effluent according to corresponding proportion, coke can preferably be reduced by being verified repeatedly Change wastewater containing phenol and cyanide items pollutant index, reaches wastewater containing phenol and cyanide water outlet processing requirement.The present invention is used except cyanogen drop nitrogen decoloration simultaneously Agent is at low cost, operation is simple, is easily achieved, and complexing agent property is stablized, and is not easily decomposed.Na2Fe04, graft starch, poly- diformazan Base diallyl ammonium chloride, dicyandiamide formaldehyde are used in combination, and enhance treatment effect, and ammonia nitrogen < is discharged after processing 10mg/L, COD < 80mg/L, cyanide < 0.2mg/L, coloration is less than 30 times.
The features of the present invention is further illustrated below by laboratory and field case.As the result is shown in laboratory and scene Application effect is good.
To better illustrate the present invention, it is easy to understand technical solution of the present invention, of the invention is typical but non-limiting Embodiment is as follows:
Table 1: it is made according to following ratio except nitrogen decolorising agent a, b, c drop in cyanogen.
Component number A (part) B (part) C (part)
Polyion network cyanogen agent 48 50 52
Composite diatomite white vitriol 7 6 4
Graft starch 20 21 18
Polydimethyl diallyl ammonium chloride 8 6 6
Sodium tripolyphosphate 4 3 2
Isopropanol 0.8 0.7 0.8
Water 120 125 130
Embodiment 1
Coking wastewater containing phenol and cyanide bio-chemical effluent pH is 7.47, total cyanogen 5.20mg/L, COD 210mg/L, ammonia nitrogen 27mg/L, coloration 300 times.It will be added in wastewater containing phenol and cyanide except cyanogen drop nitrogen decolorising agent a with the dosage of 884mg/L, stirring stood 20 after 10-15 seconds Minute measurement supernatant various pollutants index, obtains total cyanogen < 0.1mg/L, COD 59mg/L, ammonia nitrogen 8mg/L, coloration is lower than 30 times.
Embodiment 2
Coking wastewater containing phenol and cyanide bio-chemical effluent is taken, each index is as follows: pH 8.15, total cyanogen 9.5mg/L, COD 350mg/L, ammonia Nitrogen 57mg/L, 500 times of coloration.It will be added in wastewater containing phenol and cyanide, be stirred except cyanogen drop nitrogen decolorising agent b with the dosage of 1615mg/L 20 minutes measurement supernatant various pollutants indexs are stood after 10-15 seconds, obtain total cyanogen < 0.1mg/L, COD65mg/L, ammonia nitrogen 9mg/L, coloration are lower than 30 times.
Embodiment 3
Coking wastewater containing phenol and cyanide bio-chemical effluent is taken, each index is as follows: pH 7.94, total cyanogen 14mg/L, COD 570mg/L, ammonia Nitrogen 62mg/L, 900 times of coloration.It will be added in wastewater containing phenol and cyanide, be stirred except cyanogen drop nitrogen decolorising agent c with the dosage of 2490mg/L 20 minutes measurement supernatant various pollutants indexs are stood after 10-15 seconds, obtain total cyanogen < 0.1mg/L, COD 60mg/L, ammonia nitrogen 8.9mg/L, coloration are lower than 30 times.
Field application example
Live water quality situation: pH 7.56, total cyanogen 5.23mg/L, COD 240mg/L, ammonia nitrogen 32mg/L, 300 times of coloration. It will be added in system except cyanogen drop nitrogen decolorising agent b according to 890mg/L, through radical sedimentation basin, the water conservancy residence time, 1-1.5 was small When, measure supernatant total cyanogen 0.15mg/L, COD 43mg/L, ammonia nitrogen 7mg/L, 20 times of coloration.

Claims (6)

1. suitable coking wastewater containing phenol and cyanide except cyanogen drop nitrogen decolorising agent, which is characterized in that its constituent and mass fraction are as follows: mostly from 45-55 parts of sub- network cyanogen agent, 15-25 parts of graft starch, 5-10 parts of polydimethyl diallyl ammonium chloride, seven water sulphur of composite diatomite Sour zinc 2-8 parts, 1-5 parts of sodium tripolyphosphate, 0.1-1 parts of isopropanol, remaining be water.
2. suitable coking wastewater containing phenol and cyanide according to claim 1 except cyanogen drop nitrogen decolorising agent, which is characterized in that its form at Point and mass fraction are as follows: 48-53 parts of polyion network cyanogen agent, 18-22 parts of graft starch, polydimethyl diallyl ammonium chloride 6-8 Part, 4-6 parts of composite diatomite white vitriol, 2-4 parts of sodium tripolyphosphate, 0.5-1 parts of isopropanol, remaining be water.
3. nitrogen decolorising agent drops in the cyanogen that removes of suitable coking wastewater containing phenol and cyanide according to claim 1 or 2, which is characterized in that described Polyion network cyanogen agent is mixed by following raw materials example in mass ratio: Na2Fe04: polymeric aluminium ferrum silicate: poly- phosphorus iron chloride: Dicyandiamide formaldehyde resin: ferrous citrate=(4~5): (3~4): (2~3): (0.5~1): (1~1.5).
4. nitrogen decolorising agent drops in the cyanogen that removes of suitable coking wastewater containing phenol and cyanide according to claim 1 or 2, which is characterized in that described The mass ratio of diatomite and white vitriol in composite diatomite white vitriol are as follows: diatomite: white vitriol=0.4:1~ 1:1。
5. the preparation method for removing cyanogen drop nitrogen decolorising agent of suitable coking wastewater containing phenol and cyanide, feature exist as claimed in claim 1 or 2 In the specific method is as follows:
1) diatomite and white vitriol are put into four-hole boiling flask according to mass ratio 0.4:1~1:1, according to solid-liquid mass ratio 1: 5 are added clear water, then with 1-2ml/ minute speed be added dropwise concentration for 30% sulfuric acid in flask, in 40-45 DEG C, 80r/min Stirring condition under react 2-2.5 hours;Reactant is filtered, is dry, is placed in Muffle furnace and roasts 4-5 at 400-450 DEG C Hour, calcining matter coolant seal is spare, and gained preparation is composite diatomite white vitriol.
2) polyion network cyanogen agent is put into reaction kettle, distilled water is added according to the mass ratio of solute and water 1:2.2-3.2, with After the speed of 150-180r/min stirs 20-25 minutes, composite diatomite white vitriol is put into, is continued with 100-150r/min Speed stirring, stirring until liquid phase it is homogeneous after add 15-25 parts of graft starch, polydimethyl diallyl ammonium chloride 5-10 Part, 1-5 parts of sodium tripolyphosphate, 0.1-1 parts of isopropanol, are stirred with 120-150r/min, after stirring 15-20 minutes, then with 50- The speed of 80r/min stirs 15-20 minutes, is made after mixing except nitrogen decolorising agent drops in cyanogen.
6. the application method for removing cyanogen drop nitrogen decolorising agent of suitable coking wastewater containing phenol and cyanide as described in claim 1, which is characterized in that The dosage that nitrogen decolorising agent is dropped except cyanogen are as follows:
T=170 × CT-N CCOD≤350mg/L
In formula: except nitrogen decolorising agent dosage, mg/L drop in cyanogen in T- wastewater containing phenol and cyanide;
CT-NTotal cyanide content in wastewater containing phenol and cyanide, mg/L;
CCODCOD content in wastewater containing phenol and cyanide, mg/L.
CN201810926647.5A 2018-08-15 2018-08-15 Cyanogen-removing nitrogen-reducing decolorant suitable for coking phenol-cyanogen wastewater and preparation and use methods thereof Active CN109052594B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810926647.5A CN109052594B (en) 2018-08-15 2018-08-15 Cyanogen-removing nitrogen-reducing decolorant suitable for coking phenol-cyanogen wastewater and preparation and use methods thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810926647.5A CN109052594B (en) 2018-08-15 2018-08-15 Cyanogen-removing nitrogen-reducing decolorant suitable for coking phenol-cyanogen wastewater and preparation and use methods thereof

Publications (2)

Publication Number Publication Date
CN109052594A true CN109052594A (en) 2018-12-21
CN109052594B CN109052594B (en) 2021-12-03

Family

ID=64678421

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810926647.5A Active CN109052594B (en) 2018-08-15 2018-08-15 Cyanogen-removing nitrogen-reducing decolorant suitable for coking phenol-cyanogen wastewater and preparation and use methods thereof

Country Status (1)

Country Link
CN (1) CN109052594B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113772779A (en) * 2021-09-18 2021-12-10 鞍钢栗田(鞍山)水处理有限公司 Medicament for realizing reduction of low-concentration cyanide-containing coking wastewater sludge and preparation method thereof
CN115888970A (en) * 2022-11-22 2023-04-04 山东(烟台)中日产业技术研究院(烟台市产业技术研究院) Cyanide removal treatment method for cyanidation tailings

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS534348A (en) * 1976-06-11 1978-01-14 Nippon Steel Chemical Co Treating method of drainage of coking factory
CN101327984A (en) * 2008-07-15 2008-12-24 南通立源水处理技术有限公司 Multi-effect pollution-removing water purifying agent and application method thereof
CN101734780A (en) * 2009-12-15 2010-06-16 娄底市裕德科技有限公司 Oxidization coagulant for treating coking wastewater
CN101857300A (en) * 2010-07-16 2010-10-13 太原工业学院 A biochemical tail water advanced treatment agent for coking wastewater
WO2013078639A1 (en) * 2011-11-30 2013-06-06 Rohm And Haas Company Coking wastewater treatment
CN103288192A (en) * 2013-06-09 2013-09-11 吉林市英达水务科技有限责任公司 Method for synthesizing composite kieselguhr coagulant from kieselguhr waste liquor
CN104261535A (en) * 2014-09-28 2015-01-07 佑景天(北京)国际水环境研究中心有限公司 Efficient discoloring agent and discoloring treatment method of printing and dyeing wastewater
CN105198159A (en) * 2015-09-14 2015-12-30 山东杨帆环保工程有限公司 Coagulant for treating coking wastewater and method for treating coking wastewater by virtue of coagulant
CN106957070A (en) * 2017-03-20 2017-07-18 浙江清环保工程有限公司 A kind of rapidly and efficiently ammonia nitrogen removal agent and its preparation method and application
CN108046461A (en) * 2017-11-23 2018-05-18 南京悠谷新材料科技有限公司 Industrial circulation water treatment equipment

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS534348A (en) * 1976-06-11 1978-01-14 Nippon Steel Chemical Co Treating method of drainage of coking factory
CN101327984A (en) * 2008-07-15 2008-12-24 南通立源水处理技术有限公司 Multi-effect pollution-removing water purifying agent and application method thereof
CN101734780A (en) * 2009-12-15 2010-06-16 娄底市裕德科技有限公司 Oxidization coagulant for treating coking wastewater
CN101857300A (en) * 2010-07-16 2010-10-13 太原工业学院 A biochemical tail water advanced treatment agent for coking wastewater
WO2013078639A1 (en) * 2011-11-30 2013-06-06 Rohm And Haas Company Coking wastewater treatment
CN103288192A (en) * 2013-06-09 2013-09-11 吉林市英达水务科技有限责任公司 Method for synthesizing composite kieselguhr coagulant from kieselguhr waste liquor
CN104261535A (en) * 2014-09-28 2015-01-07 佑景天(北京)国际水环境研究中心有限公司 Efficient discoloring agent and discoloring treatment method of printing and dyeing wastewater
CN105198159A (en) * 2015-09-14 2015-12-30 山东杨帆环保工程有限公司 Coagulant for treating coking wastewater and method for treating coking wastewater by virtue of coagulant
CN106957070A (en) * 2017-03-20 2017-07-18 浙江清环保工程有限公司 A kind of rapidly and efficiently ammonia nitrogen removal agent and its preparation method and application
CN108046461A (en) * 2017-11-23 2018-05-18 南京悠谷新材料科技有限公司 Industrial circulation water treatment equipment

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
刘步林: "《农药剂型加工技术》", 31 October 1998, 化学工业出版社 *
张光华: "《水处理化学品制备与应用指南》", 31 October 2003, 中国石化出版社 *
段久芳: "《天然高分子材料》", 30 September 2016, 华中科技大学出版社 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113772779A (en) * 2021-09-18 2021-12-10 鞍钢栗田(鞍山)水处理有限公司 Medicament for realizing reduction of low-concentration cyanide-containing coking wastewater sludge and preparation method thereof
CN113772779B (en) * 2021-09-18 2023-06-09 鞍钢栗田(鞍山)水处理有限公司 Medicament for realizing sludge reduction of low-concentration cyanogen-containing coking wastewater and preparation method thereof
CN115888970A (en) * 2022-11-22 2023-04-04 山东(烟台)中日产业技术研究院(烟台市产业技术研究院) Cyanide removal treatment method for cyanidation tailings
CN115888970B (en) * 2022-11-22 2024-11-01 山东(烟台)中日产业技术研究院(烟台市产业技术研究院) Cyanide removal treatment method for cyanide tailings

Also Published As

Publication number Publication date
CN109052594B (en) 2021-12-03

Similar Documents

Publication Publication Date Title
CN105923735B (en) A kind of composite water treatment medicament and preparation method thereof based on ferrate
CN110316800B (en) Preparation and application methods of flocculant for coking wastewater treatment
CN102795696A (en) Coagulant used for advanced treatment of biochemical effluent of coking wastewater
CN105036269B (en) A kind of multiple-effect water treatment agent and preparation method thereof and method for treating water
CN101264997A (en) Method for processing film filtration concentrated solution of domestic refuse percolate treatment
KR101478305B1 (en) Inorganic coagulant for treating waste-water and preparation method of the same
CN102718295A (en) Compound medicament for treating coking wastewater and preparation method thereof
CN102963983B (en) Vertical flow artificial wetland substrate modified based on LDHs (layered double hydroxides) coating film and preparation method of substrate
Martín-Pozo et al. Removal of quinolone antibiotics from wastewaters and sewage sludge
CN111646534A (en) Coking phenol-cyanogen wastewater purifying agent and preparation method and application thereof
Song et al. Efficient removal of Cr (III)-carboxyl complex from neutral and high-salinity wastewater by nitrogen doped biomass-based composites
CN109052594A (en) Be suitble to coking wastewater containing phenol and cyanide removes cyanogen drop nitrogen decolorising agent and preparation, application method
CN101618922A (en) Method for processing landfill percolate
Zhen et al. Porous red mud ceramsite for aquatic phosphorus removal: Application in constructed wetlands
CN107814466B (en) DPT production wastewater treatment process
CN107188384A (en) The processing method of sludge
CN107963709A (en) A kind of high-efficiency sewage dephosphorization agent and its application in municipal wastewater advanced treating
CN102070263A (en) Coking phenol cyanogen sewage treating method
CN117185501B (en) A compartmentalized method for removing heavy metals using photoelectrons in collaboration with microorganisms
CN108126667B (en) Flocculating agent and preparation method thereof
CN108636365A (en) A kind of modified straw fiber adsorbing material and its application method
Wang et al. Using potassium ferrate as advanced treatment for municipal wastewater
CN104628105A (en) Organic sewage treatment complex reagent
CN119031966A (en) Metal salt coagulants
KR100732230B1 (en) Wastewater treatment agent for phosphorus removal and preparation method thereof

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
CB02 Change of applicant information

Address after: 114002 Dadaowan Industrial Zone A06-8, Anshan City, Liaoning Province

Applicant after: Angang Litian (Anshan) water treatment Co.,Ltd.

Address before: 114002 Dadaowan Industrial Zone A06-8, Anshan City, Liaoning Province

Applicant before: ANGANG BK GIULINI WATER TREATMENT CO.,LTD.

CB02 Change of applicant information
GR01 Patent grant
GR01 Patent grant