CN108970586A - A method of utilizing low-concentration ammonia-nitrogen in biological adsorption removing water body - Google Patents

A method of utilizing low-concentration ammonia-nitrogen in biological adsorption removing water body Download PDF

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CN108970586A
CN108970586A CN201710399767.XA CN201710399767A CN108970586A CN 108970586 A CN108970586 A CN 108970586A CN 201710399767 A CN201710399767 A CN 201710399767A CN 108970586 A CN108970586 A CN 108970586A
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nitrogen
ammonia
biomass
water body
metal ion
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黄凯
尹铮
张建峰
尹衍利
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Nanjing Environmental Protection Technology Co Ltd
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Nanjing Environmental Protection Technology Co Ltd
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/24Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0233Compounds of Cu, Ag, Au
    • B01J20/0237Compounds of Cu
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/04Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
    • B01J20/041Oxides or hydroxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/04Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
    • B01J20/043Carbonates or bicarbonates, e.g. limestone, dolomite, aragonite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/32Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3231Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
    • B01J20/3234Inorganic material layers
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4812Sorbents characterised by the starting material used for their preparation the starting material being of organic character
    • B01J2220/485Plants or land vegetals, e.g. cereals, wheat, corn, rice, sphagnum, peat moss

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

Present invention relates particularly to a kind of methods using low-concentration ammonia-nitrogen in biological adsorption removing water body;The following steps are included: preparing biomass absorbent agent material first;Then metal ion is supported on biomass absorbent agent material;The adsorbent material is launched into waste water or water body containing ammonia and nitrogen components again, the amino molecule in aqueous medium is fixed on the load biomass absorbent granular materials of metal ion, to realize the adsorbing and removing purification of ammonia and nitrogen components in water body;Adsorbing the ammonia nitrogen molecule to come up can then be desorbed with diluted acid, concentration, be recycled, and sorbent material can be repeated as many times and use;The method of the present invention is easy to operate, is easy to implement, does not have secondary pollution, various raw and auxiliary materials used are cheap to be easy to get, scale is changeable, both it can shed in the water body of large watershed and use, can also be designed to use in special reactor, with its high-efficiency and economic, it is adaptable the features such as and become administer low-concentration ammonia-nitrogen aqueous medium very promising advanced technology.

Description

A method of utilizing low-concentration ammonia-nitrogen in biological adsorption removing water body
Technical field
The present invention relates to method for treating water, and in particular to a kind of side using low-concentration ammonia-nitrogen in biological adsorption removing water body Method.
Background technique
Due to sanitary wastewater, the uncontrolled discharge of industrial wastewater and a large amount of uses of chemical fertilizer, so that the ammonia in natural water Nitrogen content is generally higher.Ammonia nitrogen is exceeded, and the eutrophication problem that will lead to water body is (as a large amount of in caused water plant, algae and microorganism Breed and seriously consume the dissolved oxygen in water body), directly influence the benign development of natural ecological environment.Ammonia is to the lethal of fish Concentration is 0.2~2mg/L, and raiser is to water eutrophication problem very headache.Country has formulated very the discharge of ammonia nitrogen Stringent control standard, each relevant enterprise also take various suitable methods to the processing of ammonia nitrogen waste water.In general, to super The ammonia nitrogen waste water (> 10g/L) of high concentration can recycle ammonium salt using evaporative crystallization method;For the ammonia nitrogen waste water of higher concentration (> 1g/L) can then use air stripping method, the MAP precipitation method, membrane separation process, break point chlorination oxidative treatment;And low concentration Ammonia nitrogen waste water (< 500mg/L) processing then have ion-exchange, biological denitrificaion method processing.For high-concentration ammonia nitrogenous wastewater, Processing technique is more mature, and for the ammonia nitrogen waste water or water body purification of low concentration, it is only the difficult point of ammonia nitrogen removal technological development And challenge.Processing for Low Concentration Ammonia Containing Wastewater, ion-exchange simple process, easy to operate, investment is lower, but resin Or zeolite quantity is big, difficult for regeneration, costly, and biological denitrificaion rule technical maturity, but long flow path, reactor are big, land occupation Greatly, often need that additional carbon, energy consumption is high, time-consuming, therefore, there is an urgent need to develop it is more economical, faster, more easily handle it is low dense Spend the new technology of ammonia nitrogen.
Summary of the invention
The present invention overcomes the shortcomings of the prior art, technical problem to be solved are as follows: provide it is a kind of it is economical, efficiently, Simply, conveniently, not secondary pollution using biological adsorption removing water body in low-concentration ammonia-nitrogen method.
In order to solve the above-mentioned technical problem, the technical solution adopted by the present invention are as follows:
A method of utilizing low-concentration ammonia-nitrogen in biological adsorption removing water body, comprising the following steps:
A, it is with the biomass material or abandoned biomass rolled into a ball containing carboxyl, sulfydryl, amino or phenolic hydroxyl group active function Raw material prepares biomass absorbent agent material;
B, biomass absorbent agent material prepared by step a pH value range is added to be 1-14 and contain each metal ion species Aqueous solution in, carry out metal ion absorption enrichment;The additive amount of the biomass absorbent agent material is every liter to be processed 0.1-50 grams is added in low-concentration ammonia-nitrogen aqueous solution;Stirring 5-1200 minutes, obtains the biomass absorbent for being enriched with metal ion Agent powder;
C, by the resulting biomass adsorbent powder of step b after water purification is washed 2-3 times repeatedly, in room temperature or 60 DEG C Hot bellows in be dried to its moisture content be 10-80% when, drying object further grind, sieved and is classified, collection granularity exist The compound bio adsorbent material that the following particle of 200 mesh can be used as loaded metal ion is spare;
D, the aqueous solution to be processed containing low concentration ammonia nitrogen component is taken, first adjusts its pH value between 6-11, then will The compound bio adsorbent material investment of the resulting loaded metal ion of step c wherein, stirs, after adsorption reaction 1-10 hours, mistake Filter separation, detects the ammonia and nitrogen components in water;
E, the resulting adsorbent for having adsorbed amino molecule is filtered in step d to be mixed with the diluted acid that pH value is 2-4, it will be therein Amino molecule desorption recycling, and the compound bio adsorbent material for having loaded metal ion then continues on for the suction of water body low-concentration ammonia-nitrogen Attached removing.
Prepared in step a biomass absorbent agent material the specific steps are by biomass material or abandoned biomass with Alkali, water are stirred hybrid reaction according to the mass ratio of 1:0.05-0.2:0.5-2, stir 12-24 hours, filtering, consolidate Body product, wherein the alkali be lithium, sodium, potassium, calcium, the oxide of magnesium, hydroxide, carbonate, bicarbonate or ammonium carbonate, One of ammonium hydrogen carbonate, urea and ammonium hydroxide or two kinds or more mix;The above solid product is washed with water until neutrality, feeding are true Empty baking oven is 60-120 DEG C of drying in temperature, drying object is smashed, is sieved, the following powder collection of 40 mesh can be used as biomass Sorbent material.
The biomass material containing carboxyl, sulfydryl, amino, phenolic hydroxyl group active function group is garlic residue, seaweed, wine Grain, the one or more of tangerine slag, apple skin and chitosan.
Metal ion described in step b is Cu2+、Ni2+、Co2+、Zn2+And Ag+One or more.
Stirring means in step b are mechanical stirring or air stirring, and mixing time is 300-500 minutes.
The present invention is that complexing can occur with ammonia using the basic principle of ammonia nitrogen method in biological adsorption removing water body Metal ion such as Cu2+、Ni2+、Co2+、Zn2+Or Ag+Deng being supported on biomass absorbent material in advance, then by the adsorption material The characteristics of material is launched into waste water or water body containing ammonia and nitrogen components, complex reaction can occur with metal ion using amino molecule, Amino molecule in aqueous medium is fixed on the load biomass absorbent granular materials of metal ion, to realize in water body The adsorbing and removing of ammonia and nitrogen components purifies;And adsorbing the ammonia nitrogen molecule to come up can then be desorbed with diluted acid, concentration, be recycled, adsorbent Material can then be repeated as many times and use.
Compared with the prior art, the invention has the following beneficial effects:
The compound bio adsorbent material prepared by the present invention for having loaded metal ion can then be repeated as many times and use.The present invention Method is easy to operate, process is simple, is easy to implement, does not have secondary pollution, various raw and auxiliary materials used are cheap to be easy to get, scale can be big Can be small, it can both shed in the water body of large watershed and use, can also be designed to use in special reactor, can both administer Natural water such as river, lake, cultivation fish pond, can also administer industrial, agricultural, the special of life outlet nitrogen-containing wastewater is controlled Reason, with its high-efficiency and economic, it is adaptable the features such as and become administer low-concentration ammonia-nitrogen aqueous medium very promising elder generation Into technology.
Detailed description of the invention
Fig. 1 is the process flow of the biomass adsorbent material processing Low Concentration Ammonia Containing Wastewater of loaded metal ion of the present invention Figure.
Specific embodiment
The present invention is further illustrated below in conjunction with specific embodiment.
Embodiment 1
Prepare 10 liters of nitric acid copper ion solution of 0.1M concentration, with the hydrochloric acid and sodium hydroxide solution of 0.1M adjust metal from After the pH of sub- solution is 6,200 grams of apple skin adsorbent are put into, after being stirred to react 30 minutes, adsorbent is filtered, uses distilled water After washing 3 times, it is put into hot wind in 60 DEG C of baking oven and dries 6 hours;Further grinding, screening, classification, can be obtained granularity 200 Negative copper biological adsorption powder-product below mesh.10 liters of water samples containing 50mg/L ammonia nitrogen are taken, surveying its pH value is 7.2, is direct plungeed into The negative copper biological adsorption powder-product of 50 grams of above-mentioned preparations, after being stirred to react 5 hours, it is small to measure ammonia-nitrogen content in water sample for filtering In 1mg/L.
And absorbent particles are then stirred to react 1 hour with 200 milliliters of dilute hydrochloric acid that pH value is 3, and are constantly added suitable The hydrochloric acid conditioning solution pH stable of 1:1 volume ratio is 3, then is filtered, and filtered ammonia nitrogen in solution concentration is 25g/L, It is 1 that its pH value, which can further be adjusted, and obtains solid ammonium chloride using evaporative crystallization method concentration and recovery.Absorbent particles then return It goes to reuse.
Embodiment 2
Prepare 10 liters of nickel nitrate solion of 0.1M concentration, with the hydrochloric acid and sodium hydroxide solution of 0.1M adjust metal from After the pH of sub- solution is 6,100 grams of Cortex Bulbus Allii adsorbent are put into, after being stirred to react 300 minutes, adsorbent is filtered, uses distilled water After washing 3 times, it is put into hot wind in 60 DEG C of baking oven and dries 6 hours;Further grinding, screening, classification, can be obtained granularity 200 Negative nickel biological adsorption powder-product below mesh.10 liters of water samples containing 50mg/L ammonia nitrogen are taken, surveying its pH value is 7.2, is direct plungeed into The negative nickel biological adsorption powder-product of 50 grams of above-mentioned preparations, after being stirred to react 5 hours, it is small to measure ammonia-nitrogen content in water sample for filtering In 3mg/L.
And absorbent particles are then stirred to react 1 hour with 200 milliliters of dilute hydrochloric acid that pH value is 3, and are constantly added suitable The hydrochloric acid conditioning solution pH stable of 1:1 volume ratio is 3, then is filtered, and filtered ammonia nitrogen in solution concentration is 24g/L, It is 1 that its pH value, which can further be adjusted, and obtains solid ammonium chloride using evaporative crystallization method concentration and recovery.Absorbent particles then return It goes to reuse.
Embodiment 3
Prepare 10 liters of nitric acid silver ion solution of 0.1M concentration, with the nitric acid and sodium hydroxide solution of 0.1M adjust metal from After the pH of sub- solution is 4,300 grams of beer malt vinasse adsorbent is put into, after being stirred to react 500 minutes, adsorbent is filtered, used After distillation water washing 3 times, it is put into hot wind in 60 DEG C of baking oven and dries 6 hours;Further grinding, screening, classification, can be obtained granularity Silver biological adsorption powder-product is born below 200 mesh.10 liters of water samples containing 50mg/L ammonia nitrogen are taken, surveying its pH value is 7.2, directly The negative silver-colored biological adsorption powder-product of 50 grams of above-mentioned preparations of investment, after being stirred to react 5 hours, filtering measures ammonia nitrogen in water sample and contains Amount is less than 0.5mg/L.
And absorbent particles are then stirred to react 1 hour with 200 milliliters of dilute citric acid that pH value is 4, then are filtered, and are filtered Ammonia nitrogen in solution concentration afterwards is 24g/L, and can further adjust its pH value is 1, and is obtained using evaporative crystallization method concentration and recovery Solid citric acid ammonium.Absorbent particles then return to reuse.
Embodiment 4
Prepare 10 liters of zinc nitrate solion of 0.1M concentration, with the hydrochloric acid and sodium hydroxide solution of 0.1M adjust metal from After the pH of sub- solution is 6,200 grams of Cortex Bulbus Allii adsorbent are put into, after being stirred to react 30 minutes, adsorbent is filtered, uses distilled water After washing 3 times, it is put into hot wind in 60 DEG C of baking oven and dries 6 hours;Further grinding, screening, classification, can be obtained granularity 200 Negative zinc biological adsorption powder-product below mesh.10 liters of water samples containing 20mg/L ammonia nitrogen are taken, surveying its pH value is 9.9, then directly throws Enter 50 grams or more the negative zinc biological adsorption powder-products respectively prepared, after being stirred to react 5 hours, filtering measures ammonia nitrogen in water sample and contains Amount is less than 1mg/L.
And absorbent particles are then stirred to react 1 hour with 200 milliliters of dilute hydrochloric acid that pH value is 3, and are constantly added suitable The hydrochloric acid conditioning solution pH stable of 1:1 volume ratio is 3, then is filtered, and filtered ammonia nitrogen in solution concentration is 10g/L, It is 1 that its pH value, which can further be adjusted, and obtains solid ammonium chloride using evaporative crystallization method concentration and recovery.Absorbent particles then return It goes to reuse.
Embodiment 5
10 liters of certain waterworks water sample is taken, chemically examining ammonia nitrogen concentration therein is 10mg/L, and pH value 7.8 puts into embodiment party 50 grams of negative copper biological adsorption material prepared in formula 1, after being stirred to react 5 hours, filtering measures ammonia-nitrogen content in water sample and is less than 1mg/L。
And absorbent particles are then stirred to react 1 hour with 200 milliliters of dilute hydrochloric acid that pH value is 3, and are constantly added suitable The hydrochloric acid conditioning solution pH stable of 1:1 volume ratio is 3, then is filtered, and filtered ammonia nitrogen in solution concentration is 4.5g/L, It is 1 that its pH value, which can further be adjusted, and obtains solid ammonium chloride using evaporative crystallization method concentration and recovery.Absorbent particles then return It goes to reuse.
Embodiment 6
Prepare 0.1M concentration copper nitrate and 10 liters of zinc nitrate mixed solution, with the hydrochloric acid and sodium hydroxide solution tune of 0.1M After the pH for saving metal ion solution is 6, apple skin and 200 grams of Cortex Bulbus Allii mixed adsorbent are put into, it, will after being stirred to react 30 minutes Adsorbent filtering after being washed with distilled water 3 times, is put into hot wind in 60 DEG C of baking oven and dries 6 hours;It further grinds, screening, divide Grade, can be obtained the biological adsorption powder-product of granularity negative copper zinc below 200 mesh.Take 10 liters of water containing 50mg/L ammonia nitrogen Sample, surveying its pH value is 7.2, direct plunges into the biological adsorption powder-product of the negative copper zinc of 50 grams of above-mentioned preparations, is stirred to react 5 hours Afterwards, it filters, measures ammonia-nitrogen content in water sample and be less than 1mg/L.
And absorbent particles are then stirred to react 1 hour with 200 milliliters of dilute hydrochloric acid that pH value is 3, and are constantly added suitable The hydrochloric acid conditioning solution pH stable of 1:1 volume ratio is 3, then is filtered, and filtered ammonia nitrogen in solution concentration is 20g/L, It is 1 that its pH value, which can further be adjusted, and obtains solid ammonium chloride using evaporative crystallization method concentration and recovery.Absorbent particles then return It goes to reuse.
Above case study on implementation is to help those skilled in the art and more fully understands core of the invention skill Art main points, all known biology to metal ion with absorption property that can be detailed of the those of ordinary skill including biological adsorption field Adsorbent is raw material, carries out and prepares the suction of metal load type biomass to the adsorption operations of the metal cations such as copper, silver, nickel, cobalt, zinc Enclosure material.Biomass absorbent material therein refers to the metal cations such as all pairs of copper, silver, nickel, cobalt, zinc with adsorption effect Biomass material sorbent material;The waste water containing ammonia nitrogen in embodiments herein is either the ammonia nitrogen mould manually prepared Quasi- waste water, the water sample being also possible in the industrial wastewater or natural environment containing ammonia nitrogen that actual industry spot is fetched.
Finally, it should be noted that the above embodiments are only used to illustrate the technical solution of the present invention., rather than its limitations;To the greatest extent Pipe present invention has been described in detail with reference to the aforementioned embodiments, those skilled in the art should understand that: its according to So be possible to modify the technical solutions described in the foregoing embodiments, or to some or all of the technical features into Row equivalent replacement;And these are modified or replaceed, various embodiments of the present invention technology that it does not separate the essence of the corresponding technical solution The range of scheme.

Claims (5)

1. a kind of method using low-concentration ammonia-nitrogen in biological adsorption removing water body, which comprises the following steps:
A, using the biomass material or abandoned biomass rolled into a ball containing carboxyl, sulfydryl, amino or phenolic hydroxyl group active function as raw material, Prepare biomass absorbent agent material;
B, biomass absorbent agent material prepared by step a is added to the water that pH value range is 1-14 and contains each metal ion species In solution, the absorption enrichment of metal ion is carried out;The additive amount of the biomass absorbent agent material is every liter to be processed low dense It spends and adds 0.1-50 grams in ammonia nitrogen aqueous solution;Stirring 5-1200 minutes, obtains the biomass adsorbent powder for being enriched with metal ion End;
C, by the resulting biomass adsorbent powder of step b after water purification is washed 2-3 times repeatedly, in room temperature or 60 DEG C of heat Be dried in bellows its moisture content be 10-80% when, drying object further grind, sieved and is classified, collection granularity in 200 mesh The compound bio adsorbent material that following particle can be used as loaded metal ion is spare;
D, the aqueous solution to be processed containing low concentration ammonia nitrogen component is taken, first adjusts its pH value between 6-11, then by step c The compound bio adsorbent material investment of resulting loaded metal ion wherein, after adsorption reaction 1-10 hours, filter and divide by stirring From, detect water in ammonia and nitrogen components;
E, the resulting adsorbent for having adsorbed amino molecule is filtered in step d and is mixed with the diluted acid that pH value is 2-4, by ammonia therein point Subsolution sucks back receipts, and the absorption that the compound bio adsorbent material for having loaded metal ion then continues on for water body low-concentration ammonia-nitrogen is de- It removes.
2. a kind of method using low-concentration ammonia-nitrogen in biological adsorption removing water body according to claim 1, feature exist In, prepared in step a biomass absorbent agent material the specific steps are by biomass material or abandoned biomass and alkali, water by It is stirred hybrid reaction according to the mass ratio of 1:0.05-0.2:0.5-2, is stirred 12-24 hours, filtering obtains solid product, Wherein, the alkali be lithium, sodium, potassium, calcium, the oxide of magnesium, hydroxide, carbonate, bicarbonate, ammonium carbonate, ammonium hydrogen carbonate, One of urea and ammonium hydroxide or two kinds or more mix;The above solid product is washed with water up to neutrality, is sent into vacuum drying oven, Temperature is 60-120 DEG C of drying, and drying object is smashed, is sieved, the following powder collection of 40 mesh can be used as biomass adsorbent material Material.
3. a kind of method using low-concentration ammonia-nitrogen in biological adsorption removing water body according to claim 1, feature exist In the biomass material containing carboxyl, sulfydryl, amino or phenolic hydroxyl group active function group in step a is garlic residue, sea Algae, vinasse, tangerine slag, apple skin and chitosan one or more.
4. a kind of method using low-concentration ammonia-nitrogen in biological adsorption removing water body according to claim 1, feature exist In metal ion described in step b is Cu2+、Ni2+、Co2+、Zn2+And Ag+One or more.
5. a kind of method using low-concentration ammonia-nitrogen in biological adsorption removing water body according to claim 1, feature exist In the stirring means in step b are mechanical stirring or air stirring, and mixing time is 300-500 minutes.
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Application publication date: 20181211