CN109336293A - The removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF) - Google Patents

The removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF) Download PDF

Info

Publication number
CN109336293A
CN109336293A CN201811400290.3A CN201811400290A CN109336293A CN 109336293 A CN109336293 A CN 109336293A CN 201811400290 A CN201811400290 A CN 201811400290A CN 109336293 A CN109336293 A CN 109336293A
Authority
CN
China
Prior art keywords
waste water
formaldehyde
removal
water
displacement
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
CN201811400290.3A
Other languages
Chinese (zh)
Inventor
潘晋峰
张诗剑
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.)
FUZHOU YUDENG ENVIRONMENTAL PROTECTION ENGINEERING DESIGN Co Ltd
Original Assignee
FUZHOU YUDENG ENVIRONMENTAL PROTECTION ENGINEERING DESIGN 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 FUZHOU YUDENG ENVIRONMENTAL PROTECTION ENGINEERING DESIGN Co Ltd filed Critical FUZHOU YUDENG ENVIRONMENTAL PROTECTION ENGINEERING DESIGN Co Ltd
Priority to CN201811400290.3A priority Critical patent/CN109336293A/en
Publication of CN109336293A publication Critical patent/CN109336293A/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
    • C02F1/24Treatment of water, waste water, or sewage by flotation
    • 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
    • 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
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/18Nature of the water, waste water, sewage or sludge to be treated from the purification of gaseous effluents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F5/00Softening water; Preventing scale; Adding scale preventatives or scale removers to water, e.g. adding sequestering agents
    • C02F5/02Softening water by precipitation of the hardness

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

The present invention relates to a kind of removal techniques of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF), the present invention is to obtain the waste water for meeting sewage treatment plant's standard by the way that SS removal, water quality and water homogenizing, formaldehyde remove, calcium ion removes, SS is removed again in displacement waste water and Treatment of Sludge step removal displacement formaldehyde in waste water;The formaldehyde removal targeting of present invention process method is strong, and removal efficiency is high, and up to 99.8% or more, and the lime method reaction time is short, operating cost is low.

Description

The removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF)
Technical field
The invention belongs to formaldehyde in waste water removal technology fields, and in particular to a kind of dry tail gas spray of medium density fibre board (MDF) The removal technique of dedusting displacement formaldehyde in waste water.
Background technique
To adapt to the stringenter wood-based panel industry atmosphere pollutants emission standards of country, the production of various regions medium density fibre board (MDF) Enterprise is both needed to carry out upgrading on the basis of existing dry tail gas cyclone dust removal, and the upgrading technique of mainstream is adopted at present It should to ensure that the substances such as salinity, formaldehyde will not be accumulated in circulated sprinkling water with circulated sprinkling dedusting+wet static dedusting technology Technology needs periodically to replace part circulated sprinkling water, and displacement waste water has the following characteristics that coolant-temperature gage is high (at 50 DEG C or so); Organic concentration height (COD is in 10000mg/L or so);Biodegradability is poor (B/C is below 0.3);Coloration is high, and (coloration is at 5000 times Left and right);The features such as concentration of formaldehyde height (formaldehyde is in 1000mg/L or so).High-concentration formaldehyde wastewater is a kind of typical difficult biochemical drop The toxicity organic wastewater of solution, formaldehyde therein can directly be reacted with the intracorporal protein of microorganism, DNA, RNA, to inhibit it Bioactivity, even results in microorganism death, and general biochemical processing process is difficult to adapt to.
The treatment process of the formaldehyde waste water of high concentration, is mainly the following method at present:
First is that oxidizing process.In oxidizing process, what is the most commonly used is by H2O2And Fe2+The Fenton reagent of composition, PARA FORMALDEHYDE PRILLS(91,95) waste water Oxidation processes are carried out, CO is oxidized the formaldehyde into2And H2O so that realize the drop to organic matters such as formaldehyde in waste water in a short time Solution.The chemical agent that oxidizing process uses is more, and operating cost is high and oxidizing process is not high to the removal targeting of formaldehyde in waste water, goes Except efficiency be easy to be influenced by other low molecule organic matters it is not high to the removal efficiency of the organic wastewater containing formaldehyde of complicated component.
Second is that biological treatment.Biological treatment is a kind of pollution processing that index low in cost, recyclable, environmentally friendly is high Method.But since formaldehyde waste water has stronger inhibition or even destructiveness for microorganism, only not by biology itself The processing work of formaldehyde waste water can be competent at.In concrete practice, usually by the degradation function of anaerobic hydrolysis-acidification combination aerobe, It is jointly processed by formaldehyde waste water.Simultaneously, it is necessary to process range be limited to the formaldehyde waste water of low concentration, otherwise the formaldehyde in waste water It will inhibit even to kill aerobe in advance.It in general, is handled by other methods elder generation PARA FORMALDEHYDE PRILLS(91,95) waste water, when When concentration is reduced to safety index, then it is aided with biological treatment, to reach optimal formaldehyde waste water processing effect.
Third is that blow-off method.Blow-off method handles the principle of formaldehyde waste water, is for formaldehyde low boiling point, volatile and soluble easily in water Chemical characteristic, by the Formaldehyde Gasification in formaldehyde waste water, and can be by the formaldehyde gas recycling and reusing of generation.This method, Primarily directed to the higher formaldehyde waste water of concentration, certain recycle can be played the role of.However, this method has quite Big limitation.First is that being unable to the lower formaldehyde waste water of concentration for the treatment of, and after formaldehyde waste water higher for concentration processing simultaneously Decontamination cannot really be played the role of, it is still desirable to which other methods carry out advanced treating to waste water;Second is that it is low in economic efficiency, it blows The energy consumption of de- method is larger, and can similarly be recycled to high-concentration formaldehyde wastewater by other separating technologies, in contrast Blow-off method does not simultaneously have economic and practical.
Summary of the invention
The present invention is directed to prior art problem, provides in a kind of dry tail gas spraying and dedusting displacement waste water of medium density fibre board (MDF) The formaldehyde removal targeting of the removal technique of formaldehyde, present invention process method is strong, and removal efficiency is high, and up to 99.8% or more, and The lime method reaction time is short, and operating cost is low.
To achieve the above object, the technical solution adopted by the present invention is that:
A kind of removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF), the technique includes following Step:
(1) it replaces SS removal in waste water: displacement waste water being pumped into flotation tank by water pump and be added flocculating agent A, removes waste water In SS;
(2) water quality and water homogenizing: flotation tank water outlet gravity flow enters the homogenizing that conditioning tank carries out water quality and water;
(3) formaldehyde removes: the waste water in conditioning tank being continuously pumped into the first formaldehyde resin reactor by water pump, then presses formaldehyde It is that lime mixing is added in 2:1, and adjusting pH value is 12, is warming up to 70-75 DEG C, carries out preliminary with lime quality concentration ratio Resinification reaction;Then gravity flow enters the second formaldehyde resin reactor, is warming up to 80-85 DEG C, under stirring, first again Aldehyde continues that polymerization reaction generation hexose occurs;
(4) calcium ion removes: the water outlet of the second formaldehyde resin reactor removes reactor from calcium ion is flowed into, and sodium carbonate is added, It is thoroughly mixed, then separates sludge with waste water, wherein sodium carbonate amount is consistent with amount of lime;
(5) SS is removed again: calcium ion removes reactor water outlet and removes reactor from SS is flowed into, and first adjusts pH value of waste water with sulfuric acid It to neutrality, then adds suitable aluminium polychloride and anionic polyacrylamide and is stirred, remove and reacted in waste water The suspended impurity of generation, water outlet obtain the waste water for meeting sewage plant influent quality requirement;
(6) Treatment of Sludge: the sludge that above-mentioned flotation tank, calcium ion removal reactor and SS removal reactor generate is discharged into sludge Pond is transported outward after being dehydrated by sludge dewatering equipment desiccation, and the filtrate of generation, which is back in conditioning tank, to be continued with.
Further, flocculating agent A is cationic polyacrylamide, dosage 30-50mg/L in step (1).
Further, homogenizing is completed by air stirring in step (2), and stirring air dosage is 1-2m3/ (m2H).
Further, the first formaldehyde resin reactor and the second formaldehyde resin reactor series operation in step (3), Its heating mode is steam direct heating.
Further, the first formaldehyde resin reactor and when the second formaldehyde resin reactor overall reaction in step (3) Between be 3h.
The present invention has the advantages that formaldehyde resin reactor is using two sets of continuous series fortune in present invention process method Row, compared with conventional intermittent duty, reactor volume is small, low cost and heat loss is few, and steam demand amount is small, operating cost Low, removal formaldehyde is more efficient;Meanwhile formaldehyde resin reactor heating mode uses steam direct heating mode, with other Heating method is compared, and the thermal efficiency is high, and steam demand amount is small, further decreases operating cost and cost;In addition, the present invention is logical The mating calcium ion removal reactor of formaldehyde resin reactor is crossed, Ca remaining in waste water is removed2+, avoid remaining in waste water Ca2+The harm such as fouling blockage is generated to follow-up equipment;Formaldehyde removal targeting of the invention is strong, and removal efficiency is high, up to 99.8% or more.
Detailed description of the invention
Fig. 1 is formaldehyde removal device flow diagram in the embodiment of the present invention.
Specific embodiment
In order to make content of the present invention easily facilitate understanding, the present invention will be further described for following instance, but It is not used to limit the scope of the present invention.
Embodiment 1
A kind of removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF), the technique includes following Step:
(1) it replaces SS removal in waste water: displacement waste water being pumped into flotation tank by water pump and be added flocculating agent A, dosage is 50mg/L removes the SS in waste water;
(2) water quality and water homogenizing: flotation tank water outlet gravity flow enter conditioning tank by air stirring progress water quality and water it is equal Change, stirring air dosage is 2m3/ (m2H);
(3) formaldehyde removes: the waste water in conditioning tank being continuously pumped into the first formaldehyde resin reactor by water pump, then presses formaldehyde It is that lime mixing is added in 2:1, and adjusting pH value is 12, is heated up using steam direct heating mode with lime quality concentration ratio To 70 DEG C, preliminary resinification reaction is carried out;Then gravity flow enters the second formaldehyde resin reactor, is warming up to 85 DEG C again, Under stirring, formaldehyde continues that polymerization reaction generation hexose, the first formaldehyde resin reactor and the second formaldehyde resin occurs Change reactor total reaction time is 3h;
(4) calcium ion removes: the water outlet of the second formaldehyde resin reactor removes reactor from calcium ion is flowed into, and sodium carbonate is added, It is thoroughly mixed, then separates sludge with waste water;
(5) SS is removed again: calcium ion removes reactor water outlet and removes reactor from SS is flowed into, and first adjusts pH value of waste water with sulfuric acid It to neutrality, then adds aluminium polychloride and anionic polyacrylamide and is stirred, remove what reaction in waste water generated Suspended impurity, water outlet obtain the waste water for meeting sewage plant influent quality requirement;
(6) Treatment of Sludge: the sludge that above-mentioned flotation tank, calcium ion removal reactor and SS removal reactor generate is discharged into sludge Pond is transported outward after being dehydrated by sludge dewatering equipment desiccation, and the filtrate of generation, which is back in conditioning tank, to be continued with.
Through detecting, the dry tail gas spraying and dedusting displacement formaldehyde in waste water original concentration of medium density fibre board (MDF) in 1500mg/L, Concentration of formaldehyde is in 3.0mg/L after the present invention removes process.
Embodiment 2
A kind of removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF), the technique includes following Step:
(1) it replaces SS removal in waste water: displacement waste water being pumped into flotation tank by water pump and be added flocculating agent A, dosage is 30mg/L removes the SS in waste water;
(2) water quality and water homogenizing: flotation tank water outlet gravity flow enter conditioning tank by air stirring progress water quality and water it is equal Change, stirring air dosage is 1.5m3/ (m2H);
(3) formaldehyde removes: the waste water in conditioning tank being continuously pumped into the first formaldehyde resin reactor by water pump, then presses formaldehyde It is that lime mixing is added in 2:1, and adjusting pH value is 12, is heated up using steam direct heating mode with lime quality concentration ratio To 75 DEG C, preliminary resinification reaction is carried out;Then gravity flow enters the second formaldehyde resin reactor, is warming up to 80 DEG C again, Under stirring, formaldehyde continues that polymerization reaction generation hexose, the first formaldehyde resin reactor and the second formaldehyde resin occurs Change reactor total reaction time is 3h;
(4) calcium ion removes: the water outlet of the second formaldehyde resin reactor removes reactor from calcium ion is flowed into, and sodium carbonate is added, It is thoroughly mixed, then separates sludge with waste water;
(5) SS is removed again: calcium ion removes reactor water outlet and removes reactor from SS is flowed into, and first adjusts pH value of waste water with sulfuric acid It to neutrality, then adds aluminium polychloride and anionic polyacrylamide and is stirred, remove what reaction in waste water generated Suspended impurity, water outlet obtain the waste water for meeting sewage plant influent quality requirement;
(6) Treatment of Sludge: the sludge that above-mentioned flotation tank, calcium ion removal reactor and SS removal reactor generate is discharged into sludge Pond is transported outward after being dehydrated by sludge dewatering equipment desiccation, and the filtrate of generation, which is back in conditioning tank, to be continued with.
Through detecting, the dry tail gas spraying and dedusting displacement formaldehyde in waste water original concentration of medium density fibre board (MDF) in 1500mg/L, Concentration of formaldehyde is in 2.0mg/L after the present invention removes process.
The foregoing is merely presently preferred embodiments of the present invention, all equivalent changes done according to scope of the present invention patent with Modification, is all covered by the present invention.

Claims (5)

1. a kind of removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF), it is characterised in that: institute State technique the following steps are included:
(1) it replaces SS removal in waste water: displacement waste water being pumped into flotation tank by water pump and be added flocculating agent A, removes waste water In SS;
(2) water quality and water homogenizing: flotation tank water outlet gravity flow enters the homogenizing that conditioning tank carries out water quality and water;
(3) formaldehyde removes: the waste water in conditioning tank being continuously pumped into the first formaldehyde resin reactor by water pump, then presses formaldehyde It is that lime mixing is added in 2:1, and adjusting pH value is 12, is warming up to 70-75 DEG C, carries out preliminary with lime quality concentration ratio Resinification reaction;Then gravity flow enters the second formaldehyde resin reactor, is warming up to 80-85 DEG C, under stirring, first again Aldehyde continues that polymerization reaction generation hexose occurs;
(4) calcium ion removes: the water outlet of the second formaldehyde resin reactor removes reactor from calcium ion is flowed into, and sodium carbonate is added, It is thoroughly mixed, then separates sludge with waste water;
(5) SS is removed again: calcium ion removes reactor water outlet and removes reactor from SS is flowed into, and first adjusts pH value of waste water with sulfuric acid It to neutrality, then adds suitable aluminium polychloride and anionic polyacrylamide and is stirred, remove and reacted in waste water The suspended impurity of generation, water outlet obtain the waste water for meeting sewage plant influent quality requirement;
(6) Treatment of Sludge: the sludge that above-mentioned flotation tank, calcium ion removal reactor and SS removal reactor generate is discharged into sludge Pond is transported outward after being dehydrated by sludge dewatering equipment desiccation, and the filtrate of generation, which is back in conditioning tank, to be continued with.
2. a kind of removal of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF) according to claim 1 Technique, it is characterised in that: flocculating agent A is cationic polyacrylamide, dosage 30-50mg/L in step (1).
3. a kind of removal of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF) according to claim 1 Technique, it is characterised in that: homogenizing is completed by air stirring in step (2), and stirring air dosage is 1-2m3/ (m2H).
4. a kind of removal of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF) according to claim 1 Technique, it is characterised in that: the first formaldehyde resin reactor and the second formaldehyde resin reactor series operation in step (3), Its heating mode is steam direct heating.
5. a kind of removal of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF) according to claim 1 Technique, it is characterised in that: the first formaldehyde resin reactor and the second formaldehyde resin reactor total reaction time in step (3) For 3h.
CN201811400290.3A 2018-11-22 2018-11-22 The removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF) Pending CN109336293A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811400290.3A CN109336293A (en) 2018-11-22 2018-11-22 The removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811400290.3A CN109336293A (en) 2018-11-22 2018-11-22 The removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF)

Publications (1)

Publication Number Publication Date
CN109336293A true CN109336293A (en) 2019-02-15

Family

ID=65317189

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811400290.3A Pending CN109336293A (en) 2018-11-22 2018-11-22 The removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF)

Country Status (1)

Country Link
CN (1) CN109336293A (en)

Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1985003927A1 (en) * 1984-03-07 1985-09-12 "Licencia" Találmányokat Ertékesito^" És Innováció Process for dewatering municipal and other sewage sludges
CN101070254A (en) * 2007-07-05 2007-11-14 济南圣泉集团股份有限公司 Method for producing organic fertilizer using formaldehyde waste water to ferment
CN101613170A (en) * 2009-07-17 2009-12-30 江南大学 A kind of method of handling high-concentration formaldehyde wastewater
CN201520689U (en) * 2009-09-28 2010-07-07 上海中耀环保实业有限公司 Reactor for removing formaldehyde in waste water
CN105060553A (en) * 2015-07-18 2015-11-18 重庆医科大学 Formaldehyde wastewater treatment method
CN105481183A (en) * 2015-12-29 2016-04-13 北京蓝图工程设计有限公司 Formaldehyde sewage treatment technology
CN105565590A (en) * 2015-12-14 2016-05-11 潘敏 Advanced treatment system of high-concentration methanol wastewater by DAT-IAT (demand aeration tank-intermittent aeration tank) technique
CN105800863A (en) * 2014-12-31 2016-07-27 北京清大国华环境股份有限公司 High concentration formaldehyde wastewater treatment method and apparatus thereof
US20170335204A1 (en) * 2016-05-19 2017-11-23 Ecolab Usa Inc. Heavy amines as hydrogen sulfide and mercaptan scavengers
CN107628725A (en) * 2016-07-18 2018-01-26 中南大学 The processing method of ultra-high concentration organic wastewater in a kind of processing for blueberry preserved fruits
CN108349732A (en) * 2015-10-09 2018-07-31 沙特基础工业全球技术公司 Hydrogen and calcium carbonate are prepared by formaldehyde
CN108585380A (en) * 2018-06-07 2018-09-28 安徽德玉环境工程装备有限公司 A kind of process of brush wastewater treatment processed

Patent Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1985003927A1 (en) * 1984-03-07 1985-09-12 "Licencia" Találmányokat Ertékesito^" És Innováció Process for dewatering municipal and other sewage sludges
CN101070254A (en) * 2007-07-05 2007-11-14 济南圣泉集团股份有限公司 Method for producing organic fertilizer using formaldehyde waste water to ferment
CN101613170A (en) * 2009-07-17 2009-12-30 江南大学 A kind of method of handling high-concentration formaldehyde wastewater
CN201520689U (en) * 2009-09-28 2010-07-07 上海中耀环保实业有限公司 Reactor for removing formaldehyde in waste water
CN105800863A (en) * 2014-12-31 2016-07-27 北京清大国华环境股份有限公司 High concentration formaldehyde wastewater treatment method and apparatus thereof
CN105060553A (en) * 2015-07-18 2015-11-18 重庆医科大学 Formaldehyde wastewater treatment method
CN108349732A (en) * 2015-10-09 2018-07-31 沙特基础工业全球技术公司 Hydrogen and calcium carbonate are prepared by formaldehyde
CN105565590A (en) * 2015-12-14 2016-05-11 潘敏 Advanced treatment system of high-concentration methanol wastewater by DAT-IAT (demand aeration tank-intermittent aeration tank) technique
CN105481183A (en) * 2015-12-29 2016-04-13 北京蓝图工程设计有限公司 Formaldehyde sewage treatment technology
US20170335204A1 (en) * 2016-05-19 2017-11-23 Ecolab Usa Inc. Heavy amines as hydrogen sulfide and mercaptan scavengers
CN107628725A (en) * 2016-07-18 2018-01-26 中南大学 The processing method of ultra-high concentration organic wastewater in a kind of processing for blueberry preserved fruits
CN108585380A (en) * 2018-06-07 2018-09-28 安徽德玉环境工程装备有限公司 A kind of process of brush wastewater treatment processed

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
徐秀梅: "《高分子化学与物理学习指导》", 30 June 2007 *
王志海: "石灰法处理甲醛废水的试验研究", 《给排水》 *
环境保护部环境工程评估中心: "《环境影响评价技术方法》", 28 February 2017 *
许鹏飞: "化工企业中的甲醛废水的处理方法", 《中国化工贸易》 *
陈鸿彬: "《高纯试剂提纯与制备》", 31 May 1983 *

Similar Documents

Publication Publication Date Title
CN109851162B (en) Oil and gas field salt-containing wastewater standard treatment process
CN102452770A (en) Biochemical treatment/advanced oxidation treatment coupled sewage treatment technique
CN106830536A (en) A kind of advanced treatment process of ferment antibiotics waste water
CN104843934A (en) Treatment method of antibiotic production wastewater
CN105130088B (en) The processing method of ozone Oxidation Treatment percolate nanofiltration concentrate
CN109851025A (en) A kind of device and method of ozone/hydrogen peroxide solution advanced oxidation indegradable industrial effluent
CN108033630A (en) A kind of esterified waste water treatment process
CN204569599U (en) A kind of novel no pollution sewage effluent total system
CN105233838B (en) A kind of O using activated bentonite as carrier3/H2O2Preparation method, catalyst and its application of catalyst
CN101767859A (en) Waste water treatment method combining Fenton oxidization and microwave catalysis phase
CN103011506A (en) Treatment method of xylose production wastewater
CN100402441C (en) Method for treating sewage by catalytic iron internal electrogravimetry and its filler
CN103951107B (en) A kind of device and method of Treatment of Wastewater in Coking
CN106495359A (en) A kind of highly difficult advanced waste treatment apparatus and method
CN103435222B (en) Method for treating flourescent brightener wastewater with phosphorus
CN110862182A (en) Landfill leachate treatment device and method
CN102874974A (en) Advanced treatment and comprehensive utilization process for sewage and sludge in sewage treatment plant
CN205442755U (en) A fragrant iron ion follows device that ring method handled organic waste water
CN102976520A (en) High-concentration ammonia-nitrogen wastewater treatment process
CN105293839B (en) A kind of processing method of fluorescent brightener CBS waste water low boiler cut
CN109574386A (en) A kind for the treatment of of Perfume Wastewater processing system
CN107857444A (en) A kind of environment protection method for handling dyeing waste water
CN107540161A (en) High pure and ultra-fine modified calcium carbonate produces the processing method and processing system of waste water
CN209583892U (en) A kind for the treatment of of Perfume Wastewater processing system
CN109336293A (en) The removal technique of the dry tail gas spraying and dedusting displacement formaldehyde in waste water of medium density fibre board (MDF)

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: 20190215

RJ01 Rejection of invention patent application after publication