CN105948307B - A kind for the treatment of process of lead waste water - Google Patents

A kind for the treatment of process of lead waste water Download PDF

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Publication number
CN105948307B
CN105948307B CN201610313618.2A CN201610313618A CN105948307B CN 105948307 B CN105948307 B CN 105948307B CN 201610313618 A CN201610313618 A CN 201610313618A CN 105948307 B CN105948307 B CN 105948307B
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waste water
montmorillonite
heavy metal
lead
treatment
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CN105948307A (en
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孙静亚
高志伟
张异凡
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Zhejiang Ocean University ZJOU
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Zhejiang Ocean University ZJOU
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    • 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
    • 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
    • B01J20/046Solid 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 containing halogens, e.g. halides
    • 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
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/12Naturally occurring clays or bleaching earth
    • 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
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Dispersion Chemistry (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Water Treatment By Sorption (AREA)
  • Silicates, Zeolites, And Molecular Sieves (AREA)

Abstract

The invention discloses a kind for the treatment of process of lead waste water comprising waste water filtering, adjusting pH value, modified montmorillonite used heavy metal absorbent absorption, secondary filter and examination of wastewater discharge and etc.;Waste water treatment process containing heavy metal lead in the present invention is simple, excellent effect, waste water after processing can reach discharge standard, the modified montmorillonite used heavy metal absorbent manufacture craft used is simple and easy, the modified montmorillonite used heavy metal absorbent used may be reused after having handled waste water through simple process.

Description

A kind for the treatment of process of lead waste water
Technical field
The present invention relates to technical field of waste water processing, more particularly, to a kind for the treatment of process of lead waste water.
Background technique
Lead is often used as raw material applied to manufacturing industry such as battery, plating, pigment, rubber, pesticide, fuel.Stereotype production Acid waste water (pH=3) the lead concentration highest discharged in technique, the waste water lead concentration that electroplating effluent generates are also very high.Lead is nature Boundary is distributed one of the element being often used in very wide element and industry.Lead and soluble lead salt are all toxic, lead waste water pair Human health and animal and plant growth have serious harm.If every daily ingestion lead amount is more than 0.3-1.0mg, so that it may in human body inner product It is tired, cause anaemia, neuritis etc..With the rapid development of industrial technology, the heavy metal lead in industrial wastewater is as a kind of pollution Object, the discharge standard of clear stipulaties lead waste water is that lead always contains 1mg/L in national emission standard.Lead waste water comes from various batteries Workshop, dressing plant, petrochemical plant etc., battery industry are the main sources of lead waste water;It is reported that 1 battery of every production Lead loss 4.54-6810mg is resulted in, followed by petroleum industry produces gasoline additive.Although lead is common not as good as copper, cadmium, But it is the common ingredients in waste water.Especially Battery Plant generates a large amount of lead waste water in process of production, and Pb In Exhausted Water contains Amount exceeds hundred times of national standard, constitutes very big threat to underground water source, if arbitrarily discharged without processing, necessarily gives environment Great harm is brought with society.
In existing lead containing wastewater treatment technology, ion-exchange, the precipitation method, absorption method and electrolysis method be using it is more, More mature robust techniques.But there is also numerous deficiencies, such as electrolysis method, although the effect of removal heavy metal lead ion is also Well, but during processing, can consume a large amount of electric energy in the treatment process of especially a large amount of waste water, energy consumption compared with Greatly, it is difficult to meet the requirement for the energy-saving and emission-reduction advocated at present;The precipitation method, the precipitation method are commonly divided into chemical precipitation and physics again Precipitating, chemical precipitation are exactly that a large amount of alkali is added into waste water, make waste water in alkalinity, then generate the sediment of indissoluble, pass through It filters out, physical method is that flocculant is added into heavy metal-containing waste water, and flocculant is mostly colloid, largely similar using its surface Then charge adsorption heavy metal ion removes after gravitational settling through the methods of filtering;Ion-exchange and absorption method, although behaviour Make simply, energy consumption is small, but there is also problems ineffective when single method processing.
Summary of the invention
To solve the above problems, the present invention provides one kind, low energy consumption, and treatment process is simple and easy, to the place of heavy metal lead Reason works well, the lead containing wastewater treatment technique that the inorganic agent after handling waste water can be recycled.
To achieve the above object, The technical solution adopted by the invention is as follows:
A kind for the treatment of process of lead waste water, comprising the following steps:
One, waste water filtering;
Two, the pH value of waste water is adjusted to 6~7.5;
Three, 40~50kg/m is pressed3Additive amount adds modified montmorillonite used heavy metal absorbent, and Air Exposure 20 into waste water ~60 hours;
Four, the modified montmorillonite used heavy metal absorbent after being filtered to remove absorption heavy metal lead;
Five, treated, and waste water is discharged after the assay was approved.
Although main pollutant is heavy metal lead ion therein in lead waste water, inevitably had substantially in waste water Long-pending solid waste needs to remove, to prevent generating adverse effect to heavy metal lead treatment process later;Heavy metal lead is in acid Solubility highest in property environment, the weakly acidic pH environment that the pH value of waste water is adjusted to 6~7.5 before treatment can be in certain journey The content of the heavy metal lead in waste water is reduced on degree, while inexcessive adjusting pH makes waste water in alkalinity or strong basicity, in this way may be used To reduce the investment of aqueous slkali, the step of adjusting pH value again after wastewater treatment can also be reduced, simplifies technique;It is modified montmorillonite used When heavy metal absorbent processing, Air Exposure makes heavy metal absorbent and waste water one is be stirred effect using air-flow Contact increases, and two being to be passed through a large amount of oxygen thereto, can pass through some high oxygen demand pollutions in reaction removal waste water Object.
Preferably, modified montmorillonite used heavy metal absorbent is made by following steps:
A) Montmorillonite Purification prepares montmorillonite dispersion liquid by solid-liquid mass ratio after purification for 1:2~5;
B) addition hydroxy Al solion in the montmorillonite dispersion liquid prepared into step a, ultrasonic disperse 10~30 minutes Afterwards, solution is dry, intercalation modifying montmorillonite is made;Wherein the mass ratio of montmorillonite dispersion liquid and hydroxy Al solion is 1: 3~7;
C) intercalation modifying montmorillonite made from step b is roasted 1~1.5 hour at 300~450 DEG C;
D) in the sodium chloride solution that the intercalation modifying montmorillonite after step c roasting is added to 6mol/L, ultrasonic treatment 15~20 minutes, and modified montmorillonite used heavy metal absorbent is made after drying.
Montmorillonite is a kind of aluminium silicate mineral of stratiform, and interlayer has an exchangeable cations abundant, and due to Its interlayer structure having has certain absorption property, but since its interlamellar spacing is in 1nm or so, since its interlayer can be handed over The presence of ion is changed, the heavy metal ion that can be adsorbed is limited, needs to be modified it processing;Hydroxyl aluminium ion be it is a kind of with Aluminium ion is center ion, and numerous hydroxyls electrically surround the large-scale polymerization plasma group of aluminium ion formation due to ion band, can be with Stable presence in aqueous solution has abnormal excellent ion exchange since its outer layer has a large amount of hydroxyl to surround Performance, and the size of this kind of polymerization plasma group is suitable, it is close with the interlamellar spacing of montmorillonite, montmorillonite can be entered after processing Interlayer, and the montmorillonite of stratiform is strutted into certain distance, increases the interlamellar spacing of montmorillonite, pillared work is played between montmorillonite layer With, so that the absorption property of montmorillonite is become more excellent, can have more excellent absorption property, can also expand its absorption Adsorbate type;After high-temperature roasting, hydroxyl therein can remove, the hydroxyl aluminium ion of interlayer is made to become nano aluminium oxide, it will Montmorillonite interlayer structure struts, and expands interlamellar spacing.
Preferably, adjusting pH value using the acetic acid of 1mol/L and the potassium acetate of 1mol/L in step 2.
Preferably, then the Montmorillonite Purification processing in step a exists for montmorillonite is first ground to 400 mesh to 600 mesh Impregnate 20~30 minutes in 75% ethanol solution, impregnated 10~15 minutes in the hydrochloric acid that pH is 4.5~5 later, finally spend from Sub- water is dry after cleaning 1~3 time.
Montmorillonite Purification treatment process is successively impregnated in ethyl alcohol and hydrochloric acid, and having for montmorillonite surface attachment can be removed Machine object and impurity, especially HCl treatment can remove the inorganic impurity for being filled in montmorillonite duct and interlayer, be that it has more More adsorption spaces has stronger adsorption capacity.
Preferably, hydroxy Al solion is made by following methods: 0.003~0.03mol/L aluminium chloride is added to pH It is made for 7.5~8.5 sodium hydroxide solution, wherein control hydroxide ion and aluminum ions molar ratio are 1.8~2.5:1.
Preferably, modified montmorillonite used heavy metal absorbent can be in the chlorination of 5~7mol/L after adsorbing heavy metal lead Recycling is re-used for processing lead waste water after being ultrasonically treated 0.5~2.5 hour in sodium solution.
Preferably, heating rate when control intercalation modifying montmorillonite roasts is 1~5 DEG C/min, roasting in step c Temperature fall afterwards.
Slow heating rate can make the alumina crystal of modified montmorillonite used interlayer more complete.
Preferably, hydroxy Al solion is during the preparation process, liquor alumini chloridi is at the uniform velocity added in 18~24 minutes Into sodium hydroxide solution, and controlling temperature when addition is 70~90 DEG C.
Preferably, hydroxy Al solion is during the preparation process, liquor alumini chloridi was at the uniform velocity added to hydrogen in 20 minutes In sodium hydroxide solution, and controlling temperature when addition is 90 DEG C.
Although hydroxyl aluminium ion is a kind of polymerizing cationically group that can be stabilized, but during the preparation process if added The rate added it is excessively slow or it is too fast can all influence the aluminum ions formation of hydroxyl, also will affect and be formed by the aluminum ions stabilization of hydroxyl Property.
Therefore, the invention has the following advantages:
(1) waste water treatment process containing heavy metal lead in the present invention is simple, and excellent effect, waste water after processing can reach To discharge standard;
(2) modified montmorillonite used heavy metal absorbent manufacture craft employed in the present invention is simple and easy;
(3) modified montmorillonite used heavy metal absorbent employed in the present invention, can through simple process after having handled waste water To reuse.
Specific embodiment
Further description of the technical solution of the present invention With reference to embodiment.
Embodiment 1
A kind for the treatment of process of lead waste water, comprising the following steps:
One, waste water filtering;
Two, the pH value of waste water is adjusted to 7;
Three, 45kg/m is pressed3Additive amount adds modified montmorillonite used heavy metal absorbent into waste water, and Air Exposure 40 is small When;
Four, the modified montmorillonite used heavy metal absorbent after being filtered to remove absorption heavy metal lead;
Five, treated, and waste water is discharged after the assay was approved.
Wherein, modified montmorillonite used heavy metal absorbent is made by following steps:
A) montmorillonite is that 1:4 prepares montmorillonite dispersion liquid by solid-liquid mass ratio;
B) hydroxy Al solion is added in the montmorillonite dispersion liquid prepared into step a, ultrasonic disperse after twenty minutes, will Solution is dry, and intercalation modifying montmorillonite is made;Wherein the mass ratio of montmorillonite dispersion liquid and hydroxy Al solion is 1:5;Hydroxyl Base aluminium ion solution is made by following methods: 0.01mol/L aluminium chloride is added to the sodium hydroxide solution that pH is 8 and is made, wherein It controls hydroxide ion and aluminum ions molar ratio is 2.1:1;
C) intercalation modifying montmorillonite made from step b is roasted 1.3 hours at 370 DEG C;
D) in the sodium chloride solution that the intercalation modifying montmorillonite after step c roasting is added to 6mol/L, ultrasonic treatment 17 minutes, and modified montmorillonite used heavy metal absorbent is made after drying.
Embodiment 2
A kind for the treatment of process of lead waste water, comprising the following steps:
One, waste water filtering;
Two, the pH value of waste water is adjusted to 7;
Three, 45kg/m is pressed3Additive amount adds modified montmorillonite used heavy metal absorbent into waste water, and Air Exposure 40 is small When;
Four, the modified montmorillonite used heavy metal absorbent after being filtered to remove absorption heavy metal lead;
Five, treated, and waste water is discharged after the assay was approved;
Six, modified montmorillonite used heavy metal absorbent can surpass after adsorbing heavy metal lead in the sodium chloride solution of 6mol/L Recycling is re-used for processing lead waste water after sonication 1.5 hours.
Wherein, modified montmorillonite used heavy metal absorbent is made by following steps:
A) Montmorillonite Purification prepares montmorillonite dispersion liquid by solid-liquid mass ratio after purification for 1:4;Montmorillonite Purification is handled Montmorillonite is first ground to 500, is then impregnated in 75% ethanol solution 25 minutes, impregnates 13 in the hydrochloric acid that pH is 4.7 later Minute, it is dry after finally cleaning 2 times with deionized water;
B) hydroxy Al solion is added in the montmorillonite dispersion liquid prepared into step a, ultrasonic disperse after twenty minutes, will Solution is dry, and intercalation modifying montmorillonite is made;Wherein the mass ratio of montmorillonite dispersion liquid and hydroxy Al solion is 1:5;Hydroxyl Base aluminium ion solution is made by following methods: 0.01mol/L aluminium chloride is added to the sodium hydroxide solution that pH is 8 and is made, wherein It controls hydroxide ion and aluminum ions molar ratio is 2.1:1;
C) intercalation modifying montmorillonite made from step b is roasted 1.3 hours at 300~450 DEG C;
D) in the sodium chloride solution that the intercalation modifying montmorillonite after step c roasting is added to 6mol/L, ultrasonic treatment 17 minutes, and modified montmorillonite used heavy metal absorbent is made after drying.
Embodiment 3
A kind for the treatment of process of lead waste water, comprising the following steps:
One, waste water filtering;
Two, using the potassium acetate of the acetic acid of 1mol/L and 1mol/L, the pH value of waste water is adjusted to 6;
Three, 40kg/m is pressed3Additive amount adds modified montmorillonite used heavy metal absorbent into waste water, and Air Exposure 20 is small When;
Four, the modified montmorillonite used heavy metal absorbent after being filtered to remove absorption heavy metal lead;
Five, treated, and waste water is discharged after the assay was approved;
Six, modified montmorillonite used heavy metal absorbent can surpass after adsorbing heavy metal lead in the sodium chloride solution of 5mol/L Recycling is re-used for processing lead waste water after sonication 0.5 hour.
Wherein, modified montmorillonite used heavy metal absorbent is made by following steps:
A) Montmorillonite Purification prepares montmorillonite dispersion liquid by solid-liquid mass ratio after purification for 1:2;Montmorillonite Purification is handled Montmorillonite is first ground to 400 mesh, then impregnates in 75% ethanol solution 20 minutes, is impregnated in the hydrochloric acid that pH is 4.5 later It is 10 minutes, dry after finally cleaning 1 time with deionized water;
B) hydroxy Al solion is added in the montmorillonite dispersion liquid prepared into step a, ultrasonic disperse after ten minutes, will Solution is dry, obtained intercalation modifying montmorillonite, and the mass ratio of montmorillonite dispersion liquid and hydroxy Al solion is 1:3;Wherein, hydroxyl Base aluminium ion solution is made by following methods: 0.003mol/L aluminium chloride is added to the sodium hydroxide solution that pH is 7.5 and is made, Middle control hydroxide ion and aluminum ions molar ratio are 1.8:1, hydroxy Al solion during the preparation process, liquor alumini chloridi It is at the uniform velocity added in sodium hydroxide solution in 18 minutes, and controlling temperature when addition is 70 DEG C;
C) intercalation modifying montmorillonite made from step b is roasted 1 hour at 300 DEG C;Control the roasting of intercalation modifying montmorillonite The heating rate of burning is 1 DEG C/min, Temperature fall after roasting;
D) in the sodium chloride solution that the intercalation modifying montmorillonite after step c roasting is added to 6mol/L, ultrasonic treatment 15 minutes, and modified montmorillonite used heavy metal absorbent is made after drying.
Embodiment 4
A kind for the treatment of process of lead waste water, comprising the following steps:
One, waste water filtering;
Two, using the potassium acetate of the acetic acid of 1mol/L and 1mol/L, the pH value of waste water is adjusted to 7;
Three, 45kg/m is pressed3Additive amount adds modified montmorillonite used heavy metal absorbent into waste water, and Air Exposure 40 is small When;
Four, the modified montmorillonite used heavy metal absorbent after being filtered to remove absorption heavy metal lead;
Five, treated, and waste water is discharged after the assay was approved;
Six, modified montmorillonite used heavy metal absorbent can surpass after adsorbing heavy metal lead in the sodium chloride solution of 6mol/L Recycling is re-used for processing lead waste water after sonication 1.5 hours.
Wherein, modified montmorillonite used heavy metal absorbent is made by following steps:
A) Montmorillonite Purification prepares montmorillonite dispersion liquid by solid-liquid mass ratio after purification for 1:4;Montmorillonite Purification is handled Montmorillonite is first ground to 500 mesh, then impregnates in 75% ethanol solution 25 minutes, is impregnated in the hydrochloric acid that pH is 4.7 later It is 12 minutes, dry after finally cleaning 2 times with deionized water;
B) hydroxy Al solion is added in the montmorillonite dispersion liquid prepared into step a, ultrasonic disperse after twenty minutes, will Solution is dry, obtained intercalation modifying montmorillonite, and the mass ratio of montmorillonite dispersion liquid and hydroxy Al solion is 1:5;Wherein, hydroxyl Base aluminium ion solution is made by following methods: 0.01mol/L aluminium chloride is added to the sodium hydroxide solution that pH is 8 and is made, wherein Controlling hydroxide ion and aluminum ions molar ratio is 2.1:1, and during the preparation process, liquor alumini chloridi exists hydroxy Al solion It is at the uniform velocity added in sodium hydroxide solution in 21 minutes, and controlling temperature when addition is 80 DEG C;
C) intercalation modifying montmorillonite made from step b is roasted 1.3 hours at 370 DEG C;Control intercalation modifying montmorillonite The heating rate of roasting is 3 DEG C/min, Temperature fall after roasting;
D) in the sodium chloride solution that the intercalation modifying montmorillonite after step c roasting is added to 6mol/L, ultrasonic treatment 17 minutes, and modified montmorillonite used heavy metal absorbent is made after drying.
Embodiment 5
A kind for the treatment of process of lead waste water, comprising the following steps:
One, waste water filtering;
Two, using the potassium acetate of the acetic acid of 1mol/L and 1mol/L, the pH value of waste water is adjusted to 7.5;
Three, 50kg/m is pressed3Additive amount adds modified montmorillonite used heavy metal absorbent into waste water, and Air Exposure 60 is small When;
Four, the modified montmorillonite used heavy metal absorbent after being filtered to remove absorption heavy metal lead;
Five, treated, and waste water is discharged after the assay was approved;
Six, modified montmorillonite used heavy metal absorbent can surpass after adsorbing heavy metal lead in the sodium chloride solution of 7mol/L Recycling is re-used for processing lead waste water after sonication 2.5 hours.
Wherein, modified montmorillonite used heavy metal absorbent is made by following steps:
A) Montmorillonite Purification prepares montmorillonite dispersion liquid by solid-liquid mass ratio after purification for 1:5;Montmorillonite Purification is handled Montmorillonite is first ground to 600 mesh, is then impregnated in 75% ethanol solution 30 minutes, impregnates 15 in the hydrochloric acid that pH is 5 later Minute, it is dry after finally cleaning 3 times with deionized water;
B) hydroxy Al solion is added in the montmorillonite dispersion liquid prepared into step a, it, will after ultrasonic disperse 30 minutes Solution is dry, obtained intercalation modifying montmorillonite, and the mass ratio of montmorillonite dispersion liquid and hydroxy Al solion is 1:7;Wherein, hydroxyl Base aluminium ion solution is made by following methods: 0.03mol/L aluminium chloride is added to the sodium hydroxide solution that pH is 8.5 and is made, Middle control hydroxide ion and aluminum ions molar ratio are 2.5:1, hydroxy Al solion during the preparation process, liquor alumini chloridi It is at the uniform velocity added in sodium hydroxide solution in 24 minutes, and controlling temperature when addition is 90 DEG C;
C) intercalation modifying montmorillonite made from step b is roasted 1.5 hours at 450 DEG C;Control intercalation modifying montmorillonite The heating rate of roasting is 5 DEG C/min, Temperature fall after roasting;
D) in the sodium chloride solution that the intercalation modifying montmorillonite after step c roasting is added to 6mol/L, ultrasonic treatment 20 minutes, and modified montmorillonite used heavy metal absorbent is made after drying.
Following technical indicator may be implemented through the invention:
Through lead content≤0.1mg/L in treated the lead waste water of the treatment process in the present invention.

Claims (6)

1. a kind for the treatment of process of lead waste water, it is characterised in that the following steps are included:
One, waste water filtering;
Two, the pH value of waste water is adjusted to 6~7.5;
Three, 40~50kg/m is pressed3Additive amount adds modified montmorillonite used heavy metal absorbent, and Air Exposure 20~60 into waste water Hour;
Four, the modified montmorillonite used heavy metal absorbent after being filtered to remove absorption heavy metal lead;
Five, treated, and waste water is discharged after the assay was approved;
The modified montmorillonite used heavy metal absorbent is made by following steps:
A) Montmorillonite Purification prepares montmorillonite dispersion liquid by solid-liquid mass ratio after purification for 1:2~5;
B) hydroxy Al solion is added in the montmorillonite dispersion liquid prepared into step a, it, will after ultrasonic disperse 10~30 minutes Solution is dry, and intercalation modifying montmorillonite is made;Wherein the mass ratio of montmorillonite dispersion liquid and hydroxy Al solion is 1:3~7;
C) intercalation modifying montmorillonite made from step b is roasted 1~1.5 hour at 300~450 DEG C;
D) in the sodium chloride solution that the intercalation modifying montmorillonite after step c roasting is added to 6mol/L, ultrasonic treatment 15~ 20 minutes, and modified montmorillonite used heavy metal absorbent is made after drying;
The hydroxy Al solion is made by following methods: 0.003~0.03mol/L aluminium chloride be added to pH be 7.5~ 8.5 sodium hydroxide solution is made, wherein control hydroxide ion and aluminum ions molar ratio are 1.8~2.5:1;
During the preparation process, liquor alumini chloridi was at the uniform velocity added to sodium hydroxide in 18~24 minutes to the hydroxy Al solion In solution, and controlling temperature when addition is 70~90 DEG C.
2. a kind for the treatment of process of lead waste water according to claim 1, it is characterised in that: used in the step 2 The acetic acid of 1mol/L and the potassium acetate of 1mol/L adjust pH value.
3. a kind for the treatment of process of lead waste water according to claim 1, it is characterised in that: the illiteracy in the step a is de- Stone purification processes are that montmorillonite is first ground to 400 mesh to 600 mesh, are then impregnated 20~30 minutes in 75% ethanol solution, it It is impregnated 10~15 minutes in the hydrochloric acid that pH is 4.5~5 afterwards, it is dry after finally cleaning 1~3 time with deionized water.
4. a kind for the treatment of process of lead waste water according to claim 1, it is characterised in that: described is modified montmorillonite used heavy Metal absorbent recycles after being ultrasonically treated 0.5~2.5 hour in the sodium chloride solution of 5~7mol/L after adsorbing heavy metal lead It is re-used for processing lead waste water.
5. a kind for the treatment of process of lead waste water according to claim 1, it is characterised in that: in the step c, control is inserted Heating rate when the modified montmorillonite used roasting of layer is 1~5 DEG C/min, Temperature fall after roasting.
6. a kind for the treatment of process of lead waste water according to claim 1, it is characterised in that: the hydroxy Al solion During the preparation process, liquor alumini chloridi is at the uniform velocity added in sodium hydroxide solution in 20 minutes, and controls temperature when addition It is 90 DEG C.
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聚羟基铝柱撑蒙脱石吸附重金属离子实验研究;刘云等;《矿物岩石》;200509;第25卷(第3期);122-126

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