CN109879375A - A kind of indigo use in waste water treatment anode plate preparation method - Google Patents
A kind of indigo use in waste water treatment anode plate preparation method Download PDFInfo
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Abstract
The present invention relates to electrochemical treatments technical fields, especially a kind of indigo use in waste water treatment anode plate preparation method, by the material component in anode plate preparation process is added in a certain order, melted so that the biggish lead composition of specific gravity is melt into liquid first and then successively aluminium, calcium and strontium are added, and by stirring, it realizes and is uniformly mixed, reduce anode board raw material mixing difficulty, reduce anode plate preparation cost, and ensure that anode plate excellent combination property, improve quality.
Description
Technical field
The present invention relates to electrochemical treatments technical field, especially a kind of indigo use in waste water treatment anode plate preparation method.
Background technique
With in the fast development process of the industrial sectors such as chemical engineering industry, metallurgical industry, New-type adjuvant, pharmacy etc. chemistry
The addition of substance causes large amount of organic ingredient to enter in waste water, causes waste component and structure change complicated, and these
Organic components are mixed into, and due to its bio-toxicity and difficult for biological degradation performance, so that gradually accumulating in the environment, cause environment
By serious pollution, high degree threatens human survival safety.
Currently, for the processing method of hardly degraded organic substance in waste water, there are many kind, such as supercritical water oxidations, photocatalysis
Method, ultrasonic method, Fenton reagent method, microwave method, electrochemical method etc., wherein with electrochemical method have it is easy to operate, be convenient for
Automation control, reaction condition are mild, without secondary pollution, post-processing is simple, and can combine with other processing methods, and
There is efficient degradation capability to hardly degraded organic substance, and in organic pollutant degradation treatment process, without adding other examinations
Agent belongs to Green Chemistry process, becomes current wastewater treatment research hotspot.In electrochemical treatments organic pollutant degradation process
In, the surface properties for the anode material being mainly subject to, electrochemical reactor configuration, the physico-chemical property of organic matter, solution state
Etc. factors influence, therefore, quick research and development has been obtained with anode material for electrochemical catalytic oxidation degradation of organic substances,
Such as: in the electrode material for the organic wastewater treatment by electrochemical electrolytic engineering that number of patent application is 201711140416.3, with four
First alloy is anode, and graphite is cathode, constitutes chopped-off head electrolysis system, and the mode of sacrificial anode induces iron ion and aluminum ionsization
Activity is learned, a large amount of micro cell is quickly formed, meanwhile, the particulate matter for constituting coloration can be generated ferric hydroxide colloid cohesion
Agent adsorption-condensation and be removed, wherein the quaternary alloy ingredient calcic used is 0.3-0.5% weight content, aluminium 0.5-1%
Weight content, tin are 20-30% weight content, remaining is lead, and being aided with current density is 0.1-0.2Acm-2;When electrolysis
Between be 45min;Fe/Al bimetallic assists Treatment of Wastewater by Electrolysis, and under the conditions of pH value is 5-10, decomposition voltage reaches 10-15V
Under the conditions of realize organic wastewater electrolysis processing so that percent of decolourization can reach 99%, COD in electrolysis jeans bipseudoindoxyl dye sewage
Removal rate has reached 84%.
But in the prior art, for quaternary alloy electrode material in preparation process, since treatment process is inappropriate,
Lead to the comprehensive performances inferior qualitys such as hardness, tensile strength and the resistivity of the quaternary alloy electrode material that are prepared, makes
At for handle indigo pollutant effluents etc. be difficult to the organic principle degraded degradation removal effect it is undesirable.
In consideration of it, this researcher combines long-term exploratory experiment and prepares the indigo mode for polluting sewage by laboratory
As test object, and in quaternary alloy electrode material preparation process technological parameter and material addition sequence control
System provides new approaches for the preparation of quaternary alloy electrode material.
Summary of the invention
In order to solve the above technical problems existing in the prior art, the present invention provides a kind of indigo use in waste water treatment anode
Plate preparation method.
It is achieved particular by following technical scheme:
Indigo use in waste water treatment anode plate preparation method, comprising the following steps:
(1) lead is added in graphite crucible, heating fusing forms molten liquid;
(2) control molten liquid is at 750-850 DEG C, and aluminium is added by 1.2-2.7% weight content thereto, and constant temperature is primary
Melting after being melt into liquid completely to aluminium, obtains metal liquid;
(3) controlled at 750-850 DEG C, calcium is added by 0.1-0.28% weight content thereto and presses 17-19%
Strontium is added in weight content, and constant temperature stirs secondary smelting, and casting ingot-forming is forged and rolled, and punching is to get indigo use in waste water treatment anode plate.
By the material component in anode plate preparation process is added in a certain order so that the biggish lead composition of specific gravity first by
It is melt into liquid and then successively aluminium, calcium and strontium is added and melt, and by stirring, realize and be uniformly mixed, reduce anode plate
Raw material mixes difficulty, reduces anode plate preparation cost, and ensure that anode plate excellent combination property, improves quality.
In order to avoid the small calcium of specific gravity, strontium swim in metallic solution surface, cause preparation product quality and performance compared with
The defect of difference, it is preferable that the step (3) is added in calcium, strontium adition process using plunging.
The biggish defect of amount of oxidation loss after being added in order to avoid Al, it is preferable that the step (2), in the addition of aluminium
In the process, using addition accounts for the carbon dust of metal liquid quality 1.2-2% thereto in plunging addition or adition process.
Gas entrance can be effectively obstructed, while causing scaling loss amount larger, additionally it is possible to guarantee the performance of the product of preparation,
Improve quality, it is preferable that the carbon dust, additional amount account for the 1.8% of metal liquid quality.
The secondary smelting time is 10-15min.
The indigo use in waste water treatment anode plate of above method preparation using Fe/Al for being pressed when handling indigo pollutant effluents
It is that assistance electrolysis processing is added in 1:0.2-0.8 bimetallic according to mass ratio
It is treated in journey to indigo pollutant effluents, is to be negative with quaternary alloy material for positive (anode), graphite
The electrolysis system of pole (cathode) composition, in the quaternary alloy material, calcium is 0.1-0.28% weight content, aluminium 1.2-
2.7% weight content, strontium are 17-19% weight content, surplus is lead.
It is anode, the electrolysis system that form as cathode of graphite using quaternary alloy material, and then sacrifices the side of anode (anode)
Formula induces aluminum ions chemical activity, quickly forms a large amount of micro cell, improves to the hardly degraded organic substance in organic wastewater
Degradation capability, and aluminium ion quickly forms alumine hydroxide colloid, and this colloid has stronger absorption property, can be a large amount of
Cohesion absorption organic wastewater in color, improve to the percent of decolourization of organic wastewater.
In order to reduce the COD content in organic wastewater, percent of decolourization is improved, it is preferable that in the quaternary alloy material, calcium is
0.23% weight content, aluminium are 2.5% weight content, strontium is 18% weight content, surplus is lead.
In order to further decrease the COD content in organic wastewater, percent of decolourization is improved, it is preferable that the quaternary alloy material
In, calcium is 0.17% weight content, aluminium is 1.8% weight content, strontium is 17% weight content, surplus is lead.
The electrode material of the invention can enhance the processing capacity to organic wastewater under electrolytic condition appropriate,
COD content is reduced, percent of decolourization is improved, so that for during handling organic wastewater, being to assist electrolysis using Fe, Al bimetallic
Waste water controls pH value of waste water under the conditions of 5-10, and decomposition voltage 10-15V, electrolysis time control are close in 50-60min, electric current
Degree is 0.1-0.2Acm-2.High degree makes COD removal efficiency improve 3-5 percentage points.Especially electricity is assisted in bimetallic
During solving waste water, so that the formation of a large amount of micro cell, and iron, aluminum ions chemical activity are strengthened, so that quick shape
It at the colloid that iron hydroxide, aluminium hydroxide mix, and quickly agglomerates, enhancing improves the color adsorption capacity in organic wastewater
Decoloring ability.
In order to make the relative amount of the aluminium hydroxide to be formed, iron hydroxide complex colloid be in mixing ratio appropriate
Range, it is ensured that can preferably enhance and ability is removed to the color in organic wastewater, it is preferable that the electrode material is for locating
It is according to mass ratio using Fe, Al bimetallic to assist electrolysis wastewater after 1:0.2-0.8 mixing during managing organic wastewater,
PH value of waste water is controlled under the conditions of 5-10, decomposition voltage 13V, electrolysis time control are in 55min, current density 0.15A
cm-2。
It is further preferred that Fe, Al bimetallic, is 1:0.6 mixing assisting electrolysis wastewater process to be according to mass ratio.
In order to avoid the ingredients such as more low-gravity strontium, calcium after being added in smelting furnace, swims in and smelt solution table
Face causes the performance of the quaternary alloy material obtained poor, and then causes to the lower defect of COD removal efficiency in organic wastewater,
It is preferred that the strontium is added and is smelted using plunging after mixing strontium with calcium.
The invention during preparing electrode material, quaternary alloy material be by buy in the market post-processing at
Anode plate (positive plate), or form by oneself melting, wherein smelting technology technique referring to disclosed in the prior art, example
Such as: lead is heated up in graphite crucible fusing melting, and in fusion process, a small amount of carbon dust and Al material is added, to Al material
Material is smelted into after metal liquid, and solvent is added thereto and calcium, strontium material composition carry out secondary smelting, is uniformly mixed,
Casting ingot-forming is forged and rolls, is punching into anode plate (positive plate).
By calcium, strontium ingredient are added in final step, amount of oxidation loss can be effectively reduced, using graphite crucible,
Help to reduce cost, improves the chemical property stability for the treatment of process, and mix using carbon dust with Al material and melting, energy is added
Alloy air-breathing and oxidization burning loss are enough effectively reduced, during the addition process, the additional amount control of carbon dust is accounting for aluminium alloy weight
Be when 1.8% it is best, can aid in improve electrode material as anode plate processing organic wastewater when organic matter degradation ability;
Under the premise of guaranteeing alloy material quality, the amount of oxidation loss of aluminium alloy is reduced, especially control is added in calcium, strontium ingredient
Smelting time later is especially advisable in 15min with 13min;The temperature of entire fusion process is between 750-850 DEG C;?
Casting before stirring, help to improve the uniformity of metal melting body, at the same can be avoided the materials such as the biggish lead of specific gravity it is excessive under
It is heavy, cause the material quality of preparation poor.Above-mentioned preparation process helps to improve hardness, tensile strength and the resistance of alloy material
Rate etc., so that for carrying out electrochemical treatment process, the drop of high degree improved to organic pollutant to organic wastewater
Solution ability;And good assistance can be formed with bimetallic, enhance in organic wastewater COD removal efficiency and color remove
Rate.
Specific embodiment
It is limited below with reference to the embodiment of specific test operation process technical solution of the present invention is further
It is fixed, but claimed range is not only limited to made description.
In certain embodiments, indigo use in waste water treatment anode plate preparation method, comprising the following steps:
(1) lead is added in graphite crucible, heating fusing forms molten liquid;
(2) control molten liquid is at 750-850 DEG C, and aluminium is added by 1.2-2.7% weight content thereto, and constant temperature is primary
Melting after being melt into liquid completely to aluminium, obtains metal liquid;
(3) controlled at 750-850 DEG C, calcium is added by 0.1-0.28% weight content thereto and presses 17-19%
Strontium is added in weight content, and constant temperature stirs secondary smelting, and casting ingot-forming is forged and rolled, and punching is to get indigo use in waste water treatment anode plate.
In certain embodiments, the step (3) are added in calcium, strontium adition process using plunging.
In certain embodiments, the step (2) are added or are added using plunging in the adition process of aluminium
The carbon dust for accounting for metal liquid quality 1.2-2% is added thereto in the process.
In certain embodiments, the carbon dust, additional amount account for the 1.8% of metal liquid quality.
In certain embodiments, the secondary smelting time is 10-15min.
In certain embodiments, the aluminium is added according to 1.8% weight content;Calcium is contained according to 0.17% weight
Amount is added;Strontium is added according to 17% weight content, and surplus is lead.
In certain embodiments, the aluminium is added according to 2.5% weight content;Calcium is contained according to 0.23% weight
Amount is added;Strontium is added according to 18% weight content, and surplus is lead.
In certain embodiments, the indigo use in waste water treatment anode plate of above method preparation is for handling indigo pollutant effluents
When, it uses Fe/Al to be added according to mass ratio for 1:0.2-0.8 bimetallic and assists electrolysis processing.
This research is research object by preparing bipseudoindoxyl dye pollutant effluents, using electrochemistry during experimental study
Method carries out indigo pollutant effluents processing.The original COD for the indigo waste water being wherein configured toCrFor 3785mg/L, chromatic value is
2439.Be configured to dye discoloration waste water as the reason of research object using bipseudoindoxyl dye to be: there is bipseudoindoxyl dye chemistry to need
Oxygen amount is high, colour fading difficulty is larger, and the difficulty for the post-processing for pollute to waste water compared to other pollutants is larger.The invention
Specifically in the course of the research, it is to be carried out according to following tests step and method:
(1) prepared by quaternary alloy anode plate material
Leady raw materials are placed in graphite crucible after heating fusing, adjustment temperature is once to be melted between 750-850 DEG C
Refining processing, and in melting once treatment process, aluminium is added according to 1.2-2.7% weight content thereto and accounts for molten metal constitution
The carbon dust of amount 1.8%, so that it is smelted into after metal liquid completely, control smelting temperature is constant, and calcium, strontium raw material are pressed respectively
It after 0.1-0.28% weight content and the mixing of 17-19% weight content, is added using plunging, stirring secondary smelting processing
10-15min, and ingot is cast it into, it forges and rolls, punching obtains anode plate electrode material.In above-mentioned preparation process, other are not
Matters to the greatest extent are handled referring to preparation processing method in the prior art, not detailed matters, referring to phase in art technology
Pass technology is operated, such as: calcium, strontium material is added in plunging, is referred to the similar quaternary alloy such as related PbAgCaSr
Operating method in anode plate preparation flow is handled.
This experiment is specifically in the operating process of above-mentioned preparation method, in quaternary alloy anode plate material preparation process
Parameter makes following accurate adjusting with after variation, is prepared into different quaternary alloy electrode materials, shown in table 1 specific as follows:
Table 1
It carries out hardness, tensile strength, resistivity to sample prepared by table 1 to detect, result is as shown in table 2 below:
Table 2
It is shown by upper 2 data of table as it can be seen that different for each material composition additional amount, it will high degree affects preparation
Quaternary alloy electrode material performance, the invention choose additional amount within the scope of, can effectively enhance hardness
And tensile strength, reduce resistivity;In order to further verify in the invention operating method, prepared by quaternary alloy
Processing step in technique influences situation, this researcher in the course of the research, based on the sample 5 of preparation, and will prepare work
Skill step makes following adjustment:
Trial target: sample 5;
Reference substance: being prepared according to 5 preparation method of sample, and calcium, strontium raw material do not use plunging during the preparation process
It is added, is added according to the method for being routinely added to.
Reference substance is detected using the hardness, tensile strength and Resistivity testing method of the invention, is tied
Fruit shows: the hardness of reference substance is 14.98Hv, tensile strength 5.47kg/mm2, resistivity is 0.216 Ω mm.To sum up, right
During the preparation process, whether plunging is used to be added calcium, strontium raw material, it will the sample of the influence preparation of high degree
Quality.The plunging of use is referring to the methods of plunging in related packet in the prior art or other industrial chemicals feeding methods
It is operated.
In order to enhance the comprehensive performance of quaternary alloy electrode material, this researcher with better chemical property
During above-mentioned quaternary alloy material preparation research, carried out on the basis of 5 preparation method of sample, and to its technological parameter
Corresponding adjustment, and its corresponding hardness and tensile strength, resistivity are detected, as the result is shown: according to 5 preparation method of sample
Preparation is sample when calcium is 0.23% weight content, aluminium is 2.5% weight content, strontium is 18% weight content, surplus is lead
The quaternary alloy anode plate material of product 8: hardness 22.34Hv, tensile strength 7.43kg/mm2, resistivity is 0.157 Ω
mm;It is sample 9 when calcium is 0.17% weight content, aluminium is 1.8% weight content, strontium is 17% weight content, surplus is lead
Quaternary alloy electrode material: hardness 22.35Hv, tensile strength 7.41kg/mm2, resistivity is 0.153 Ω mm.
(2) quaternary alloy material is anode, graphite is the indigo Wastewater of electrolyte
The quaternary alloy anode plate material being prepared using above-mentioned preparation method be positive pole, graphite be electrolyte it is indigo
Waste water, specific test operation process are as described below:
Electrolytic cell group is at situation, as shown in table 3 below, when electrolysis: assisting according to the bimetallic that Fe/Al mass ratio is 1:1 mixing
Electrolysis is helped, controls pH value of waste water under the conditions of 5, decomposition voltage 10V, electrolysis time control are in 50min, current density
0.1A·cm-2。
Table 3
It is shown by the data of table 3 as it can be seen that the material composition for quaternary alloy anode plate material forms difference, it will right
When the quaternary alloy anode plate material is used to be electrolysed organic wastewater, removes COD and decoloring ability causes different degrees of influence, and
The invention is passed through to be adjusted in the raw material composition to quaternary alloy material, and combines the system of quaternary alloy anode plate material
Standby technique is prepared into anode plate (anode), so that being used for being electrolysed indigo waste water, can effectively reduce the content of COD, mention
High percent of decolourization.
In addition to this, on the basis of above-mentioned test group 8, this researcher pass through to the current density range of experimentation,
The influence to COD removal efficiency such as electrolysis time, pH value has carried out exploratory experiment, as follows as the result is shown:
Current density: trial stretch is from 0.1Acm-2According to 0.01Acm-2Incremental amplitude be gradually increased, and survey
COD removal efficiency situation is tried, as the result is shown: being 0.1-0.2Acm in current density-2Between range, with the increasing of current density
Greatly, COD removal rate is gradually increased, and speedup is larger, and increases to 0.2Acm in current density-2When above, COD removal
The speed that rate increases gradually decreases, and electrolytic efficiency is decreased obviously, and as current density is gradually increased, energy consumption is remarkably reinforced,
The electrode material proportion of goods damageds obviously increase;And pass through and in test the color throw of organic wastewater is observed and detected simultaneously,
As the result is shown are as follows: current density be 0.1-0.2Acm-2Between, COD removal efficiency is gradually increased, and electrolytic efficiency is higher, and
And it is higher to the percent of decolourization of organic wastewater, it is especially 0.15Acm in current density-2When, make the percent of decolourization to waste water
Highest can reach 99.6% or so, and also relatively high to the removal efficiency of COD, maintain 85.1 or so.
Electrolysis time: taking multiple electrolysis to handle, and measures the amplification size feelings that COD in different time sections is electrolysed removal rate
Condition, and then electrolytic efficiency is measured, and obtained through overtesting: when electrolysis time is within 35min, COD removal rate is presented substantially
The ascendant trend of degree, and when reaching 40min for electrolysis time, COD removal rate only maintain 84.1% or so, and after reneing
Long electrolysis time, and the electrolysis power consumption situation for extending this period is counted, as the result is shown: the electricity for extending this period
When the ratio of solution, COD removal rate value added and electrolysis power consumption value is only 35min than electrolysis time, COD removal rate increases
When being worth 1-5% low with the electrolysis ratio of power consumption value, and reaching 60min or more for extending electrolysis time, COD removal rate increases
The value added ratio with electrolysis power consumption value significantly reduces, and causes a large amount of energy consumption, and the variation of COD removal efficiency speedup compared with
Difference.As it can be seen that being maintained within 60min for electrolysis time, it will help to reduce electrolysis energy consumption, reduce cost for wastewater treatment.
And it is longer according to electrolysis time, COD removal efficiency is higher and higher, obtains: should control electrolysis time between 50-60min.
PH value: being unobvious in the influence that the range of 5-10 is fluctuated to waste water COD;But occur in strong basicity waste water anti-
It answers, is quickly generated Fe (OH)2With Al (OH)3Precipitating hinders the progress of deoxidization, degradation reaction;It is bis- to be conducive to Fe/Al in acid condition
Metal handles organic matter, but since electrolysis method accounts for leading role in the treatment of waste water, strong acidic condition does not have really
Help electrolysis system to be persistently normally carried out, the Fe because under strongly acidic conditions, in waste water2+Dense, iron filings surface is easy hair
Raw passivation influences treatment effect, therefore Fe/Al bimetallic assists Treatment of Wastewater by Electrolysis, and effect is handled under the conditions of pH value is in 5-10
Fruit is relatively preferable.Especially when pH value is 6, COD removal efficiency and percent of decolourization are higher, and COD removal efficiency can reach for control
85% or more, percent of decolourization has reached 99.3% or more.
During above-mentioned test, the voltage of use is according to the voltage model used in those skilled in the art's routine test
It encloses, such as 1-30V, and by during the test, having adjusted the test of corresponding voltage value range, as a result showing
Show, the COD for facilitating electrolysis wastewater in 10-15V is removed, and is passed through during voltage adjustment, by controlling voltage
Two groups of comparative tests of Fe/Al bimetallic are not added by addition and in 10-15V, equally controlled in voltage in 1-10V, 15-30V
Deng range adjustment under, be added and do not add two groups of comparative tests of Fe/Al bimetallic, as the result is shown: being 1-10V in voltage
Between 15-30 in change procedure, addition assists the COD removal efficiency influential effect of electrolysis processing little with bimetallic is not added;
And voltage control in change procedure, is added by bimetallic, electrolysis is assisted to assist to be electrolysed than not adding bimetallic between 10-15V
The COD removal efficiency effect of processing is preferable, and removal efficiency is enabled to have apparent amplification;It can be seen that for using electricity
Voltage-controlled system is between 10-15V, it will facilitates Fe/Al bimetallic and assists electrolysis wastewater, removes COD.
(3) difference Fe/Al, which is added, assists to be electrolysed indigo Wastewater than bimetallic
On the basis of above-mentioned test group 8, this researcher carries out the mixing of Fe/Al difference according to the test method of test group 8
Mass ratio is added in electrolysis system, is formed bimetallic and is assisted to be electrolysed indigo pollutant effluents, and is electrolysed to different addition mass ratioes
The COD removal efficiency and percent of decolourization of indigo pollutant effluents are detected, and result is as shown in table 4 below:
Table 4
Show that Fe/Al mixing ratio additional amount will as it can be seen that assisting in electrolytic process for Fe/Al bimetallic by the data of table 4
Different degrees of influence can be caused to COD removal efficiency, hence it is evident that it is seen that: for being added than control between 1:0.2-0.8,
COD removal efficiency is more excellent, and little for the influence degree of percent of decolourization.
In the course of the research, carbon dust is added in graphite crucible by this researcher, can effectively be covered on molten liquid
In dignity, so that molten metal and air exclusion, reduce alloy air-breathing and oxidization burning loss, but, it is different in carbon dust additional amount
In the case of, pushing gravity when carbon dust is covered on molten liquid surface is completely not identical, therefore molten liquid surface can
Just covering, and be not easy to be pressed into inside melt liquid under self gravitation effect, it will it is to influence anode plate synthesis
The key factor of performance indicator, in consideration of it, whether this researcher during preparing anode plate, is added carbon dust, additional amount
How much to have carried out following Adjustment Tests, and the integrated performance index for the sample that corresponding test group obtains is had detected, result is such as
Shown in the following table 5:
The test of table 5 is carried out on the basis of the preparation of above-mentioned sample 8.
The difference as it can be seen that for carbon dust additional amount is shown by the data of table 5, it will to the synthesis of the anode panel products of preparation
Performance causes different degrees of influence, and for the control of carbon dust additional amount between the zone of reasonableness between 1.2-2%, it will have
Help improve anode plate comprehensive performance quality, reduce resistivity, improves tensile strength and hardness.
In the invention, the additional amount for carbon dust be by Pb be melt into liquid after quality in terms of, and for Al,
Ca, Sr etc. are measured with quaternary alloy total weight.
The foregoing is only a preferred embodiment of the present invention, but scope of protection of the present invention is not limited thereto,
Anyone skilled in the art in the technical scope disclosed by the present invention, according to the technique and scheme of the present invention and its
Inventive concept is subject to equivalent substitution or change, should be covered by the protection scope of the present invention.
Claims (10)
1. a kind of indigo use in waste water treatment anode plate preparation method, which comprises the following steps:
(1) lead is added in graphite crucible, heating fusing forms molten liquid;
(2) control molten liquid is at 750-850 DEG C, and aluminium is added by 1.2-2.7% weight content thereto, and constant temperature once melts
Refining, after being melt into liquid completely to aluminium, obtains metal liquid;
(3) controlled at 750-850 DEG C, calcium is added by 0.1-0.28% weight content thereto and presses 17-19% weight
Strontium is added in content, and constant temperature stirs secondary smelting, and casting ingot-forming is forged and rolled, and punching is to get indigo use in waste water treatment anode plate.
2. indigo use in waste water treatment anode plate preparation method as described in claim 1, which is characterized in that the step (3),
In calcium, strontium adition process, it is added using plunging.
3. indigo use in waste water treatment anode plate preparation method as described in claim 1, which is characterized in that the step (2),
In the adition process of aluminium, metal liquid quality 1.2-2% is accounted for using being added thereto in plunging addition or adition process
Carbon dust.
4. indigo use in waste water treatment anode plate preparation method as claimed in claim 3, which is characterized in that the carbon dust adds
Enter amount accounts for metal liquid quality 1.8%.
5. indigo use in waste water treatment anode plate preparation method as described in claim 1, which is characterized in that the secondary smelting
Time is 10-15min.
6. indigo use in waste water treatment anode plate preparation method as described in claim 1, which is characterized in that the aluminium, be by
It is added according to 1.8% weight content;Calcium is added according to 0.17% weight content;Strontium is added according to 17% weight content, remaining
Amount is lead.
7. indigo use in waste water treatment anode plate preparation method as claimed in claim 6, which is characterized in that the anode plate,
Hardness is 22.35Hv, tensile strength 7.41kg/mm2, resistivity is 0.153 Ω mm.
8. indigo use in waste water treatment anode plate preparation method as described in claim 1, which is characterized in that the aluminium, be by
It is added according to 2.5% weight content;Calcium is added according to 0.23% weight content;Strontium is added according to 18% weight content, remaining
Amount is lead.
9. indigo use in waste water treatment anode plate preparation method as claimed in claim 8, which is characterized in that the anode plate,
Hardness is 22.34Hv, tensile strength 7.43kg/mm2, resistivity is 0.157 Ω mm.
10. if the indigo use in waste water treatment anode plate of the described in any item method preparations of claim 1-9 is for handling indigo dirt
When contaminating waste water, uses Fe/Al to be added according to mass ratio for 1:0.2-0.8 bimetallic and assist electrolysis processing.
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Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1076058A (en) * | 1992-02-29 | 1993-09-08 | 山东省文登市密闭蓄电池厂 | Positive-negative electrode plate grid allog material for sealed lead-acid battery |
CN107673448A (en) * | 2017-11-16 | 2018-02-09 | 贵州省新材料研究开发基地 | A kind of electrode material of organic wastewater treatment by electrochemical electrolytic engineering |
CN107758809A (en) * | 2017-11-16 | 2018-03-06 | 贵州省新材料研究开发基地 | A kind of method that bimetallic assists electric treatment organic wastewater |
CN108808010A (en) * | 2018-06-12 | 2018-11-13 | 河北超威电源有限公司 | A kind of Moped Scooter positive electrode grid of lead storage battery alloy and preparation method thereof |
-
2019
- 2019-02-24 CN CN201910134882.3A patent/CN109879375A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1076058A (en) * | 1992-02-29 | 1993-09-08 | 山东省文登市密闭蓄电池厂 | Positive-negative electrode plate grid allog material for sealed lead-acid battery |
CN107673448A (en) * | 2017-11-16 | 2018-02-09 | 贵州省新材料研究开发基地 | A kind of electrode material of organic wastewater treatment by electrochemical electrolytic engineering |
CN107758809A (en) * | 2017-11-16 | 2018-03-06 | 贵州省新材料研究开发基地 | A kind of method that bimetallic assists electric treatment organic wastewater |
CN108808010A (en) * | 2018-06-12 | 2018-11-13 | 河北超威电源有限公司 | A kind of Moped Scooter positive electrode grid of lead storage battery alloy and preparation method thereof |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113233548A (en) * | 2021-03-25 | 2021-08-10 | 上海应用技术大学 | Electrochemical-supported chloride ion capturing method and device |
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