CN104907047A - Method used for treating highly concentrated ammonia-nitrogen in rare earth waste water - Google Patents

Method used for treating highly concentrated ammonia-nitrogen in rare earth waste water Download PDF

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CN104907047A
CN104907047A CN201510271796.9A CN201510271796A CN104907047A CN 104907047 A CN104907047 A CN 104907047A CN 201510271796 A CN201510271796 A CN 201510271796A CN 104907047 A CN104907047 A CN 104907047A
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waste water
nitrogen
organic composite
adsorption
aluminum
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雷春生
张帆
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Changzhou University
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Abstract

The invention relates to a method used for treating highly concentrated ammonia-nitrogen in rare earth waste water, and belongs to the field of highly concentrated ammonia-nitrogen treatment. According to the method, a sticky solution is prepared from a prepared organic composite denitrfying agent modified magnesium aluminum iron hydrotalcite magnetic nano adsorption material and an adhesion agent at a mass ratio of 7:1; the surfaces of adsorption rods are coated with the sticky solution, and the adsorption rods are dried under ventilation states and are delivered into an adsorption tower; a rare earth waste water penetrating fluid is delivered through the adsorption tower so as to adsorb 8000 to 12000mg/L highly concentrated ammonia-nitrogen in the rare earth waste water, wherein aging of adsorption material surface layers can be realized via adsorption saturation; under action of applied magnetic field and current scour, layer-by-layer falling of the adsorption material surface layers is realized, and at last the ammonia-nitrogen content of the rare earth waste water is detected. The method is capable of realizing adsorption material renewal; regeneration is not needed; the ammonia-nitrogen concentration of discharged waste water is controlled to be lower than 0.7mg/L; ammonia-nitrogen removing rate is higher than 99.99%; and no secondary pollution is caused to the environment.

Description

A kind of process RE waste water middle and high concentration ammonia nitrogen method
Technical field
The present invention relates to a kind of process RE waste water middle and high concentration ammonia nitrogen method, belong to high ammonia-nitrogen wastewater process field.
Background technology
Rare-earth trade is an emerging industry, along with people's environmental consciousness strengthens, the pollution problem of rare-earth trade draws attention gradually, and ammonia nitrogen pollutant is one of three large waste water produced in rare-earth smelting, ammonia nitrogen has certain harm for human body and water body, in water quality index, ammonia nitrogen causes the important pollutant of the one of body eutrophication and environmental pollution, it can make water lose self-purification function, it enters human body and synthesizes nitroso compound, bring out canceration, the generation of gastrointestinal disorders and endemic illness when ammonia-nitrogen content is too high in drinking water, can be caused.
Discharge in Rare Earth Production process three kinds of waste water, the ammonium salt waste water that the acid waste water of mainly rare earth ore concentrate baking tail gases spray cleaning generation, carbonated rare earth production process produce and the ammonium salt waste water that Rare Earth Separation produces.For ammonia nitrogen, the wastewater flow rate that rare-earth trade produces every year reaches more than 1,500 ten thousand tons, wherein ammonia-nitrogen content 8000 ~ 12000mg/L, exceeds discharging standards tens doubly to hundreds of times.
Ammonia nitrogen waste water enters water body, particularly flow to lake more slowly, bay, easily cause algae and other microorganism amount reproduction in water, form eutrophication pollution, difficulty is run except water treatment plants can be made, cause outside the peculiar smell of drinking water, oxygen in water can be made time serious to decline, fish kill, lake even can be caused to be destroyed, ammonia nitrogen also makes to increase chlorine dosage in water disinfection and industrial circulating water sterilisation process, to some metal, particularly to copper, there is corrosivity, in order to reduce waste and the environmental pollution of water resource, improve Business Economic Benefit and society's effect, advanced treating carried out to ammonia nitrogen waste water imperative.
Modern technologies process RE waste water middle and high concentration ammonia nitrogen method mainly contains blow-off method and vaporizing extract process, ion-exchange.Blow-off method and vaporizing extract process refer to when in waste water, pH value is adjusted to alkalescence, ion state ammonium is converted into molecular state ammonia, again waste gas is contacted with gas, ammonia nitrogen is made to transfer to gas phase from liquid phase, the method is usually used in high-concentration ammonia nitrogenous wastewater process, but it is low to there is treatment effeciency when practical operation, occur incrustation scale impact operation, energy consumption and maintenance workload cause the phenomenons such as secondary pollution more greatly and easily; And be CN101372370 at publication number, by by 50% ~ 80% form organic denitrifier by lipid, 10% ~ 50% amine and 10% ~ 50% alkanes and add in high-concentration ammonia nitrogenous wastewater in a kind of method that name is called described in " organic denitrifier and denitrogenation method processing high-concentration ammonia nitrogenous wastewater ", to regulate after pH value of waste water aeration 2 hours, this invention effectively can improve ammonia nitrogen removal frank, but still cannot solve in stripping process due to secondary pollution problem that ammonia emission causes; The ion-exchange of next refers to select have the zeolite of very strong selectivity as exchanger resin to ion, thus reach the object removing ammonia nitrogen, to high-concentration ammonia nitrogenous wastewater, frequently operating difficulties can be caused because of resin regeneration, sub-exchange process clearance is lower, also can cause secondary pollution for environment.
Summary of the invention
The technical problem that the present invention mainly solves: there is ammonia emission in conjunction with blow-off method in high-concentration ammonia nitrogenous wastewater processing procedure for organic composite denitrifier, cause secondary environmental pollution problem, provide a kind of organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite nano magnetic adsorptive material, absorption high-concentration ammonia nitrogen in waste water, and saturated after can aging sorbing material top layer, under externally-applied magnetic field and current scour effect, realize the renewal of sorbing material, without the need to regeneration.
In order to achieve the above object, the technical solution adopted in the present invention is:
(1) magnesium-aluminum-iron hydrotalcite preparation: take 6.2 ~ 11.4g magnesium nitrate, 4.2 ~ 7.5g aluminum nitrate respectively, 5.3 ~ 11.4g ferric nitrate is dissolved in 430 ~ 550ml and contains in the ethanol solution of 5.8 ~ 8.6g urea; Stirred at ambient temperature 1h; Pour in hydrothermal reaction kettle and be heated to 130 DEG C, reaction 12 ~ 14h; The room temperature of cooling; With after ethanol and washed with de-ionized water two times at 100 DEG C dry 8h, obtain nano magnalium molten iron talcum;
(2) magnetize: be concentrated hydrochloric acid and the saturated potassium hydroxide solution immersion 6h of 36.5% successively by mass concentration by the nano magnalium molten iron talcum of above-mentioned preparation, be placed in Muffle furnace, dry at temperature is 110 DEG C, near magnetic field magnetisation;
(3) modification: the nano magnalium molten iron talc materials after pickling, alkali leaching and magnetization is immersed in 15 ~ 35g organic composite denitrifier, stirs 40 ~ 60min;
(4) dry: by modified nano magnalium molten iron talc materials washed with de-ionized water 3 times, dry under nitrogen protection condition;
(5) activate: at temperature is 800 DEG C ~ 900 DEG C, calcine 4 ~ 6h.
Described organic composite denitrifier is oxaloacetic acid, triethyl phosphate, prenol form, by quality ratio, and 10% ~ 45% oxaloacetic acid, 20% ~ 55% triethyl phosphate, 20% ~ 45% prenol.
Application process of the present invention is:
(1) by the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material prepared and adhesive in mass ratio 7:1 be made into viscous fluid, by viscous fluid Tu in polytetrafluoroethylene (PTFE) tiny balloon top layer, coating layer thickness is 4 ~ 7cm, by the polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid dry 15 ~ 25min under ventilation state, described adhesive with parts by weight count 30 parts of m-phenylene diamine (MPD)s, 15 parts of para aminoacet anilides, 15 part 3,3-MDA, 40 part 3,3,4,4-diphenyl ether dianhydride;
(2) the polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid is placed in adsorption tower, every layer of setting height(from bottom) is 10 ~ 60cm, space height is 50 ~ 120cm, allow ammonia nitrogen concentration be the RE waste water permeate flow of 8000 ~ 12000mg/L through adsorption tower, flow control 5 ~ 20m 3/ h, absorption dwell time in the tower 45 ~ 60min, until the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material ammonia nitrogen absorption on polytetrafluoroethylene (PTFE) tiny balloon surface reaches capacity, organic composite denitrifier aging magnesium-aluminum-iron hydrotalcite magnetic Nano material top layer;
(3) RE waste water penetrating fluid again current wash away with under externally-applied magnetic field effect, aging sorbing material top layer comes off layer by layer;
(4) ammonia-nitrogen content in last wastewater measurement water outlet.
Principle of the present invention: it is large that magnesium-aluminum-iron hydrotalcite material has specific area, belong to mesoporous material material, to ammonia nitrogen in waste water, there is absorption property through organic composite denitrifier is modified, the more important thing is, adding of organic composite denitrifier, can come off layer by layer voluntarily after sorbing material absorption ammonia nitrogen can be made to reach capacity, realize the renewal on sorbing material surface, again adsorb the ammonia nitrogen in high density in waste water, and the residue after coming off is separated with externally-applied magnetic field effect in current scour.
The invention has the beneficial effects as follows:
(1) produce without pernicious gas, can not secondary environmental pollution be caused;
(2) organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite nano magnetic adsorptive material is prepared, absorption high-concentration ammonia nitrogen in waste water, and saturated after can aging sorbing material top layer, under externally-applied magnetic field and current scour effect, realize the renewal of sorbing material, without the need to regeneration;
(3) after coming off, residue is little without moisture, volume, separable under externally-applied magnetic field, and ammonia nitrogen removal frank is high, cost is low.
Detailed description of the invention
The preparation of organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material:
(1) magnesium-aluminum-iron hydrotalcite preparation: take 6.2 ~ 11.4g magnesium nitrate, 4.2 ~ 7.5g aluminum nitrate respectively, 5.3 ~ 11.4g ferric nitrate is dissolved in 430 ~ 550ml and contains in the ethanol solution of 5.8 ~ 8.6g urea; Stirred at ambient temperature 1h; Pour in hydrothermal reaction kettle and be heated to 130 DEG C, reaction 12 ~ 14h; The room temperature of cooling; With after ethanol and washed with de-ionized water two times at 100 DEG C dry 8h, obtain nano magnalium molten iron talcum;
(2) magnetize: be concentrated hydrochloric acid and the saturated potassium hydroxide solution immersion 6h of 36.5% successively by mass concentration by the nano magnalium molten iron talcum of above-mentioned preparation, be placed in Muffle furnace, dry at temperature is 110 DEG C, near magnetic field magnetisation;
(3) modification: the nano magnalium molten iron talc materials after pickling, alkali leaching and magnetization is immersed in 15 ~ 35g organic composite denitrifier, stirs 40 ~ 60min;
(4) dry: by modified nano magnalium molten iron talc materials washed with de-ionized water 3 times, dry under nitrogen protection condition;
(5) activate: at temperature is 800 DEG C ~ 900 DEG C, calcine 4 ~ 6h.
Described organic composite denitrifier is oxaloacetic acid, triethyl phosphate, prenol form, by quality ratio, and 10% ~ 45% oxaloacetic acid, 20% ~ 55% triethyl phosphate, 20% ~ 45% prenol.
Nano adsorption material removes the embody rule of high-concentration ammonia nitrogenous wastewater:
(1) by the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material prepared and adhesive in mass ratio 7:1 be made into viscous fluid, by viscous fluid Tu in polytetrafluoroethylene (PTFE) tiny balloon top layer, coating layer thickness is 4 ~ 7cm, by the polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid dry 15 ~ 25min under ventilation state, described adhesive with parts by weight count 30 parts of m-phenylene diamine (MPD)s, 15 parts of para aminoacet anilides, 15 part 3,3-MDA, 40 part 3,3,4,4-diphenyl ether dianhydride;
(2) the polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid is placed in adsorption tower, every layer of setting height(from bottom) is 10 ~ 60cm, space height is 50 ~ 120cm, allow ammonia nitrogen concentration be the RE waste water permeate flow of 8000 ~ 12000mg/L through adsorption tower, flow control 5 ~ 20m 3/ h, absorption dwell time in the tower 45 ~ 60min, until the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material ammonia nitrogen absorption on polytetrafluoroethylene (PTFE) tiny balloon surface reaches capacity, organic composite denitrifier aging magnesium-aluminum-iron hydrotalcite magnetic Nano material top layer;
(3) RE waste water penetrating fluid again current wash away with under externally-applied magnetic field effect, aging sorbing material top layer comes off layer by layer;
(4) ammonia-nitrogen content in last wastewater measurement water outlet.
Example 1
First take respectively 6.2g magnesium nitrate, 4.2g aluminum nitrate, 5.3g ferric nitrate be dissolved in 430ml and contain in the ethanol solution of 5.8g urea; Stirred at ambient temperature 1h; Pour in hydrothermal reaction kettle and be heated to 130 DEG C, reaction 12h, the room temperature of cooling; With after ethanol and washed with de-ionized water two times at 100 DEG C dry 8h, obtain nano magnalium molten iron talcum; Be concentrated hydrochloric acid and the saturated potassium hydroxide solution immersion 6h of 36.5% more successively by mass concentration by the nano magnalium molten iron talcum of above-mentioned preparation, be placed in Muffle furnace, dry at temperature is 110 DEG C, near magnetic field magnetisation; Then the nano magnalium molten iron talc materials after pickling, alkali leaching and magnetization is immersed in 15g organic composite denitrifier, wherein comprise 6.5g oxaloacetic acid, 4.5g triethyl phosphate, 4g prenol, stir 40min; By modified nano magnalium molten iron talc materials washed with de-ionized water 3 times, dry under nitrogen protection condition, 4h is calcined at temperature is 800 DEG C, organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material can be obtained, by the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material prepared and adhesive in mass ratio 7:1 be made into viscous fluid, by viscous fluid Tu in polytetrafluoroethylene (PTFE) tiny balloon top layer, coating layer thickness is 4cm, by the polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid dry 15min under ventilation state; The polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid is placed in adsorption tower, and every layer of setting height(from bottom) is 10cm, and space height is 50cm, allow ammonia nitrogen concentration be the RE waste water permeate flow of 8000mg/L through adsorption tower, flow control 5m 3/ h, absorption dwell time in the tower 45min, until the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material ammonia nitrogen absorption on polytetrafluoroethylene (PTFE) tiny balloon surface reaches capacity, organic composite denitrifier aging magnesium-aluminum-iron hydrotalcite magnetic Nano material top layer; RE waste water penetrating fluid again current wash away with under externally-applied magnetic field effect, aging sorbing material top layer comes off layer by layer, and in last wastewater measurement water outlet, ammonia-nitrogen content is 0.6mg/L, and ammonia nitrogen removal frank is more than 99.99%.
Example 2
First take respectively 8.3g magnesium nitrate, 5.9g aluminum nitrate, 7.6g ferric nitrate be dissolved in 500ml and contain in the ethanol solution of 7.1g urea; Stirred at ambient temperature 1h; Pour in hydrothermal reaction kettle and be heated to 130 DEG C, reaction 13h, the room temperature of cooling; With after ethanol and washed with de-ionized water two times at 100 DEG C dry 8h, obtain nano magnalium molten iron talcum; Be concentrated hydrochloric acid and the saturated potassium hydroxide solution immersion 6h of 36.5% more successively by mass concentration by the nano magnalium molten iron talcum of above-mentioned preparation, be placed in Muffle furnace, dry at temperature is 110 DEG C, near magnetic field magnetisation; Then the nano magnalium molten iron talc materials after pickling, alkali leaching and magnetization is immersed in 20g organic composite denitrifier, wherein comprise 7g oxaloacetic acid, 8g triethyl phosphate, 5g prenol, stir 55min; By modified nano magnalium molten iron talc materials washed with de-ionized water 3 times, dry under nitrogen protection condition, 5h is calcined at temperature is 850 DEG C, organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material can be obtained, by the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material prepared and adhesive in mass ratio 7:1 be made into viscous fluid, by viscous fluid Tu in polytetrafluoroethylene (PTFE) tiny balloon top layer, coating layer thickness is 6cm, by the polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid dry 20min under ventilation state; The polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid is placed in adsorption tower, and every layer of setting height(from bottom) is 20cm, and space height is 70cm, allow ammonia nitrogen concentration be the RE waste water permeate flow of 10000mg/L through adsorption tower, flow control 15m 3/ h, absorption dwell time in the tower 55min, until the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material ammonia nitrogen absorption on polytetrafluoroethylene (PTFE) tiny balloon surface reaches capacity, organic composite denitrifier aging magnesium-aluminum-iron hydrotalcite magnetic Nano material top layer; RE waste water penetrating fluid again current wash away with under externally-applied magnetic field effect, aging sorbing material top layer comes off layer by layer, and in last wastewater measurement water outlet, ammonia-nitrogen content is 0.4mg/L, and ammonia nitrogen removal frank is more than 99.99%.
Example 3
First take respectively 11.4g magnesium nitrate, 7.5g aluminum nitrate, 11.4g ferric nitrate be dissolved in 550ml and contain in the ethanol solution of 8.6g urea; Stirred at ambient temperature 1h; Pour in hydrothermal reaction kettle and be heated to 130 DEG C, reaction 14h, the room temperature of cooling; With after ethanol and washed with de-ionized water two times at 100 DEG C dry 8h, obtain nano magnalium molten iron talcum; Be concentrated hydrochloric acid and the saturated potassium hydroxide solution immersion 6h of 36.5% more successively by mass concentration by the nano magnalium molten iron talcum of above-mentioned preparation, be placed in Muffle furnace, dry at temperature is 110 DEG C, near magnetic field magnetisation; Then the nano magnalium molten iron talc materials after pickling, alkali leaching and magnetization is immersed in 35g organic composite denitrifier, wherein comprise 8g oxaloacetic acid, 14g triethyl phosphate, 13g prenol, stir 60min; By modified nano magnalium molten iron talc materials washed with de-ionized water 3 times, dry under nitrogen protection condition, 6h is calcined at temperature is 900 DEG C, organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material can be obtained, by the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material prepared and adhesive in mass ratio 7:1 be made into viscous fluid, by viscous fluid Tu in polytetrafluoroethylene (PTFE) tiny balloon top layer, coating layer thickness is 7cm, by the polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid dry 25min under ventilation state; The polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid is placed in adsorption tower, and every layer of setting height(from bottom) is 20cm, and space height is 120cm, allow ammonia nitrogen concentration be the RE waste water permeate flow of 12000mg/L through adsorption tower, flow control 20m 3/ h, absorption dwell time in the tower 60min, until the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material ammonia nitrogen absorption on polytetrafluoroethylene (PTFE) tiny balloon surface reaches capacity, organic composite denitrifier aging magnesium-aluminum-iron hydrotalcite magnetic Nano material top layer; RE waste water penetrating fluid again current wash away with under externally-applied magnetic field effect, aging sorbing material top layer comes off layer by layer, and in last wastewater measurement water outlet, ammonia nitrogen is content 0.3mg/L, and ammonia nitrogen removal frank is more than 99.99%.

Claims (3)

1. process a RE waste water middle and high concentration ammonia nitrogen method, it is characterized in that organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material preparation process is:
(1) magnesium-aluminum-iron hydrotalcite preparation: take 6.2 ~ 11.4g magnesium nitrate, 4.2 ~ 7.5g aluminum nitrate respectively, 5.3 ~ 11.4g ferric nitrate is dissolved in 430 ~ 550ml and contains in the ethanol solution of 5.8 ~ 8.6g urea; Stirred at ambient temperature 1h; Pour in hydrothermal reaction kettle and be heated to 130 DEG C, reaction 12 ~ 14h; The room temperature of cooling; With after ethanol and washed with de-ionized water two times at 100 DEG C dry 8h, obtain nano magnalium molten iron talcum;
(2) magnetize: be concentrated hydrochloric acid and the saturated potassium hydroxide solution immersion 6h of 36.5% successively by mass concentration by the nano magnalium molten iron talcum of above-mentioned preparation, be placed in Muffle furnace, dry at temperature is 110 DEG C, near magnetic field magnetisation;
(3) modification: the nano magnalium molten iron talc materials after pickling, alkali leaching and magnetization is immersed in 15 ~ 35g organic composite denitrifier, stirs 40 ~ 60min;
(4) dry: by modified nano magnalium molten iron talc materials washed with de-ionized water 3 times, dry under nitrogen protection condition;
(5) activate: at temperature is 800 DEG C ~ 900 DEG C, calcine 4 ~ 6h.
2. one processes RE waste water middle and high concentration ammonia nitrogen method according to claim 1, it is characterized in that described organic composite denitrifier is oxaloacetic acid, triethyl phosphate, prenol form, by quality ratio, 10% ~ 45% oxaloacetic acid, 20% ~ 55% triethyl phosphate, 20% ~ 45% prenol.
3. process a RE waste water middle and high concentration ammonia nitrogen method, it is characterized in that embody rule method is:
(1) by the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material prepared and adhesive in mass ratio 7:1 be made into viscous fluid, by viscous fluid Tu in polytetrafluoroethylene (PTFE) tiny balloon top layer, coating layer thickness is 4 ~ 7cm, by the polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid dry 15 ~ 25min under ventilation state, described adhesive with parts by weight count 30 parts of m-phenylene diamine (MPD)s, 15 parts of para aminoacet anilides, 15 part 3,3-MDA, 40 part 3,3,4,4-diphenyl ether dianhydride;
(2) the polytetrafluoroethylene (PTFE) tiny balloon of coated viscous fluid is placed in adsorption tower, every layer of setting height(from bottom) is 10 ~ 60cm, space height is 50 ~ 120cm, allow ammonia nitrogen concentration be the RE waste water permeate flow of 8000 ~ 12000mg/L through adsorption tower, flow control 5 ~ 20m 3/ h, absorption dwell time in the tower 45 ~ 60min, until the organic composite denitrifier modification magnesium-aluminum-iron hydrotalcite magnetic nano adsorption material ammonia nitrogen absorption on polytetrafluoroethylene (PTFE) tiny balloon surface reaches capacity, organic composite denitrifier aging magnesium-aluminum-iron hydrotalcite magnetic Nano material top layer;
(3) RE waste water penetrating fluid again current wash away with under externally-applied magnetic field effect, aging sorbing material top layer comes off layer by layer;
(4) ammonia-nitrogen content in last wastewater measurement water outlet.
CN201510271796.9A 2015-05-25 2015-05-25 Method used for treating highly concentrated ammonia-nitrogen in rare earth waste water Pending CN104907047A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106693925A (en) * 2016-12-25 2017-05-24 常州亚环环保科技有限公司 Preparation method of saturation self-falling-off ammonia-nitrogen wastewater adsorbent
CN106732469A (en) * 2017-02-22 2017-05-31 中山市环保产业有限公司 A kind of preparation method of magnetic absorption dephosphorization agent and its renovation process of product
WO2017202969A1 (en) * 2016-05-25 2017-11-30 Kemira Oyj Coagulant composition for wastewater treatment

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2002100509A1 (en) * 2001-06-08 2002-12-19 The Penn State Research Foundation A method for perchlorate removal from ground water
JP2006075815A (en) * 2004-09-13 2006-03-23 Shimane Univ Molding for denitrifying/dephosphorizing and method for denitrifying/dephosphorizing sewage or waste water
CN102649596A (en) * 2012-04-28 2012-08-29 常州亚环环保科技有限公司 Method for treating high-concentration ammonia nitrogen in pesticide waste water
CN102674515A (en) * 2012-05-18 2012-09-19 上海大学 Method for regulating, controlling and forming hydrotalcite-like compound deep treatment leachate tail water
CN102794201A (en) * 2012-07-18 2012-11-28 常州大学 Preparation method of catalyst for promoting conversion of ammonia nitrogen in coking wastewater
CN102908980A (en) * 2012-09-25 2013-02-06 常州亚环环保科技有限公司 Composite adsorbing material for removing chloride ions in water and preparation method of composite adsorbing material
CN103301803A (en) * 2013-06-27 2013-09-18 武汉科梦环境工程有限公司 Preparation method of attapulgite-modified clay for ammonia-nitrogen wastewater treatment
CN103301804A (en) * 2013-07-08 2013-09-18 兰州理工大学 Method for preparing hydrotalcite like compound/attapulgite composite material
CN104148089A (en) * 2014-07-18 2014-11-19 常州大学 Preparation and application method of high-concentration ammonia nitrogen catalyst in papermaking wastewater

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2002100509A1 (en) * 2001-06-08 2002-12-19 The Penn State Research Foundation A method for perchlorate removal from ground water
JP2006075815A (en) * 2004-09-13 2006-03-23 Shimane Univ Molding for denitrifying/dephosphorizing and method for denitrifying/dephosphorizing sewage or waste water
CN102649596A (en) * 2012-04-28 2012-08-29 常州亚环环保科技有限公司 Method for treating high-concentration ammonia nitrogen in pesticide waste water
CN102674515A (en) * 2012-05-18 2012-09-19 上海大学 Method for regulating, controlling and forming hydrotalcite-like compound deep treatment leachate tail water
CN102794201A (en) * 2012-07-18 2012-11-28 常州大学 Preparation method of catalyst for promoting conversion of ammonia nitrogen in coking wastewater
CN102908980A (en) * 2012-09-25 2013-02-06 常州亚环环保科技有限公司 Composite adsorbing material for removing chloride ions in water and preparation method of composite adsorbing material
CN103301803A (en) * 2013-06-27 2013-09-18 武汉科梦环境工程有限公司 Preparation method of attapulgite-modified clay for ammonia-nitrogen wastewater treatment
CN103301804A (en) * 2013-07-08 2013-09-18 兰州理工大学 Method for preparing hydrotalcite like compound/attapulgite composite material
CN104148089A (en) * 2014-07-18 2014-11-19 常州大学 Preparation and application method of high-concentration ammonia nitrogen catalyst in papermaking wastewater

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
张海永等: "一种新型的纳米功能材料:磁性纳米镁铝水滑石", 《无机化学学报》 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2017202969A1 (en) * 2016-05-25 2017-11-30 Kemira Oyj Coagulant composition for wastewater treatment
US11130687B2 (en) 2016-05-25 2021-09-28 Kemira Oyj Coagulant composition for wastewater treatment
CN106693925A (en) * 2016-12-25 2017-05-24 常州亚环环保科技有限公司 Preparation method of saturation self-falling-off ammonia-nitrogen wastewater adsorbent
CN106732469A (en) * 2017-02-22 2017-05-31 中山市环保产业有限公司 A kind of preparation method of magnetic absorption dephosphorization agent and its renovation process of product

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Application publication date: 20150916