CN109052709A - A kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions - Google Patents

A kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions Download PDF

Info

Publication number
CN109052709A
CN109052709A CN201810894224.XA CN201810894224A CN109052709A CN 109052709 A CN109052709 A CN 109052709A CN 201810894224 A CN201810894224 A CN 201810894224A CN 109052709 A CN109052709 A CN 109052709A
Authority
CN
China
Prior art keywords
nitrogen
ammonia
high ammonia
nitrogen wastewater
waste water
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
CN201810894224.XA
Other languages
Chinese (zh)
Inventor
武善国
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.)
Suzhou Rong Xuan Environmental Protection Co Ltd
Original Assignee
Suzhou Rong Xuan Environmental Protection 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 Suzhou Rong Xuan Environmental Protection Co Ltd filed Critical Suzhou Rong Xuan Environmental Protection Co Ltd
Priority to CN201810894224.XA priority Critical patent/CN109052709A/en
Publication of CN109052709A publication Critical patent/CN109052709A/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
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • C02F1/048Purification of waste water by evaporation
    • 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
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • C02F1/586Treatment of water, waste water, or sewage by removing specified dissolved compounds by removing ammoniacal nitrogen
    • 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
    • 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

Abstract

The present invention relates to a kind of techniques based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions, carry out wastewater treatment in the following order, and through waste collection slot, PH adjustment tank, cold boiler to tail treatment trough, PH adjustment tank also serves as ammonia nitrogen absorber, improve absorption rate.A kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions of the present invention, Treated sewage reusing while having reached discharge standard, waste liquid cocnentration factor is big, and no exhaust gas generates, and occupied area is small.

Description

A kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions
Technical field
The present invention relates to a kind of industrial waste water with high ammoniac nitrogen treatment process, especially a kind of based on evaporation process under acid washing conditions The technique of high ammonia-nitrogen wastewater.
Background technique
As country increasingly payes attention to environmental protection, in recent years, some large manufacturers introduce external production technology and are given birth to It produces, the water quality requirement for draining a certain water body to reach sewage or reusing, and it is purified.Sewage treatment is extensive Applied to every field such as environmental protection, urban landscape, medical treatment, building, agricultural, traffic, the energy, food and drink, petrochemical industry, small water low viscosity The industrial wastewater of high ammonia nitrogen, pollutant concentration is high, and waste component is complicated, and poisonous and harmful substance is more.We have developed one kind thus Based on the technique of evaporation process high ammonia-nitrogen wastewater under acid washing conditions, Treated sewage reusing while having reached discharge standard, waste liquid concentration Than big, no exhaust gas is generated, and occupied area is small.
Summary of the invention
It is provided the invention aims to overcome the deficiencies in the prior art based on the high ammonia nitrogen of evaporation process under acid washing conditions The technique of waste water.
In order to achieve the above objectives, the technical solution adopted by the present invention is that: one kind is based on the high ammonia of evaporation process under acid washing conditions The technique of nitrogen waste water, which is characterized in that comprise the steps of:
Step 1: high ammonia-nitrogen wastewater is first collected in waste collection slot, and the capacity that the waste collection slot collects waste water is small Ammonia-nitrogen content is greater than 3000ppm in 10t/d, the high ammonia-nitrogen wastewater, and the high ammonia-nitrogen wastewater is the industrial wastewater of low viscosity, The waste collection slot can store one day water;
Step 2: the high ammonia-nitrogen wastewater flow to PH adjustment tank, strong acid is added to the PH adjustment tank, by the high ammonia nitrogen Waste water is adjusted to strong acid condition, and the PH adjustment tank is tower structure, and the ratio of height to diameter of the PH adjustment tank reaches 5: 1, the PH Adjustment tank can be used as ammonia nitrogen absorber simultaneously;
Step 3: the high ammonia-nitrogen wastewater under the strong acid condition, which enters in cold boiler, to be evaporated, the high ammonia nitrogen Condensation ammonia nitrogen after waste water evaporation can be reduced to 200mg/L;
Step 4: the dope after evaporative condenser, waste water flow to tail treatment trough, the outer processing of solidliquid mixture committee of high concentration;
Step 5: the tail treatment trough carries out NH_3-N treating to waste water, the ammonia nitrogen in the waste water be reduced to 20mg/L with Under;
Step 6: the ammonia nitrogen waste water can be with qualified discharge or reuse when reaching 20mg/L.
Preferably, the Waste water concentrating after the cold boiler is than big, and solid waste or raffinate amount are less than 10%.
Due to the application of the above technical scheme, compared with the prior art, the invention has the following advantages:
1. high ammonia nitrogen waste liquid cocnentration factor is big, less than 10%, water outlet can reuse for solid waste or raffinate amount;
2. process flow is simple, using MVP evaporation technology, low energy consumption, and no exhaust gas generates;
3. process equipment is few, take up little area, operational management is convenient.
Detailed description of the invention
Fig. 1 is the process diagram of the present invention based on the technique of evaporation process high ammonia-nitrogen wastewater under acid washing conditions;
Wherein: 1, waste water;2, waste collection slot;3, PH adjustment tank;4, strong acid;5, cold boiler;6, tail treatment trough;7, The outer processing of solidliquid mixture committee;8, qualified discharge or reuse.
Specific embodiment
Below in conjunction with the accompanying drawings and specific embodiment, the present invention is described in further details.
Embodiment one:
A kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions, which is characterized in that comprise the steps of:
Step 1: high ammonia-nitrogen wastewater 1 is first collected in waste collection slot 2, and the waste collection slot 2 collects the capacity of waste water For 9.9t/d, ammonia-nitrogen content is 3001ppm in the high ammonia-nitrogen wastewater 1, and the high ammonia-nitrogen wastewater 1 is the Industry Waste of low viscosity Water, the waste collection slot 2 can store one day water;
Step 2: the high ammonia-nitrogen wastewater 1 flow to PH adjustment tank 3, strong acid 4 is added to the PH adjustment tank 3, by the height Ammonia nitrogen waste water 1 is adjusted to strong acid condition, and the PH adjustment tank 3 is tower structure, and the ratio of height to diameter of the PH adjustment tank 3 reaches 5: 1, The PH adjustment tank 3 can be used as ammonia nitrogen absorber simultaneously;
Step 3: the high ammonia-nitrogen wastewater 1 under the strong acid condition, which enters in cold boiler 5, to be evaporated, the high ammonia Condensation ammonia nitrogen after nitrogen waste water 1 evaporates can be reduced to 200mg/L;
Step 4: the dope after evaporative condenser, waste water flow to tail treatment trough 6, the outer processing of solidliquid mixture committee of high concentration 7;
Step 5: the tail treatment trough 6 carries out NH_3-N treating to waste water, and the ammonia nitrogen in the waste water is reduced to 20mg/L;
Step 6: the ammonia nitrogen waste water can be with qualified discharge or reuse 8 when reaching 20mg/L.
Preferably, for the Waste water concentrating after the cold boiler 5 than big, solid waste or raffinate amount are 9.5%.
Embodiment two:
A kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions, which is characterized in that comprise the steps of:
Step 1: high ammonia-nitrogen wastewater 1 is first collected in waste collection slot 2, and the waste collection slot 2 collects the capacity of waste water For 9t/d, ammonia-nitrogen content is 4000ppm in the high ammonia-nitrogen wastewater 1, and the high ammonia-nitrogen wastewater 1 is the industrial wastewater of low viscosity, The waste collection slot 2 can store one day water;
Step 2: the high ammonia-nitrogen wastewater 1 flow to PH adjustment tank 3, strong acid 4 is added to the PH adjustment tank 3, by the height Ammonia nitrogen waste water 1 is adjusted to strong acid condition, and the PH adjustment tank 3 is tower structure, and the ratio of height to diameter of the PH adjustment tank 3 reaches 5: 1, The PH adjustment tank 3 can be used as ammonia nitrogen absorber simultaneously;
Step 3: the high ammonia-nitrogen wastewater 1 under the strong acid condition, which enters in cold boiler 5, to be evaporated, the high ammonia Condensation ammonia nitrogen after nitrogen waste water 1 evaporates can be reduced to 200mg/L;
Step 4: the dope after evaporative condenser, waste water flow to tail treatment trough 6, the outer processing of solidliquid mixture committee of high concentration 7;
Step 5: the tail treatment trough 6 carries out NH_3-N treating to waste water, and the ammonia nitrogen in the waste water is reduced to 19mg/L;
Step 6: the ammonia nitrogen waste water can be with qualified discharge or reuse 8 when reaching 20mg/L.
Preferably, for the Waste water concentrating after the cold boiler 5 than big, solid waste or raffinate amount are 9%.
It is described based under acid washing conditions the advantages of the technique of evaporation process high ammonia-nitrogen wastewater it is as follows:
1. high ammonia nitrogen waste liquid cocnentration factor is big, less than 10%, water outlet can reuse for solid waste or raffinate amount;
2. process flow is simple, using MVP evaporation technology, low energy consumption, and no exhaust gas generates;
3. process equipment is few, take up little area, operational management is convenient.
The above is only specific application examples of the invention, are not limited in any way to protection scope of the present invention.All uses Equivalent transformation or equivalent replacement and the technical solution formed, all fall within rights protection scope of the present invention.

Claims (2)

1. a kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions, which is characterized in that comprise the steps of:
Step 1: high ammonia-nitrogen wastewater is first collected in waste collection slot, and the capacity that the waste collection slot collects waste water is less than 10t/d, ammonia-nitrogen content is greater than 3000ppm in the high ammonia-nitrogen wastewater, and the high ammonia-nitrogen wastewater is the industrial wastewater of low viscosity, institute One day water can be stored by stating waste collection slot;
Step 2: the high ammonia-nitrogen wastewater flow to PH adjustment tank, strong acid is added to the PH adjustment tank, by the high ammonia-nitrogen wastewater It adjusts to strong acid condition, the PH adjustment tank is tower structure, and the ratio of height to diameter of the PH adjustment tank reaches 5: 1, the PH adjustment Slot can be used as ammonia nitrogen absorber simultaneously;
Step 3: the high ammonia-nitrogen wastewater under the strong acid condition, which enters in cold boiler, to be evaporated, the high ammonia-nitrogen wastewater Condensation ammonia nitrogen after evaporation can be reduced to 200mg/L;
Step 4: the dope after evaporative condenser, waste water flow to tail treatment trough, the outer processing of solidliquid mixture committee of high concentration;
Step 5: the tail treatment trough carries out NH_3-N treating to waste water, and the ammonia nitrogen in the waste water is reduced to 20mg/L or less;
Step 6: the ammonia nitrogen waste water can be with qualified discharge or reuse when reaching 20mg/L.
2. the technique according to claim 1 based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions, it is characterised in that: described Waste water concentrating after cold boiler is than big, and solid waste or raffinate amount are less than 10%.
CN201810894224.XA 2018-08-08 2018-08-08 A kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions Pending CN109052709A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810894224.XA CN109052709A (en) 2018-08-08 2018-08-08 A kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810894224.XA CN109052709A (en) 2018-08-08 2018-08-08 A kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions

Publications (1)

Publication Number Publication Date
CN109052709A true CN109052709A (en) 2018-12-21

Family

ID=64678080

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810894224.XA Pending CN109052709A (en) 2018-08-08 2018-08-08 A kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions

Country Status (1)

Country Link
CN (1) CN109052709A (en)

Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008207118A (en) * 2007-02-27 2008-09-11 Hiroshima Univ Method, apparatus and system for treating ammonia nitrogen-containing waste water
CN101851012A (en) * 2009-03-30 2010-10-06 张波 Technique for MS desulfurization based on ammonia process
CN102139983A (en) * 2011-02-16 2011-08-03 神华集团有限责任公司 Waste water treatment method and system
CN102295378A (en) * 2010-06-28 2011-12-28 中国石油化工股份有限公司 Treatment and recycling method of ammonia nitrogen containing high-salt catalyst wastewater
CN102503016A (en) * 2011-12-19 2012-06-20 杭州浙大合力科技有限公司 Device and method for treating ammonia nitrogen wastewater, recycling ammonia and preparing ammonium sulfate
TWM437845U (en) * 2012-05-29 2012-09-21 Univ Chia Nan Pharm & Sciency Membrane contact system for treating ammonium-nitrogen waste water
CN104591456A (en) * 2013-11-01 2015-05-06 中国石油化工股份有限公司 High salinity ammonia nitrogen wastewater treatment method
CN206538296U (en) * 2016-12-30 2017-10-03 新阳科技集团有限公司 Ammonia-containing water processing unit
CN107352726A (en) * 2017-09-05 2017-11-17 陈雪薇 A kind of MVR ammonia still processs recovery ammonium sulfate processing high ammonia-nitrogen wastewater technology
CN206705881U (en) * 2017-04-17 2017-12-05 杭州开源环保工程有限公司 A kind of ammonia nitrogen waste water processing added with acid solution, is stored and multi-effect evaporation system
CN207391045U (en) * 2017-09-15 2018-05-22 广东闻扬环境科技有限公司 Ammonia-containing water evaporating
CN209537026U (en) * 2019-02-13 2019-10-25 江苏春绿机械制造有限公司 A kind of drop ammonia nitrogen MVR vapo(u)rization system

Patent Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008207118A (en) * 2007-02-27 2008-09-11 Hiroshima Univ Method, apparatus and system for treating ammonia nitrogen-containing waste water
CN101851012A (en) * 2009-03-30 2010-10-06 张波 Technique for MS desulfurization based on ammonia process
CN102295378A (en) * 2010-06-28 2011-12-28 中国石油化工股份有限公司 Treatment and recycling method of ammonia nitrogen containing high-salt catalyst wastewater
CN102139983A (en) * 2011-02-16 2011-08-03 神华集团有限责任公司 Waste water treatment method and system
CN102503016A (en) * 2011-12-19 2012-06-20 杭州浙大合力科技有限公司 Device and method for treating ammonia nitrogen wastewater, recycling ammonia and preparing ammonium sulfate
TWM437845U (en) * 2012-05-29 2012-09-21 Univ Chia Nan Pharm & Sciency Membrane contact system for treating ammonium-nitrogen waste water
CN104591456A (en) * 2013-11-01 2015-05-06 中国石油化工股份有限公司 High salinity ammonia nitrogen wastewater treatment method
CN206538296U (en) * 2016-12-30 2017-10-03 新阳科技集团有限公司 Ammonia-containing water processing unit
CN206705881U (en) * 2017-04-17 2017-12-05 杭州开源环保工程有限公司 A kind of ammonia nitrogen waste water processing added with acid solution, is stored and multi-effect evaporation system
CN107352726A (en) * 2017-09-05 2017-11-17 陈雪薇 A kind of MVR ammonia still processs recovery ammonium sulfate processing high ammonia-nitrogen wastewater technology
CN207391045U (en) * 2017-09-15 2018-05-22 广东闻扬环境科技有限公司 Ammonia-containing water evaporating
CN209537026U (en) * 2019-02-13 2019-10-25 江苏春绿机械制造有限公司 A kind of drop ammonia nitrogen MVR vapo(u)rization system

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
YANG XING等: "Sustainable waste water deammonification by vacuum membrane distillation without pH adjustment: Role of water chemistry", 《CHEMICAL ENGINEERING JOURNAL 》 *
刘乾亮: "膜蒸馏工艺处理高浓度氨氮废水的研究", 《中国博士学位论文全文数据库 工程科技Ⅰ辑》 *

Similar Documents

Publication Publication Date Title
CN207313355U (en) A kind of high ammonia-nitrogen wastewater processing and resource recovery equipment
CN103387306A (en) Garbage leachate processing system and processing technology thereof
CN109319976B (en) Process for treating ammonia nitrogen wastewater by adopting gaseous membrane
CN103599745A (en) Modified calcium silicate and its application in sewage dephosphorization
CN103880232A (en) Treatment system and method for organic salt-containing wastewater
CN103964528A (en) Heat pump rectification steam stripping deamination method
CN104016512B (en) A kind of method utilizing spartina alterniflora loisel's base charcoal Treatment of Copper waste water
CN205501021U (en) A processing system that is used for raffinate waste water of nickel, cobalt and manganese
CN203360209U (en) Treatment system for garbage leachate
CN108218155A (en) A kind of concentrate with high salt divides salt processing method and system
CN104003581A (en) Treatment process of high-concentration degradation-resistant organic wastewater
CN103495399A (en) Preparation method and application of sludge activated carbon
CN202465422U (en) Ammonia nitrogen wastewater recycling treatment equipment
CN108178451B (en) Treatment system for removing ammonia nitrogen in domestic wastewater
CN110372143A (en) A kind of landfill leachate materialization deamination preprocess method and equipment
CN103183431B (en) Ammonia-nitrogen wastewater treatment technology
CN102531105A (en) Process and equipment for recycling ammonia nitrogen waste water
CN103301811A (en) preparation method of biomass charcoal adsorbent and method for treating oily wastewater by biomass charcoal adsorbent
CN109052709A (en) A kind of technique based on evaporation process high ammonia-nitrogen wastewater under acid washing conditions
CN104860465A (en) Double-tower catalysis thermal-coupling reflux deamination method and deamination device thereof
CN204454816U (en) The treatment system of nitrogen-containing wastewater
CN104528989B (en) A kind of high ammonia-nitrogen wastewater processes ammonia recovery system
CN208762185U (en) A kind of energy-saving system suitable for handling desulfurization wastewater
CN104261501A (en) Ammonia nitrogen stripping method of municipal waste leachate
CN104496115A (en) Draft beer plant wastewater treatment method and treatment device

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: 20181221

RJ01 Rejection of invention patent application after publication