CN106698744A - Method for removing hydrazine hydrate in H acid waste water - Google Patents

Method for removing hydrazine hydrate in H acid waste water Download PDF

Info

Publication number
CN106698744A
CN106698744A CN201611111600.0A CN201611111600A CN106698744A CN 106698744 A CN106698744 A CN 106698744A CN 201611111600 A CN201611111600 A CN 201611111600A CN 106698744 A CN106698744 A CN 106698744A
Authority
CN
China
Prior art keywords
acid
hydrazine hydrate
parts
waste water
nitro
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
CN201611111600.0A
Other languages
Chinese (zh)
Other versions
CN106698744B (en
Inventor
方百红
杨鹏
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.)
NANJING LIANKAI ENVIRONMENTAL INSPECTION TECHNOLOGY Co.,Ltd.
Original Assignee
ZHEJIANG RIWA GROUP 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 ZHEJIANG RIWA GROUP Co Ltd filed Critical ZHEJIANG RIWA GROUP Co Ltd
Priority to CN201611111600.0A priority Critical patent/CN106698744B/en
Publication of CN106698744A publication Critical patent/CN106698744A/en
Application granted granted Critical
Publication of CN106698744B publication Critical patent/CN106698744B/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
    • C02F9/00Multistage treatment of water, waste water or sewage
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1493Selection of liquid materials for use as absorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/30Alkali metal compounds
    • B01D2251/304Alkali metal compounds of sodium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/60Inorganic bases or salts
    • B01D2251/604Hydroxides
    • 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
    • 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
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • 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
    • 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
    • C02F2101/38Organic compounds containing nitrogen
    • 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
    • C02F2101/40Organic compounds containing sulfur
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
  • Catalysts (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

The invention relates to a method for removing hydrazine hydrate in H acid waste water. The method comprises the following steps: denitration, primary reduction, secondary reduction and T acid segregation. The method is scientific and reasonable, further reduces water solution and protects the environment.

Description

A kind of method of hydrazine hydrate in removal H acid waste water
Technical field
The present invention relates to the side of hydrazine hydrate in hydrazine hydrate, more particularly to a kind of removal H acid waste water in one kind removal H acid waste water Method.
Background technology
H acid commodity are usually paste or powder.Cold water is slightly soluble in, is dissolved in the alkaline solutions such as soda ash and caustic soda.H- acid Mono-sodium salt mainly for the production of acidity, directly and reactive dye, such as acid fuchsin 6b, acid red G, Acid Black 10B, directly Black, Reactive Brilliant Red K-2BP, active purple k-3r, molten blue K-R of activity etc. more than 90 is planted, and these dyestuffs are used for wool spinning, the dye of bafta Color.
It is domestic main at present using " three sulfonation-alkali fusion " production H acid, will naphthalene sulfuric acid or 65% oleum enter Row sulfonation, obtains 1,3,6- naphthalene trisulfonic acids, then through in mixed acid nitrification, ammoniacal liquor and reduction obtains T acid ammonium salts, then by alkali fusion H acid is obtained with acidifying.Prepared by traditional T acid is to use iron powder reducing technique, although iron powder reducing technique cost is very low, is produced big Amount solid waste, so being eliminated already.The substitute is hydrogenating reduction and hydrazine hydrate reduction technique.Because using hydrazine hydrate reduction work Little is changed to original equipment when skill replaces iron powder technique, so using commonplace.But during hydrazine hydrate reduction, in order that 8- nitre Base -1,3,6- trisulfonic acid ammonium salts conversion often makes hydrazine hydrate excessive more than 25% completely, and this large amount of hydrazine hydrate is not only unrestrained Expense is fallen, but also serious pollution is caused to environment.
The content of the invention
The present invention mainly solves the deficiencies in the prior art, there is provided one kind is with insufficient amount of hydrazine hydrate to 8- nitre Base -1,3,6- trisulfonic acid ammonium salts are reduced, after ruing out of hydrazine hydrate, then with another reducing agent by remaining 8- nitros - The reduction of 1,3,6- trisulfonic acid ammonium salt is complete, and a kind of removal H acid waste water of the pollution problem of hydrazine hydrate is so solved from source The method of middle hydrazine hydrate.
Above-mentioned technical problem of the invention is mainly what is be addressed by following technical proposals:
The method of hydrazine hydrate, is carried out according to the following steps in a kind of removal H acid waste water:
A. denitration:With 3~4 hours to being passed through 4700 part 4% of aqueous sodium carbonate from bottom in 3500 parts of nitrification materials, Tail gas concentration is 32% sodium hydrate aqueous solution absorption;Whether sampling detection sees arrive terminal;If less than terminal, it is necessary to again Add 300~500 part 4% of aqueous sodium carbonate;
B. once reduce:It is that 20% ammoniacal liquor adjustment pH value is 8~9 with concentration, adds 25 parts of catalyst, is warming up to 95 DEG C, With 4 hours to being added dropwise the hydrazine hydrate that 200 parts of concentration are 80% in substrate, concentration be 80% hydrazine hydrate equivalent to 8- nitro -1, 1.4 times of 3,6- trisulfonic acid naphthalene molal quantitys, then run out of in 95~100 DEG C of reaction to hydrazine hydrates;
C. secondary reduction:It is 3 to adjust pH value with a small amount of hydrochloric acid, keeps temperature of charge at 95~100 DEG C;It is slowly added to 50 parts Reducing agent, continues to be incubated 3 hours at 100~104 DEG C, is controlled in sampling;If not being reacted to terminal, continue at 100~104 DEG C Insulation is complete to reaction;Catalyst is filtered out, recovery is used for multiple times, manufacturer's regeneration is returned after failure, mother liquor is collected;
D.T acid isolations:It is 1~2 to adjust mother liquor pH value with sulfuric acid, is subsequently adding 800 parts of anhydrous sodium sulfates;Continue to be cooled to 40 DEG C, T acid is filtered to obtain in stirring after 2 hours;
Preferably, described catalyst is Raney's nickel or Fe (OH)3/C;Wherein the addition of Raney's nickel be 8- nitros- The 1~10% of 1,3,6- trisulfonic acid naphthalene, Raney's nickel can be reused.
Preferably, described catalyst selects Fe (OH)3During/C, the method matched somebody with somebody is:By 30 parts of Iron(III) chloride hexahydrates In adding 300 parts of water with 5 points of activated carbons, be heated to 60~70 DEG C and stir 0.5 hour, then added under stirring 8- nitros- In the ammonium salt material of 1,3,6- trisulfonic acid naphthalene;Addition is 8- nitro -1, the 1~10% of 3,6- trisulfonic acid naphthalenes.
Preferably, described hydrazine hydrate and 8- nitro -1, the mol ratio of 3,6- trisulfonic acid naphthalenes is (1.0 ︰ 1)~(1.5 ︰ 1)。
Preferably, the used reducing agent of described second reduction be iron powder, zinc powder, vulcanized sodium, NaHS and Sodium polysulfide one kind therein.
Preferably, described judgement 8- nitro -1,3,6- trisulfonic acid naphthalene ammonium salts are fully converted to 8- amino -1,3,6- tri- The method of sulfonic acid naphthalene ammonium salt is:The material for having reduced is taken, constant volume surveys amino value and is designated as A1, same material is added substantial amounts of Zinc powder, is warming up to boiling, and it is 3 to adjust pH value with hydrochloric acid, is kept for 10 minutes, is then filtered, constant volume, measures amino value and is designated as A2, (A2﹣ A1)÷A1When × 100%≤0.5, for reaction is complete.
The method is scientific and reasonable, further reduces water pollution, environmental protection.
Specific embodiment
Below by embodiment, technical scheme is described in further detail.
Embodiment 1:The method of hydrazine hydrate, is carried out according to the following steps in a kind of removal H acid waste water:
A. denitration:With 3 hours to being passed through 4700 part 4% of aqueous sodium carbonate, tail from bottom in 3500 parts of nitrification materials Gas concentration is 32% sodium hydrate aqueous solution absorption;Whether sampling detection sees arrive terminal;If less than terminal, it is necessary to add again Enter 300 part 4% of aqueous sodium carbonate;
B. once reduce:It is that 20% ammoniacal liquor adjustment pH value is 8 with concentration, adds 25 parts of catalyst, 95 DEG C is warming up to, with 4 Hour to being added dropwise the hydrazine hydrate that 200 parts of concentration are 80% in substrate, concentration be 80% hydrazine hydrate equivalent to 8- nitro -1,3,6- 1.4 times of trisulfonic acid naphthalene molal quantity, then run out of in 95 DEG C of reaction to hydrazine hydrates;
C. secondary reduction:It is 3 to adjust pH value with a small amount of hydrochloric acid, keeps temperature of charge at 95 DEG C;It is slowly added to 50 parts of reduction Agent, continues to be incubated 3 hours at 100 DEG C, is controlled in sampling;If not being reacted to terminal, continue in 100 DEG C of insulations to having reacted Entirely;Catalyst is filtered out, recovery is used for multiple times, manufacturer's regeneration is returned after failure, mother liquor is collected;
D.T acid isolations:It is 1 to adjust mother liquor pH value with sulfuric acid, is subsequently adding 800 parts of anhydrous sodium sulfates;Continue to be cooled to 40 DEG C, T acid is filtered to obtain in stirring after 2 hours;
Described catalyst is Raney's nickel;Wherein the addition of Raney's nickel be 8- nitro -1,3,6- trisulfonic acid naphthalenes 1~ 10%, Raney's nickel can be reused.
Described hydrazine hydrate and 8- nitro -1, the mol ratio of 3,6- trisulfonic acid naphthalenes is (1.0 ︰ 1)~(1.5 ︰ 1).
The used reducing agent of described second reduction for iron powder, zinc powder, vulcanized sodium, NaHS and sodium polysulfide its In one kind.
Described judgement 8- nitro -1,3,6- trisulfonic acid naphthalene ammonium salts are fully converted to 8- amino -1,3,6- trisulfonic acid naphthalene ammoniums The method of salt is:The material for having reduced is taken, constant volume surveys amino value and is designated as A1, same material is added into substantial amounts of zinc powder, heat up To seething with excitement, it is 3 to adjust pH value with hydrochloric acid, is kept for 10 minutes, is then filtered, constant volume, measures amino value and is designated as A2, (A2﹣ A1)÷A1× When 100%≤0.5, for reaction is complete.
Embodiment 2:The method of hydrazine hydrate, is carried out according to the following steps in a kind of removal H acid waste water:
A. denitration:With 3.5 hours to being passed through 4700 part 4% of aqueous sodium carbonate from bottom in 3500 parts of nitrification materials, Tail gas concentration is 32% sodium hydrate aqueous solution absorption;Whether sampling detection sees arrive terminal;If less than terminal, it is necessary to again Add 400 part 4% of aqueous sodium carbonate;
B. once reduce:It is that 20% ammoniacal liquor adjustment pH value is 8.5 with concentration, adds 25 parts of catalyst, be warming up to 95 DEG C, uses 4 hours to being added dropwise the hydrazine hydrate that 200 parts of concentration are 80% in substrate, concentration be 80% hydrazine hydrate equivalent to 8- nitro -1,3, 1.4 times of 6- trisulfonic acid naphthalene molal quantitys, then run out of in 98 DEG C of reaction to hydrazine hydrates;
C. secondary reduction:It is 3 to adjust pH value with a small amount of hydrochloric acid, keeps temperature of charge at 98 DEG C;It is slowly added to 50 parts of reduction Agent, continues to be incubated 3 hours at 101 DEG C, is controlled in sampling;If not being reacted to terminal, continue in 101 DEG C of insulations to having reacted Entirely;Catalyst is filtered out, recovery is used for multiple times, manufacturer's regeneration is returned after failure, mother liquor is collected;
D.T acid isolations:It is 1.5 to adjust mother liquor pH value with sulfuric acid, is subsequently adding 800 parts of anhydrous sodium sulfates;Continue to be cooled to 40 DEG C, T acid is filtered to obtain in stirring after 2 hours;
Described catalyst is Fe (OH)3/C。
Described catalyst selects Fe (OH)3During/C, the method matched somebody with somebody is:By 30 parts of Iron(III) chloride hexahydrates and 5 points of activity Charcoal is added in 300 parts of water, is heated to 60~70 DEG C and is stirred 0.5 hour, and 8- nitro -1,3,6- tri- sulphurs are then added under stirring In the ammonium salt material of sour naphthalene;Addition is 8- nitro -1, the 1~10% of 3,6- trisulfonic acid naphthalenes.
Described hydrazine hydrate and 8- nitro -1, the mol ratio of 3,6- trisulfonic acid naphthalenes is (1.0 ︰ 1)~(1.5 ︰ 1).
The used reducing agent of described second reduction for iron powder, zinc powder, vulcanized sodium, NaHS and sodium polysulfide its In one kind.
Described judgement 8- nitro -1,3,6- trisulfonic acid naphthalene ammonium salts are fully converted to 8- amino -1,3,6- trisulfonic acid naphthalene ammoniums The method of salt is:The material for having reduced is taken, constant volume surveys amino value and is designated as A1, same material is added into substantial amounts of zinc powder, heat up To seething with excitement, it is 3 to adjust pH value with hydrochloric acid, is kept for 10 minutes, is then filtered, constant volume, measures amino value and is designated as A2, (A2﹣ A1)÷A1× When 100%≤0.5, for reaction is complete.
Embodiment 3:The method of hydrazine hydrate, is carried out according to the following steps in a kind of removal H acid waste water:
A. denitration:With 4 hours to being passed through 4700 part 4% of aqueous sodium carbonate, tail from bottom in 3500 parts of nitrification materials Gas concentration is 32% sodium hydrate aqueous solution absorption;Whether sampling detection sees arrive terminal;If less than terminal, it is necessary to add again Enter 500 part 4% of aqueous sodium carbonate;
B. once reduce:It is that 20% ammoniacal liquor adjustment pH value is 9 with concentration, adds 25 parts of catalyst, 95 DEG C is warming up to, with 4 Hour to being added dropwise the hydrazine hydrate that 200 parts of concentration are 80% in substrate, concentration be 80% hydrazine hydrate equivalent to 8- nitro -1,3,6- 1.4 times of trisulfonic acid naphthalene molal quantity, then run out of in 100 DEG C of reaction to hydrazine hydrates;
C. secondary reduction:It is 3 to adjust pH value with a small amount of hydrochloric acid, keeps temperature of charge at 100 DEG C;It is slowly added to 50 parts of reduction Agent, continues to be incubated 3 hours at 104 DEG C, is controlled in sampling;If not being reacted to terminal, continue in 104 DEG C of insulations to having reacted Entirely;Catalyst is filtered out, recovery is used for multiple times, manufacturer's regeneration is returned after failure, mother liquor is collected;
D.T acid isolations:It is 2 to adjust mother liquor pH value with sulfuric acid, is subsequently adding 800 parts of anhydrous sodium sulfates;Continue to be cooled to 40 DEG C, T acid is filtered to obtain in stirring after 2 hours;
Described catalyst is Raney's nickel.
Described hydrazine hydrate and 8- nitro -1, the mol ratio of 3,6- trisulfonic acid naphthalenes is (1.0 ︰ 1)~(1.5 ︰ 1).
The used reducing agent of described second reduction for iron powder, zinc powder, vulcanized sodium, NaHS and sodium polysulfide its In one kind.
Described judgement 8- nitro -1,3,6- trisulfonic acid naphthalene ammonium salts are fully converted to 8- amino -1,3,6- trisulfonic acid naphthalene ammoniums The method of salt is:The material for having reduced is taken, constant volume surveys amino value and is designated as A1, same material is added into substantial amounts of zinc powder, heat up To seething with excitement, it is 3 to adjust pH value with hydrochloric acid, is kept for 10 minutes, is then filtered, constant volume, measures amino value and is designated as A2, (A2﹣ A1)÷A1× When 100%≤0.5, for reaction is complete.

Claims (6)

1. in a kind of removal H acid waste water hydrazine hydrate method, it is characterised in that carry out according to the following steps:
A. denitration:With 3~4 hours to being passed through 4700 part 4% of aqueous sodium carbonate, tail gas from bottom in 3500 parts of nitrification materials Absorbed with the sodium hydrate aqueous solution that concentration is 32%;Whether sampling detection sees arrive terminal;If less than terminal, it is necessary to add 300~500 part 4% of aqueous sodium carbonate;
B. once reduce:It is that to adjust pH value be 8~9 to 20% ammoniacal liquor with concentration, adds 25 parts of catalyst, is warming up to 95 DEG C, it is small with 4 When to being added dropwise the hydrazine hydrate that 200 parts of concentration are 80% in substrate, concentration be 80% hydrazine hydrate equivalent to 8- nitro -1,3,6- tri- 1.4 times of sulfonic acid naphthalene molal quantity, then run out of in 95~100 DEG C of reaction to hydrazine hydrates;
C. secondary reduction:It is 3 to adjust pH value with a small amount of hydrochloric acid, keeps temperature of charge at 95~100 DEG C;It is slowly added to 50 parts of reduction Agent, continues to be incubated 3 hours at 100~104 DEG C, is controlled in sampling;If not being reacted to terminal, continue in 100~104 DEG C of insulations It is complete to reacting;Catalyst is filtered out, recovery is used for multiple times, manufacturer's regeneration is returned after failure, mother liquor is collected;
D.T acid isolations:It is 1~2 to adjust mother liquor pH value with sulfuric acid, is subsequently adding 800 parts of anhydrous sodium sulfates;Continue to be cooled to 40 DEG C, T acid is filtered to obtain in stirring after 2 hours.
2. in a kind of removal H acid waste water according to claim 1 hydrazine hydrate method, it is characterised in that:Described catalysis Agent is Raney's nickel or Fe (OH)3/C;Wherein the addition of Raney's nickel is 8- nitro -1, the 1~10% of 3,6- trisulfonic acid naphthalenes, thunder Buddhist nun Nickel can be reused.
3. in a kind of removal H acid waste water according to claim 2 hydrazine hydrate method, it is characterised in that:Described catalysis Fe (OH) is selected in agent3During/C, the method matched somebody with somebody is:During 30 parts of Iron(III) chloride hexahydrates and 5 points of activated carbons are added into 300 parts of water, plus Hot to 60~70 DEG C are stirred 0.5 hour, 8- nitro -1 are then added under stirring, in the ammonium salt material of 3,6- trisulfonic acid naphthalenes; Addition is 8- nitro -1, the 1~10% of 3,6- trisulfonic acid naphthalenes.
4. in a kind of removal H acid waste water according to claim 1 hydrazine hydrate method, it is characterised in that:Described hydration Hydrazine and 8- nitro -1, the mol ratio of 3,6- trisulfonic acid naphthalenes is (1.0 ︰ 1)~(1.5 ︰ 1).
5. in a kind of removal H acid waste water according to claim 1 hydrazine hydrate method, it is characterised in that:Described second The used reducing agent of secondary reduction is iron powder, zinc powder, vulcanized sodium, NaHS and sodium polysulfide one kind therein.
6. in a kind of removal H acid waste water according to claim 1 hydrazine hydrate method, it is characterised in that:Described judgement 8- nitro -1,3,6- trisulfonic acid naphthalene ammonium salts are fully converted to 8- amino -1, and the method for 3,6- trisulfonic acid naphthalene ammonium salts is:Take and reduce Material, constant volume, survey amino value be designated as A1, same material is added into substantial amounts of zinc powder, boiling is warming up to, adjust pH value with hydrochloric acid It is 3, is kept for 10 minutes, then filter, constant volume, measures amino value and be designated as A2, (A2﹣ A1)÷A1It is reaction when × 100%≤0.5 Completely.
CN201611111600.0A 2016-12-06 2016-12-06 A method of hydrazine hydrate in removal H acid waste water Active CN106698744B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201611111600.0A CN106698744B (en) 2016-12-06 2016-12-06 A method of hydrazine hydrate in removal H acid waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201611111600.0A CN106698744B (en) 2016-12-06 2016-12-06 A method of hydrazine hydrate in removal H acid waste water

Publications (2)

Publication Number Publication Date
CN106698744A true CN106698744A (en) 2017-05-24
CN106698744B CN106698744B (en) 2019-10-18

Family

ID=58937539

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201611111600.0A Active CN106698744B (en) 2016-12-06 2016-12-06 A method of hydrazine hydrate in removal H acid waste water

Country Status (1)

Country Link
CN (1) CN106698744B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107602422A (en) * 2017-09-11 2018-01-19 吴江梅堰三友染料化工有限公司 A kind of clean type product 1,6,1,7 mixes the preparation method of 1-naphthlamine-6-sulfonic acid
CN114230078A (en) * 2021-12-21 2022-03-25 武汉瑞阳化工有限公司 Comprehensive utilization method of acidic wastewater generated in 1-fluoronaphthalene production

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04210954A (en) * 1991-02-25 1992-08-03 Sugai Kagaku Kogyo Kk Production of 1-amino-8-hydroxynaphthalene-3,6-disulfonic acid
CN101367753A (en) * 2008-10-15 2009-02-18 湖北楚源高新科技股份有限公司 Novel continuous nitrification denitrating, abstraction, hydrogenation reduction production process for H acid
CN101823968A (en) * 2010-05-21 2010-09-08 南通龙翔化工有限公司 Method for preparing 1,8-diaminonaphthalene by reducing 1,8-dinitronaphthalene with hydrazine hydrate
CN102936214A (en) * 2011-08-15 2013-02-20 中国中化股份有限公司 Method for clean preparation H acid
CN104592063A (en) * 2014-12-24 2015-05-06 青岛奥盖克化工股份有限公司 Environment-friendly production process of H acid

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04210954A (en) * 1991-02-25 1992-08-03 Sugai Kagaku Kogyo Kk Production of 1-amino-8-hydroxynaphthalene-3,6-disulfonic acid
CN101367753A (en) * 2008-10-15 2009-02-18 湖北楚源高新科技股份有限公司 Novel continuous nitrification denitrating, abstraction, hydrogenation reduction production process for H acid
CN101823968A (en) * 2010-05-21 2010-09-08 南通龙翔化工有限公司 Method for preparing 1,8-diaminonaphthalene by reducing 1,8-dinitronaphthalene with hydrazine hydrate
CN102936214A (en) * 2011-08-15 2013-02-20 中国中化股份有限公司 Method for clean preparation H acid
CN104592063A (en) * 2014-12-24 2015-05-06 青岛奥盖克化工股份有限公司 Environment-friendly production process of H acid

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107602422A (en) * 2017-09-11 2018-01-19 吴江梅堰三友染料化工有限公司 A kind of clean type product 1,6,1,7 mixes the preparation method of 1-naphthlamine-6-sulfonic acid
CN107602422B (en) * 2017-09-11 2020-05-29 吴江梅堰三友染料化工有限公司 Preparation method of cleaning type product 1,6, 1,7 mixed clevuric acid
CN114230078A (en) * 2021-12-21 2022-03-25 武汉瑞阳化工有限公司 Comprehensive utilization method of acidic wastewater generated in 1-fluoronaphthalene production
CN114230078B (en) * 2021-12-21 2023-09-22 武汉瑞阳化工有限公司 Comprehensive utilization method of acid wastewater generated in production of 1-fluoronaphthalene

Also Published As

Publication number Publication date
CN106698744B (en) 2019-10-18

Similar Documents

Publication Publication Date Title
CN101717355B (en) Method for synthesizing dyestuff intermediate H acid by naphthalene
CN101381331B (en) Method for preparing color-forming intermediate H acids
CN103937286B (en) A kind of clean preparation method of disperse dyes
CN101880247A (en) Method for producing naphthalene sulfonic formaldehyde condensation compound
CN101838174B (en) Preparation method of bromo-nitroaniline dye stuff intermediate
CN103739524B (en) A kind of preparation method of H acid monosodium salt
CN105694524B (en) A kind of preparation method of acid black 172
CN102602938A (en) Method for preparing precipitate white carbon black by utilizing serpentine tailings
CN106698744A (en) Method for removing hydrazine hydrate in H acid waste water
CN105085411A (en) Preparation method of 6-hydroxy-2,3,5-triamidopyrimidine sulfate
CN103613511A (en) Dilute sulfuric acid diazotization process of substituted phenylamine
CN102320635A (en) Comprehensive utilization method of waste sulfuric acid of sulfonated products
CN104861690B (en) Method used for preparing disperse blue 360
CN101402552B (en) Method for producing m-cresol with direct hydrolyzation
CN103205134B (en) Method for synthesizing DSD (4, 4'-diaminostilbene-2, 2'-disulfonic) acid-triazine fluorescent brightening agents
CN104927394A (en) Synthetic process for active dye black
CN103466707A (en) Production method of chromic chloride hexahydrate
CN106587494A (en) Method for improving ammonia-nitrogen content of H acid wastewater
CN109535040A (en) A kind of preparation method of clean type product amido-G-acid
CN101798278A (en) Method for preparing thiodipropionic acid
CN102627531A (en) Method for producing acicular 2, 5-dimethylphenol by water melt crystallization
CN102070552B (en) Method for preparing 3-amino-5-nitro-2,1-benzisothiazole and diazonium salt thereof
CN104327535A (en) Preparation method of acid black 172
CN101531831B (en) Production method of direct blended brown D-RS dye
CN108003070B (en) Sulfonation method in H acid production

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right

Effective date of registration: 20210318

Address after: 355200 No.44 Jishi Road, Taimushan Town, Fuding City, Ningde City, Fujian Province

Patentee after: Lin Chenyi

Address before: 311203 Six Work Sections Outside Reclamation of Yipeng Street, Dajiangdong Industrial Agglomeration Area, Hangzhou City, Zhejiang Province

Patentee before: ZHEJIANG RIWA GROUP Co.,Ltd.

TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20210811

Address after: 210000 floor 2, 3 and 4, building C7, No.9 Kechuang Avenue, intelligent manufacturing Industrial Park (Zhongshan area), Jiangbei new district, Nanjing City, Jiangsu Province

Patentee after: NANJING LIANKAI ENVIRONMENTAL INSPECTION TECHNOLOGY Co.,Ltd.

Address before: 355200 No.44 Jishi Road, Taimushan Town, Fuding City, Ningde City, Fujian Province

Patentee before: Lin Chenyi

TR01 Transfer of patent right