CN104909425B - Method used for treating high concentration ammonia nitrogen in metallurgical waste water - Google Patents

Method used for treating high concentration ammonia nitrogen in metallurgical waste water Download PDF

Info

Publication number
CN104909425B
CN104909425B CN201510272156.XA CN201510272156A CN104909425B CN 104909425 B CN104909425 B CN 104909425B CN 201510272156 A CN201510272156 A CN 201510272156A CN 104909425 B CN104909425 B CN 104909425B
Authority
CN
China
Prior art keywords
waste water
ammonia nitrogen
iron
high concentration
organic composite
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.)
Expired - Fee Related
Application number
CN201510272156.XA
Other languages
Chinese (zh)
Other versions
CN104909425A (en
Inventor
雷春生
盛艳花
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.)
Changzhou University
Original Assignee
Changzhou University
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 Changzhou University filed Critical Changzhou University
Priority to CN201510272156.XA priority Critical patent/CN104909425B/en
Publication of CN104909425A publication Critical patent/CN104909425A/en
Application granted granted Critical
Publication of CN104909425B publication Critical patent/CN104909425B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Treatment Of Water By Ion Exchange (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

The invention discloses a method used for treating high concentration ammonia nitrogen in metallurgical waste water, and belongs to the field of metallurgical waste water treatment. According to the method, an organic composite denitrification agent modified magnesium aluminum iron hydrotalcite magnetic nano adsorptive material is prepared via magnetization, modification, drying, and activation, and then adsorption rods are prepared and are arranged in an adsorption tower to treat high concentration ammonia nitrogen in metallurgical waste water. In removing processes, high concentration ammonia nitrogen in waste water is absorbed, after saturation, aging of the surface layer of the adsorption material is realized, and updating of the adsorption material is realized under the action of an applied magnetic field and flow scour, and regeneration is not needed. After shedding, an obtained residue is waterless, and is small in volume; no ammonia gas is generated or released into the atmosphere; no precipitate is obtained; and no environmental secondary pollution is caused. Separation can be realized under the action of the applied magnetic field; ammonia nitrogen concentration is reduce to 0.45mg/L from 2000-6000mg/L; ammonia nitrogen removing ratio is higher than 99.99%; and the method can be used for treating waste water with high concentration ammonia nitrogen, and possesses a promising prospect.

Description

A kind of method of Metallurgical Waste Water middle and high concentration ammonia nitrogen
Technical field
The present invention relates to a kind of method of ammonia nitrogen in high density, especially metallurgy waste water treatment technical field.
Background technology
Metallurgical industry is one of the most ancient industry in human history, and after the Industrial Revolution of 18th century, steel and iron industry is sent out rapidly Exhibition causes serious pollution, and after entering for 20th century, metallurgical production scale increases rapidly, and the content of high-concentration ammonia nitrogen in waste water is not yet Break and increase;At present, the method removing ammonia nitrogen in waste water is a lot, and such as ion exchange method is to nh4 +Ion has very strong selectivity Zeolite as exchanger resin, thus reaching the purpose removing ammonia nitrogen, although this method process is simple, reduced investment clearance Height, but it is only applicable to the ammonia nitrogen waste water of middle low concentration, the ammonia nitrogen waste water for high concentration frequently can cause to grasp because of resin regeneration Make difficult;Break point chlorination is also had to be that chlorine or sodium hypochlorite are passed through the change that the nh3-n in waste water is oxidized in waste water n2 Learn denitrification process, stable using relatively inexpensive, treatment effect, it is not subject to Water Temperature, but investment is less, operating cost is high, by-product Thing chloramines and chlorinated organics can cause secondary pollution, be only applicable to process Low Concentration Ammonia Containing Wastewater;Also such as Publication No. Cn102060399a, entitled " organic composite denitrifier process high-concentration ammonia nitrogenous wastewater except ammonia nitrogen device ", this patent is passed through Add organic Composite denitrification agent and remove high-concentration ammonia nitrogen in waste water although present invention operation is easy and simple to handle, for ammonia nitrogen in high density The nitric efficiency of waste water is high, but the present invention is to combine with blow-off method, there is ammonia emission and cause in wastewater treatment process Secondary pollution;So a kind of process skill that can accomplish process ammonia nitrogen in high density that is efficient, economic, stable, not producing secondary pollution Art is the direction of Future Development.
Content of the invention
Present invention mainly solves technical problem: for current organic composite denitrifier combine blow-off method in ammonia nitrogen in high density There is ammonia emission in wastewater treatment process, cause secondary environmental pollution problem, there is provided a kind of organic composite denitrifier is modified Magnesium-aluminum-iron hydrotalcite nano magnetic adsorptive material, the aging adsorbing material top layer of energy after absorption high-concentration ammonia nitrogen in waste water, and saturation, Under externally-applied magnetic field and current scour act on, realize the renewal of adsorbing material, need not regenerate;Save energy consumption, reduce cost, High-concentration ammonia nitrogen in waste water can efficiently be removed.
For solving above-mentioned technical problem, the present invention adopts technical scheme as described below: organic composite denitrifier modification magnesium Ferro-aluminum brucite magnetic nano adsorption material preparation process is:
(1) magnesium-aluminum-iron brucite preparation: weigh 4.8~10.3g magnesium nitrate, 4.2~7.5g aluminum nitrate respectively, 5.5~ 13.9g ferric nitrate is dissolved in the ethanol solution that 220~380ml contains 3.6~7.2g carbamide, stirs 1h, under room temperature Enter to be heated to 140 DEG C in hydrothermal reaction kettle, react 13~15h, be cooled to room temperature, cleaned with ethanol and deionized water after three times 6h is dried at 60 DEG C, obtains nano magnalium molten iron Talcum;
(2) magnetize: by the nano magnalium molten iron Talcum of above-mentioned preparation be 36.5% with mass concentration successively concentrated hydrochloric acid and Saturation potassium hydroxide solution soaks 8h, is placed in Muffle furnace, dries at temperature is 105 DEG C, near magnetic field magnetization;
(3) modified: the nano magnalium molten iron talc materials after pickling, alkali leaching and magnetization to be immersed 10~40g organic multiple Close in denitrifier, stir 25~65min;
(4) dry: modified nano magnalium molten iron talc materials deionized water is cleaned 3 times, in nitrogen ceiling Dry under part;
(5) activate: at temperature is 800 DEG C~900 DEG C, calcine 4~6h, you can.
Described organic composite denitrifier is: oxaloacetic acid, potassium oxalate, three kinds of octadecyl acrylate, by quality ratio: 10%~30% oxaloacetic acid, 20%~45% potassium oxalate, 15%~70% octadecyl acrylate.
A kind of concrete application method processing Metallurgical Waste Water middle and high concentration ammonia nitrogen:
(1) by the organic composite preparing denitrifier modification magnesium-aluminum-iron brucite magnetic nano adsorption material and adhesive 5:1 is made into viscous fluid in mass ratio, and by viscous fluid uniformly in plastic hollow microsphere top layer, coating layer thickness is 4~7cm;
(2) the plastic hollow microsphere of coated viscous fluid is dried after 9~17min under ventilation state, is placed in adsorption tower, Every layer of setting height(from bottom) is 15~60cm, and space height is 40~85cm, allows the metallurgy that ammonia nitrogen concentration is 2000~6000mg/l to give up Water flows through in adsorption tower, flow speed control 7~18m3/ h, stops 25~60min in adsorption tower, and organic composite denitrifier adsorbs not Break and tend to saturation, magnesium-aluminum-iron brucite magnetic nano adsorption material top layer is constantly aging;
(3) Metallurgical Waste Water current wash away with externally-applied magnetic field in the presence of, aging adsorbing material top layer comes off layer by layer;
(4) finally measure ammonia-nitrogen content in water outlet waste water.
Described adhesive proportioning by weight is: 35 parts of glycerol, 15 parts of Polyethylene Glycol, 30 parts of citric acids and 20 parts Boric acid.
The principle of the present invention: magnesium-aluminum-iron hydrotalcite material has specific surface area greatly, belongs to mesoporous material material, through organic multiple Close denitrifier modified to ammonia nitrogen in waste water, there is absorption property it is often more important that, the addition of organic composite denitrifier, can make Obtain after adsorbing material absorption ammonia nitrogen reaches saturation and can voluntarily come off layer by layer, realize the renewal on adsorbing material surface, again adsorb useless Ammonia nitrogen in high density in water, and the residue after coming off separates in current scour and externally-applied magnetic field effect.
Compared with additive method, Advantageous Effects are the present invention:
(1) in the organic composite denitrifier modification magnesium-aluminum-iron brucite magnetic nano adsorption material absorption waste water preparing The aging adsorbing material top layer of energy after ammonia nitrogen in high density, and saturation, under externally-applied magnetic field and current scour act on, realizes adsorbing material Renewal, need not regenerate;
(2) residue no moisture, small volume after coming off, separable under externally-applied magnetic field, adsorbing material need not regenerate, and removes Rate is high, low cost;
(3) it is directed to Metallurgical Waste Water water quality situation, that has selected that oxaloacetic acid, potassium oxalate, octadecyl acrylate make is organic Composite denitrification agent, its addition enables to voluntarily come off layer by layer after adsorbing material absorption ammonia nitrogen reaches saturation, with strong points;
(4) also no precipitation generates, is not result in secondary environmental pollution will not to produce ammonia entrance air.
Embodiment
Organic composite denitrifier modification magnesium-aluminum-iron brucite magnetic nano adsorption material preparation of the present invention: weigh respectively first 4.8~10.3g magnesium nitrate, 4.2~7.5g aluminum nitrate, 5.5~13.9g ferric nitrate be dissolved in 220~380ml contain 3.6~ In the ethanol solution of 7.2g carbamide, under room temperature stir 1h, pour into and in hydrothermal reaction kettle, be heated to 140 DEG C, reaction 13~ 15h, is cooled to room temperature, is cleaned with ethanol and deionized water after three times and 6h is dried at 60 DEG C, obtains nano magnalium molten iron Talcum; By the nano magnalium molten iron Talcum of above-mentioned preparation be 36.5% with mass concentration successively concentrated hydrochloric acid and saturation potassium hydroxide solution Soak 8h, be placed in Muffle furnace, dry at temperature is 105 DEG C, near magnetic field magnetization;By after pickling, alkali leaching and magnetization In nano magnalium molten iron talc materials immersion 10~40g organic composite denitrifier, stir 25~65min;By modified nanometer Magnesium-aluminum-iron hydrotalcite material deionized water is cleaned 3 times, dries under nitrogen protective condition;At temperature is 800 DEG C~900 DEG C Calcining 4~6h, you can.
Described organic composite denitrifier is: oxaloacetic acid, potassium oxalate, three kinds of octadecyl acrylate, by quality ratio: 10%~30% oxaloacetic acid, 20%~45% potassium oxalate, 15%~70% octadecyl acrylate;
A kind of concrete application method processing Metallurgical Waste Water middle and high concentration ammonia nitrogen: first the organic composite preparing is taken off Nitrogen agent modification magnesium-aluminum-iron brucite magnetic nano adsorption material is made into viscous fluid, by viscous fluid with adhesive 5:1 in mass ratio In plastic hollow microsphere top layer, thickness degree is 4~7cm;By the tiny balloon of coated viscous fluid under ventilation state be dried 9~ After 17min, it is placed in adsorption tower, every layer of setting height(from bottom) is 15~60cm, space height is 40~85cm, allow the ammonia nitrogen concentration be The Metallurgical Waste Water of 2000~6000mg/l flows through in adsorption tower, flow speed control 7~18m3/ h, in adsorption tower stop 25~ 60min, the absorption of organic composite denitrifier constantly tends to saturation, and magnesium-aluminum-iron brucite magnetic nano adsorption material top layer is constantly old Change;Metallurgical Waste Water current wash away with externally-applied magnetic field in the presence of, aging adsorbing material top layer comes off layer by layer;Finally measure Ammonia-nitrogen content in water outlet waste water.
Described adhesive proportioning by weight is: 35 parts of glycerol, 15 parts of Polyethylene Glycol, 30 parts of citric acids and 20 parts Boric acid.
Example 1
Weigh 4.8g magnesium nitrate, 4.2g aluminum nitrate first respectively, 5.5g ferric nitrate is dissolved in 220ml and contains 3.6g carbamide In ethanol solution, stir 1h under room temperature, pour into and in hydrothermal reaction kettle, be heated to 140 DEG C, react 13h, be cooled to room temperature, use Ethanol and deionized water are dried 6h after cleaning three times at 60 DEG C, obtain nano magnalium molten iron Talcum;Nanometer by above-mentioned preparation The concentrated hydrochloric acid that magnesium-aluminum-iron brucite is 36.5% with mass concentration successively and saturation potassium hydroxide solution soak 8h, are placed in Muffle furnace In, dry at temperature is 105 DEG C, near magnetic field magnetization;By the nano magnalium molten iron Talcum material after pickling, alkali leaching and magnetization In material immersion 1g oxaloacetic acid, 2g potassium oxalate and 7g octadecyl acrylate, stir 25min;By modified nano magnalium molten iron Talc materials deionized water is cleaned 3 times, dries under nitrogen protective condition;Calcine 4h at temperature is 800 DEG C;To be prepared into To organic composite denitrifier modification magnesium-aluminum-iron brucite magnetic nano adsorption material and adhesive 5:1 in mass ratio be made into sticky Liquid, by viscous fluid in tiny balloon top layer, coating layer thickness is 4cm;By the tiny balloon of coated viscous fluid under ventilation state After 9min is dried, it is placed in adsorption tower, every layer of tiny balloon setting height(from bottom) is 15cm, space height is 40cm, allow ammonia nitrogen concentration Metallurgical Waste Water for 2000mg/l flows through in adsorption tower, flow speed control 7m3/ h, stops 25min in adsorption tower, and organic composite takes off Nitrogen agent absorption constantly tends to saturation, and magnesium-aluminum-iron brucite magnetic nano adsorption material top layer is constantly aging;In Metallurgical Waste Water current Wash away with externally-applied magnetic field in the presence of, aging adsorbing material top layer comes off layer by layer;Finally measure ammonia nitrogen in water outlet waste water to contain Amount is reduced to 0.15mg/l from 2000mg/l, and clearance reaches more than 99.99%.
Example 2
Weigh 8.1g magnesium nitrate, 5.8g aluminum nitrate first respectively, 9.7g ferric nitrate is dissolved in 310ml and contains 5.3g carbamide In ethanol solution, stir 1h under room temperature, pour into and in hydrothermal reaction kettle, be heated to 140 DEG C, react 14h, be cooled to room temperature, use Ethanol and deionized water are dried 6h after cleaning three times at 60 DEG C, obtain nano magnalium molten iron Talcum;Nanometer by above-mentioned preparation The concentrated hydrochloric acid that magnesium-aluminum-iron brucite is 36.5% with mass concentration successively and saturation potassium hydroxide solution soak 8h, are placed in Muffle furnace In, dry at temperature is 105 DEG C, near magnetic field magnetization;By the nano magnalium molten iron Talcum material after pickling, alkali leaching and magnetization In material immersion 6g oxaloacetic acid, 8g potassium oxalate and 6g octadecyl acrylate, stir 40min;By modified nano magnalium molten iron Talc materials deionized water is cleaned 3 times, dries under nitrogen protective condition;Calcine 5h at temperature is 850 DEG C;To be prepared into To organic composite denitrifier modification magnesium-aluminum-iron brucite magnetic nano adsorption material and adhesive 5:1 in mass ratio be made into sticky Liquid, by viscous fluid in tiny balloon top layer, coating layer thickness is 6cm;By the tiny balloon of coated viscous fluid under ventilation state After 12min is dried, it is placed in adsorption tower, every layer of tiny balloon setting height(from bottom) is 40cm, space height is 60cm, allow ammonia nitrogen concentration Metallurgical Waste Water for 4000mg/l flows through in adsorption tower, flow speed control 12m3/ h, stops 45min, organic composite in adsorption tower Denitrifier absorption constantly tends to saturation, and magnesium-aluminum-iron brucite magnetic nano adsorption material top layer is constantly aging;In Metallurgical Waste Water water Stream wash away with externally-applied magnetic field in the presence of, aging adsorbing material top layer comes off layer by layer;Finally measure ammonia nitrogen in water outlet waste water Content is reduced to 0.25mg/l from 4000mg/l, and clearance reaches more than 99.99%.
Example 3
Weigh 10.3g magnesium nitrate, 7.5g aluminum nitrate first respectively, 13.9g ferric nitrate is dissolved in 380ml and contains 7.2g carbamide Ethanol solution in, under room temperature stir 1h, pour into and in hydrothermal reaction kettle, be heated to 140 DEG C, react 15h, be cooled to room temperature, Cleaned with ethanol and deionized water after three times and 6h is dried at 60 DEG C, obtain nano magnalium molten iron Talcum;By receiving of above-mentioned preparation The concentrated hydrochloric acid that rice magnesium-aluminum-iron brucite is 36.5% with mass concentration successively and saturation potassium hydroxide solution soak 8h, are placed in Muffle In stove, dry at temperature is 105 DEG C, near magnetic field magnetization;By the nano magnalium molten iron Talcum after pickling, alkali leaching and magnetization In material immersion 12g oxaloacetic acid, 8g potassium oxalate and 20g octadecyl acrylate, stir 65min;By modified nano magnalium Molten iron talc materials deionized water is cleaned 3 times, dries under nitrogen protective condition;Calcine 6h at temperature is 900 DEG C;To make The standby organic composite denitrifier modification magnesium-aluminum-iron brucite magnetic nano adsorption material obtaining is made into adhesive 5:1 in mass ratio Viscous fluid, by viscous fluid in tiny balloon top layer, coating layer thickness is 7cm;By the tiny balloon of coated viscous fluid in ventilation shape After 17min being dried under state, it is placed in adsorption tower, every layer of tiny balloon setting height(from bottom) is 60cm, space height is 85cm, allow ammonia nitrogen Concentration is that the Metallurgical Waste Water of 6000mg/l flows through in adsorption tower, flow speed control 18m3/ h, stops 60min in adsorption tower, organic Composite denitrification agent absorption constantly tends to saturation, and magnesium-aluminum-iron brucite magnetic nano adsorption material top layer is constantly aging;Metallurgical useless Water current wash away with externally-applied magnetic field in the presence of, aging adsorbing material top layer comes off layer by layer;Finally measure in water outlet waste water Ammonia-nitrogen content is reduced to 0.45mg/l from 6000mg/l, and clearance reaches more than 99.99%.

Claims (1)

1. a kind of process Metallurgical Waste Water middle and high concentration ammonia nitrogen method it is characterised in that:
(1) magnesium-aluminum-iron brucite preparation: weigh 4.8~10.3g magnesium nitrate, 4.2~7.5g aluminum nitrate, 5.5~13.9g nitre respectively Sour dissolved ferric iron contains in the ethanol solution of 3.6~7.2g carbamide in 220~380ml, stirs 1h, pour hydro-thermal into anti-under room temperature Answer and in kettle, be heated to 140 DEG C, react 13~15h, be cooled to room temperature, cleaned with ethanol and deionized water dry at 60 DEG C after three times Dry 6h, obtains nano magnalium molten iron Talcum;
(2) magnetize: by the nano magnalium molten iron Talcum of above-mentioned preparation be 36.5% with mass concentration successively concentrated hydrochloric acid and saturation Potassium hydroxide solution soaks 8h, is placed in Muffle furnace, dries at temperature is 105 DEG C, near magnetic field magnetization;
(3) modified: the nano magnalium molten iron talc materials immersion 10~40g organic composite after pickling, alkali leaching and magnetization is taken off In nitrogen agent, stir 25~65min;Described organic composite denitrifier is: oxaloacetic acid, potassium oxalate, three kinds of octadecyl acrylate, By quality ratio: 10%~30% oxaloacetic acid, 20%~45% potassium oxalate, 15%~70% octadecyl acrylate;
(4) dry: modified nano magnalium molten iron talc materials deionized water is cleaned 3 times, under nitrogen protective condition Dry;
(5) activate: at temperature is 800 DEG C~900 DEG C, calcine 4~6h, you can;
(6) by the organic composite preparing denitrifier modification magnesium-aluminum-iron brucite magnetic nano adsorption material and adhesive by matter Amount is made into viscous fluid than 5:1, and by viscous fluid uniformly in plastic hollow microsphere top layer, coating layer thickness is 4~7cm;Described glue Stick proportioning by weight is: 35 parts of glycerol, 15 parts of Polyethylene Glycol, 30 parts of citric acids and 20 parts of boric acid;
(7) the plastic hollow microsphere of coated viscous fluid is dried after 9~17min under ventilation state, is placed in adsorption tower, every layer Setting height(from bottom) is 15~60cm, and space height is 40~85cm, allows the Metallurgical Waste Water stream that ammonia nitrogen concentration is 2000~6000mg/l Through in adsorption tower, flow speed control 7~18m3/ h, stops 25~60min in adsorption tower, and the absorption of organic composite denitrifier constantly becomes In saturation, magnesium-aluminum-iron brucite magnetic nano adsorption material top layer is constantly aging;
(8) Metallurgical Waste Water current wash away with externally-applied magnetic field in the presence of, aging adsorbing material top layer comes off layer by layer;
(9) finally measure ammonia-nitrogen content in water outlet waste water.
CN201510272156.XA 2015-05-25 2015-05-25 Method used for treating high concentration ammonia nitrogen in metallurgical waste water Expired - Fee Related CN104909425B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510272156.XA CN104909425B (en) 2015-05-25 2015-05-25 Method used for treating high concentration ammonia nitrogen in metallurgical waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510272156.XA CN104909425B (en) 2015-05-25 2015-05-25 Method used for treating high concentration ammonia nitrogen in metallurgical waste water

Publications (2)

Publication Number Publication Date
CN104909425A CN104909425A (en) 2015-09-16
CN104909425B true CN104909425B (en) 2017-01-25

Family

ID=54078937

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510272156.XA Expired - Fee Related CN104909425B (en) 2015-05-25 2015-05-25 Method used for treating high concentration ammonia nitrogen in metallurgical waste water

Country Status (1)

Country Link
CN (1) CN104909425B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107938412A (en) * 2017-11-21 2018-04-20 常州思宇环保材料科技有限公司 A kind of efficiently Winestock machine and its application process
CN111644147A (en) * 2019-11-04 2020-09-11 南京工业大学 Zeolite for adsorbing ammonia nitrogen in wastewater

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006075815A (en) * 2004-09-13 2006-03-23 Shimane Univ Molding for denitrifying/dephosphorizing and method for denitrifying/dephosphorizing sewage or waste water
CN102060399B (en) * 2010-11-30 2012-12-26 常州大学 Ammonia nitrogen removing device assisting organic compound denitrifier in treating high concentration ammonia nitrogen wastewater
CN104261547B (en) * 2014-10-10 2016-03-02 武汉工程大学 Hydrotalcite magnetite compound material for water treatment

Also Published As

Publication number Publication date
CN104909425A (en) 2015-09-16

Similar Documents

Publication Publication Date Title
CN101538652B (en) Method for separating and recovering vanadium and chrome from vanadium and chrome-containing waste
CN101780421B (en) Ammonia nitrogen adsorbent and preparation method and application method thereof
CN106669361A (en) Method for production of sulfuric acid by flue gas desulfurization and for sulfuric acid purification and device thereof
CN104909425B (en) Method used for treating high concentration ammonia nitrogen in metallurgical waste water
RU2018140500A (en) SULPHATE REMOVAL FROM ANION EXCHANGE RESIN SOLVENTS
CN106422680B (en) Smelting flue gas purification treatment device and method with byproduct sulfuric acid of more than 40%
CN101857282A (en) Method for selectively absorbing and separating thiocyanates and thiosulfates in water solution
CN108147373A (en) A kind of method that flue gas during smelting prepares sulfuric acid
CN107840402A (en) A kind of adsorbent for being used to adsorb heavy metal
CN104474662B (en) Preparation method of stabilizer for treating arsenic-containing waste residue
CN110124510A (en) A method of utilizing oxygen-enriched side-blowing smelting lead extracting sulfuric acid
CN106854167B (en) A method of producing petroleum sulfonate
CN109467239A (en) A kind of method of iron and steel pickling waste liquid recovery acid
CN104876295A (en) Method for treating high-concentration ammonia and nitrogen in chemical industry waste water
CN104944497B (en) Method for treating high-concentration ammonia nitrogen in coal chemical industry wastewater
CN104907047A (en) Method used for treating highly concentrated ammonia-nitrogen in rare earth waste water
CN107118820A (en) A kind of coal arsenic removing method and its additive
CN104925890B (en) A kind of Refinery Wastewater middle and high concentration ammonia nitrogen method
Barloková et al. Modified clinoptilolite in the removal of iron and manganese from water
CN103769061A (en) Synthetic method of collagen hyperbranched polyester/metallic ion loaded fluoride adsorbent
JPH0256958B2 (en)
CN1238269C (en) Technological Method of producing toxic heaving metal waste water treatment agent
CN104785204A (en) Liquid-modified composite mercury remover for molecular sieves and preparation method of liquid-modified composite mercury remover
CN104876292A (en) Method for treating high-concentration ammonia nitrogen in urea
CN105601015B (en) A kind of Zero discharge treatment method of steel pickling waste liquor

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20170125

Termination date: 20210525

CF01 Termination of patent right due to non-payment of annual fee