CN109354252A - A kind of processing method of Sewage from Sulphuric Acid Plants - Google Patents

A kind of processing method of Sewage from Sulphuric Acid Plants Download PDF

Info

Publication number
CN109354252A
CN109354252A CN201811427663.6A CN201811427663A CN109354252A CN 109354252 A CN109354252 A CN 109354252A CN 201811427663 A CN201811427663 A CN 201811427663A CN 109354252 A CN109354252 A CN 109354252A
Authority
CN
China
Prior art keywords
sewage
sulphuric acid
acid plants
neutralization reaction
processing method
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201811427663.6A
Other languages
Chinese (zh)
Inventor
陶政修
龙浩
覃宝桂
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
CHINA TIN GROUP Co Ltd
Original Assignee
CHINA TIN GROUP Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by CHINA TIN GROUP Co Ltd filed Critical CHINA TIN GROUP Co Ltd
Priority to CN201811427663.6A priority Critical patent/CN109354252A/en
Publication of CN109354252A publication Critical patent/CN109354252A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • 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
    • C02F2101/101Sulfur compounds
    • 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
    • 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
    • C02F2101/203Iron or iron compound

Abstract

The invention discloses a kind of processing methods of Sewage from Sulphuric Acid Plants, belong to technical field of sewage.The processing method of the Sewage from Sulphuric Acid Plants, includes the following steps: step 1: continuous neutralization reaction;Step 2: being separated by solid-liquid separation.The present invention is with H2SO4The Sewage from Sulphuric Acid Plants that concentration is 10g/L~300g/L is process object, using agstone as neutralizer, is continuously neutralized, and for obtained neutralized reaction product after filter is separated by solid-liquid separation, obtained solid is industrial gypsum, for sale;After obtained filtered fluid otherwise processed recycles valuable metal therein, then externally discharges or return other production stations and recycle.The processing method of Sewage from Sulphuric Acid Plants of the invention, can output qualification gypsum product, be finally reached the purpose of Sewage from Sulphuric Acid Plants progress resource utilization, have many advantages, such as that process flow is short, production cost is low, the stacking and problem of management of not no melting waste slag.

Description

A kind of processing method of Sewage from Sulphuric Acid Plants
Technical field
The present invention relates to a kind of processing methods of Sewage from Sulphuric Acid Plants, belong to technical field of sewage.
Background technique
In the production process of the nonferrous metal products such as copper, lead, zinc, the sulfur dioxide flue gas of high concentration before Sulphuric acid, It requires to carry out washing, purifying to flue gas, to remove the dust in flue gas.A small amount of sulfur dioxide in washing, purifying, in flue gas It is dissolved in cleaning dust water, forms sulfurous acid, sulfurous acid is dissolved in the dioxygen oxidation in cleaning dust water simultaneously, is changed into Dilute sulfuric acid.This cleaning dust aqueous solution containing dilute sulfuric acid, is referred to as Sewage from Sulphuric Acid Plants.In Sewage from Sulphuric Acid Plants, H2SO4Concentration is 10g/L~300g/L, and contain a small amount of copper, lead, zinc metal ion, also contain a small amount of fluorine ion, chloride ion, sulfurous acid Root, arsenic ion, cadmium ion etc..
Currently, for H2SO4Concentration is that the main method of Sewage from Sulphuric Acid Plants of 10g/L~300g/L is: using lime (including Quick lime, white lime, digestion lime) it is neutralized.In N-process, control neutralize terminal pH value > 10.5, lime with Sulfuric acid is reacted, and generates that solubility is smaller and the good calcium sulfate of stability.Meanwhile copper in Sewage from Sulphuric Acid Plants, lead, zinc from Son, cadmium ion and part arsenic ion are respectively formed corresponding hydroxide precipitating, into calcium sulfate slag.In addition, a small amount of Asia Sulfate radical and calcium binding, which are formed after calcium sulfite, to be further oxided as calcium sulfate, and part arsenic ion forms arsenic acid calcium salt, Also enter in calcium sulfate slag.The above method has the advantages that technology maturation, adaptable, easy to operate, processing cost is low etc., but It, can not since a large amount of calcium sulfate slags that N-process is formed do not meet the gypsum product standard requirements of cement industry or building material industry It realizes resource utilization, ultimately forms the dangerous waste residue of smelting, the dangerous waste residue of this smelting is deposited in subsequent storage, management process In biggish environment hidden danger, the development of enterprise is constrained.
To overcome the above disadvantages, some enterprises handle sulfuric acid dirt using two sections of neutralization methods or three sections of neutralization methods Water.When using two sections of neutralization methods, first segment agstone makees neutralizer, and control neutralizes endpoint pH < 1.5;Second segment is used Lime makees neutralizer, and control neutralizes endpoint pH > 10.5.When using two sections of neutralization methods, in the first paragraph and in the process, copper, The heavy metals such as lead, zinc, arsenic, cadmium are still dissolved in the water in the form of an ion, do not form hydroxide precipitating, first segment output Calcium sulfate slag is theoretically containing less heavy metal;And in second segment N-process, the huge sum of money such as copper, lead, zinc, arsenic, cadmium forms hydrogen The calcium sulfate slag of oxide precipitation, second segment output is enriched with heavy metal, keeps this part of sulfuric acid calcium slag economically first Step has the value of development and utilization.Compared to one section neutralization method, two sections of neutralization methods are due to using cost more in first segment Low agstone makees neutralizer, therefore reagent cost consumption is lower, simultaneously as the calcium sulfate slag that second segment obtains tentatively has For the value of development and utilization, can develop and utilize, in this way, the dangerous waste residue of output has measured reduction.But in two sections And method, bigger investment, broader land occupation, more complicated operation, higher wage cost are needed, and in the first paragraph and mistake Cheng Zhong forms the gypsum product standard requirements that a large amount of calcium sulfate slags still do not meet cement industry or building material industry, cannot achieve Resource utilization.Therefore, it says on the whole, two sections of neutralization methods have obvious advantage there is no than one section neutralization method, practical The enterprise of application is simultaneously few.
When using three sections of neutralization methods, implement generally directed to ferric ion and the higher solution of aluminium ion.First segment Make neutralizer with agstone, control neutralizes endpoint pH < 1.5;Second segment lime makees neutralizer, and control neutralizes terminal pH Value < 4.5;Second segment lime makees neutralizer, and control neutralizes endpoint pH > 10.5.When using three sections of neutralization methods, first In section N-process, the heavy metals such as copper, lead, zinc, arsenic, cadmium, iron, aluminium are still dissolved in the water in the form of an ion, do not form hydrogen Oxide precipitation, the calcium sulfate slag of first segment output is theoretically containing less heavy metal;And in second segment N-process, trivalent Iron ion or aluminium ion form sediment, and into slag, and the huge sum of money such as copper, lead, zinc, arsenic, cadmium does not form hydroxide precipitating, The calcium sulfate slag of second segment output is enriched iron or aluminium can further development and production iron oxide red or aluminum sulfate product.In third section And when, the huge sum of money such as copper, lead, zinc, arsenic, cadmium forms hydroxide precipitating, and the calcium sulfate slag of third section output obtains heavy metal Higher enrichment makes this part of sulfuric acid calcium slag have value of exploiting and utilizing.Three sections of neutralization methods, due to first segment use at This lower agstone makees neutralizer, therefore than one section neutralization technology of reagent cost consumption is lower;Simultaneously as in second segment And have a stronger specific aim, the calcium sulfate slag of second segment output also has the value of development and utilization;It is obtained due to third section Calcium sulfate slag metal enrichment ratio is higher, has the value of development and utilization, can develop and utilize, in this way, the danger of output Waste residue amount, which has been got back, to be further reduced.But three sections of neutralization methods need bigger investment, broader land occupation, more complicated behaviour Make, higher wage cost, and in second segment N-process, forms iron content or the calcium sulfate slag development and utilization containing aluminium, only stop The experimental study stage is stayed in, industrial application can not be formed, and the calcium sulfate slag of first segment output does not still meet cement industry Or the gypsum product standard requirements of building material industry, it cannot achieve resource utilization.Therefore, three sections of neutralization methods, currently without reality The enterprise of border application.
In addition, the resource utilization in order to realize Sewage from Sulphuric Acid Plants, some enterprises attempt to have carried out ion exchange technique, solvent Abstraction technique, sulfide precipitation removing heavy-metal technology, macromolecule organic complex-precipitation defluorinate chlorine technology, the purpose is to sulfuric acid is dirty After various impurity or the removing of main objectionable impurities in water, the dry post that absorbs that dilute sulfuric acid is used for flue gas acid preparing is matched Acid, but these methods are due at high cost, and can not obtain satisfied technical indicator.Currently, still without success and the industry of maturation Using.
In consideration of it, it is necessary to develop a kind of processing method of new Sewage from Sulphuric Acid Plants, to make up the deficiencies in the prior art.
Summary of the invention
The purpose of the present invention is overcome the deficiencies of the prior art and provide a kind of processing method of Sewage from Sulphuric Acid Plants.The present invention with The Sewage from Sulphuric Acid Plants that concentration is 10g/L~300g/L is process object, using agstone as neutralizer, is continuously neutralized, is obtained Neutralized reaction product after filter is separated by solid-liquid separation, obtained solid is industrial gypsum, for sale;Obtained filtered fluid After otherwise processed recycles valuable metal therein, then externally discharges or return other production stations and recycle.Sulphur of the invention The processing method of sour sewage, the gypsum product of energy output qualification are finally reached the purpose that Sewage from Sulphuric Acid Plants is carried out to resource utilization, Have many advantages, such as that process flow is short, production cost is low, the stacking and problem of management of not no melting waste slag.
The technical scheme to solve the above technical problems is that a kind of processing method of Sewage from Sulphuric Acid Plants, including it is as follows Step:
Step 1: continuous neutralization reaction
Sewage from Sulphuric Acid Plants and agstone are continuously put into neutralization reaction equipment, continuous neutralization reaction is carried out, is controlled The temperature of reaction is 20 DEG C~80 DEG C, pH value is 3.0~5.0, and the reaction mass residence time is 5h~100h, obtains neutralization reaction Product slurry;
Step 2: being separated by solid-liquid separation
The neutralization reaction product slurry that step 1 is obtained, is separated by solid-liquid separation, respectively obtains industrial gypsum and filtered fluid, Industrial gypsum is for sale, it discharges or recycles again after filtered fluid is recycled valuable metal.
The principle of the present invention is:
(1) Sewage from Sulphuric Acid Plants gets utilization
Cement industry and building material industry have two basic technical indicator requirements to industrial gypsum product, first is that SO in gypsum3 Effective content is not less than 40%, second is that the moisture content of gypsum is not higher than 12%.The present invention is made using cheap agstone Neutralizer, the reaction mainly occurred in N-process are as follows: CaCO3+H2SO4+H2O=CO2↑+CaSO4·2H2O ↓, the reaction Standard free enthalpy changes delta G0It is a biggish negative for -135kJ, reaction progress is very thorough, can generate CaSO4· 2H2O。
Two basic indexs requirement according to cement industry and building material industry to gypsum product, gypsum product must have height SO3The CaSO that content and low moisture content, i.e. neutralization reaction generate4·2H2O filtering is in kind, it is necessary to have high SO3Content and compared with Few mechanical entrapment adhesive water, is only industrial gypsum.
Firstly, to realize that gypsum product has higher SO3Content is carried secretly less as far as possible it is necessary to the gypsum product ensured The unreacted small solid of agstone, therefore, the pH value control of reaction process are critically important.Present inventor is by a large amount of Experimental study proves, is 3.0~5.0 by the slurry pH value control of neutralization reaction process, both can be as much as possible by Sewage from Sulphuric Acid Plants In H2SO4It is neutralized, and may insure the CaSO that the agstone being added participates in neutralization reaction, generates neutralization reaction4· 2H2O filtering material object carries the small solid of unreacted agstone secretly less as far as possible, it is ensured that SO in obtained gypsum product3Content reaches It is required that.
Secondly, to realize the CaSO that neutralization reaction generates4·2H2O filtering less mechanical entrapment adhesive water in kind contains Measure the CaSO generated it is necessary to the neutralization reaction ensured4·2H2O filtering material object has lesser specific surface, by reducing product Specific surface achieve the purpose that reduce mechanical entrapment adhesive water.And lesser specific surface is obtained, it should just obtain larger The CaSO of grain4·2H2O filtering is in kind, this biggish CaSO4·2H2O filtering in kind is industrial gypsum product, that is, ensures to react The CaSO of generation4·2H2O has sufficient crystal to grow up condition, grows into bulky grain CaSO4·2H2O crystal.Present invention People proves by a large amount of experimental study, makees neutralizer with agstone, is 20 DEG C~80 DEG C, pH value 3.0 in reaction temperature ~5.0, the reaction mass residence time, can be with output larger particles continuously to be neutralized under conditions of 5h~100h CaSO4·2H2O filtering is in kind, it is ensured that CaSO4·2H2O filters mechanical entrapment attached water rate in kind and is not higher than 12%, makes CaSO4· 2H2O filtering material object meets the quality criteria requirements of industrial gypsum, output acceptable industrial gypsum.
Machine mixer is installed in continuous neutralization reaction equipment, it is mechanical to ensure effective progress of continuous neutralization reaction Blender can be inputting type, be also possible to side entering type.Each neutralization reaction equipment, can install separate unit blender, can also be with More blenders are installed.Sewage from Sulphuric Acid Plants is continuously added to above consersion unit, the addition speed and flow of Sewage from Sulphuric Acid Plants, it is necessary to Meeting residence time of the reaction mass in neutralization reaction equipment is 5h~100h, to ensure to react the CaSO generated4·2H2O is brilliant Body has sufficient growth time, forms biggish CaSO4·2H2O crystal reduces CaSO4·2H2The specific surface of O crystal, finally Ensure CaSO4·2H2O filters purpose of the mechanical entrapment adhesive water less than 12% in kind.Agstone is from the top of consersion unit It is added, the addition of agstone can be continuously, be also possible to desultory.When being added intermittently, add every time Enter interval time no more than 20 minutes.Control agstone is added speed and weight is added to ensure the slurry pH value of reaction process 3.0~5.0.If consersion unit is provided with neutralized reaction product overflow pipe, at interval of 1.0~2.0 hours, neutralized instead to overflowing to The neutralization reaction slurries outside equipment are answered to be filtered separation.If consersion unit is not provided with neutralization reaction slurries overflow pipe, Suitable neutralization reaction can be extracted at interval of 1.0~2.0 hours according to the neutralization reaction liquid volume capacity in consersion unit Slurries filtering, the slurries amount of extraction and the additional amount population equilibrium of interval time.When extracting neutralization reaction slurries, from neutralization reaction It is more reasonable than extracting from top that the bottom of equipment is extracted, the reason is that the CaSO of consersion unit bottom4·2H2O crystal grain compares top CaSO4·2H2O crystal grain is bigger, the CaSO obtained after filtering4·2H2O filtering mechanical entrapment adhesive water in kind is lower, It more can ensure that CaSO4·2H2O filtering material object reaches the moisture content index requirement of industrial gypsum product, forms qualified industrial gypsum. Sometimes the neutralization reaction slurries of extraction are first also subjected to classification processing, the lesser CaSO of particle with hydrocyclone4·2H2O crystal Go out to again return to neutralization reaction equipment from the overflow pipe of hydrocyclone and continues to grow up, the biggish CaSO of particle4·2H2O crystal from The underflow pipe of hydrocyclone flows out, and filter plant is entered back into, in this way, further ensuring the CaSO that filter plant obtains4· 2H2O filtering in kind is bigger CaSO4·2H2O particle, more can ensure that CaSO4·2H2O filtering material object meets the moisture of gypsum product Index request forms industrial gypsum product.
The present invention makees neutralizer using agstone, reaction temperature be 20 DEG C~80 DEG C, reacting slurry pH value be 3.0~ 5.0, the reaction mass residence time be 5h~100h under conditions of continuously neutralized, obtained CaSO4·2H2O filters machine in kind Tool carries attached water rate secretly less than 12%, SO3Content is greater than 40%, meets cement industry and building material industry to gypsum product standard base This requirement, this CaSO4·2H2O filtering in kind is industrial gypsum product, can be sold to cement industry or building material industry, real The purpose of Sewage from Sulphuric Acid Plants resource utilization is showed.
(2) process flow is short
Only there are two steps by the present invention, so that it may which the industrial gypsum product of output qualification, the two steps are i.e. continuous to be neutralized Reaction process and separation of solid and liquid process.In continuous neutralization reaction, neutralizer is made using agstone, and be maintained at N-process The pH value of middle reacting slurry solution is controlled always 3.0~5.0, can be by the H in Sewage from Sulphuric Acid Plants2SO4Complete neutralization, and can be really Protecting CaSO42H2O filtering material object has higher SO3Content;Meanwhile control continuous neutralization reaction temperature be 20 DEG C~80 DEG C, it is anti- Answering residence time of material is 5h~100h, it can be ensured that obtained CaSO4·2H2O filtering is in kind be biggish Jing Ti ?, it is mechanical Attached water rate is carried secretly less than 12%, meets gypsum product standard requirements.Separation of solid and liquid process is a simple physical process, It is easy to operate, process mechanism and automation may be implemented.
(3) production cost is low
The present invention is since process flow is short, investment reduction, also reduces equipment investment cost and process maintenance maintenance cost, Also cost of labor is saved, while using cheap agstone and making neutralizer, reduces cost.The processing side of the prior art Method makees neutralizer with lime, and 10.5 or more, lime is excessive for pH value control, neutralizer waste, and strict control solution of the present invention PH value be 3.0~5.0, the utilization rate of neutralizer agstone is high, it is superfluous seldom, reduce neutralizer consumption.The present invention adopts Make neutralizer, 1 ton of H of every processing with agstone2SO4Concentration is the Sewage from Sulphuric Acid Plants of 100g/L, only 45 yuan of consuming cost, comprising: (1) electric energy 20kwh is consumed, cost is 12 yuan;(2) 0.12 ton of agstone is consumed, cost is 12 yuan;(3) steam consumption 0.04 ton, cost is 6 yuan;(4) investment depreciation is extracted, and being converted into this is 4 yuan;(5) maintenance of equipment cost is 5 yuan;(6) wage cost It is 10 yuan;(7) gypsum selling cost is 3 yuan;(8) 3 yuan of other costs such as sample analysis etc.;(9) 0.2 ton of gypsum product is produced, is supported Being fastened as this is 10 yuan.
(4) process cleans environmental protection
Firstly, traditional treatment method is neutralizer using lime, lime granularity very little is flown upward very greatly in use, Site environment is poor.The present invention selects agstone to make neutralizer, although agstone granularity is smaller, belongs to particulate matter powder Body, powder 0.030~0.075mm of diameter, average diameter 0.05mm fly upward in use process and are greatly lowered, site environment Be improved significantly.
Secondly, the neutralized reaction product that traditional treatment method obtains, is the calcium sulfate slag and unreacted lime white of fine particle Mixture, granularity is small, and aqueous up to 40% or more, adhesive force is stronger, pollutes and corrode on-site producing devices and working environment.And That the present invention obtains is the CaSO of bulky grain4·2H2O filtering is in kind, i.e. qualified industrial gypsum product, has good permeable Performance not only has faster separation of solid and liquid speed, but also adhesive ability is low, small to production equipment, operating environment corrosion.
Finally, the neutralized reaction product that traditional treatment method obtains, is the calcium sulfate slag and unreacted lime white of fine particle Mixture, aqueous up to 40% or more, gypsum product standard moisture is wanted no more than 12% with cement industry or building material industry It asks and differs greatly.Simultaneously as traditional treatment method, does not have strict control solution, lime surplus is more, causes neutralized reaction product SO3Cement industry or building material industry is not achieved to gypsum product standard SO in content3Content is greater than 40% requirement, therefore at tradition The neutralized reaction product that reason method obtains cannot meet cement industry or building material industry to gypsum product standard requirements, answer without market With channel, resource utilization cannot achieve, stacking can only be taken to dispose, not only need to stack place, but also consumption management cost, and There is also stack and manage brought environment hidden danger.And the CaSO that the present invention obtains4·2H2O filtering material object is the stone of bulky grain Cream product meets gypsum product standard requirements, direct marketing to cement industry or building material industry, realizes Sewage from Sulphuric Acid Plants recycling It utilizes.
Based on the above technical solution, the present invention can also be improved as follows.
Further, in step 1, in the Sewage from Sulphuric Acid Plants, H2SO4Concentration is 10g/L~300g/L;The agstone Powder diameter is 0.030mm~0.075mm, average diameter 0.05mm;CaCO in the agstone3Content is 90%, Moisture content < 12%, SO3Content > 40%.
It is using above-mentioned further beneficial effect: using above-mentioned parameter, it can be ensured that obtained CaSO4·2H2O, filtering SO in kind3Content is greater than 40%, meets gypsum product standard requirements.
Further, in step 2, before the separation of solid and liquid, classification processing is also carried out using hydrocyclone.
It is using above-mentioned further beneficial effect: under the action of hydrocyclone, the lesser CaSO of particle4·2H2O Crystal is flowed out from the overflow pipe of hydrocyclone, is again returned to neutralization reaction equipment and is continued to grow up, and the biggish CaSO of particle4· 2H2O crystal is flowed out from the underflow pipe of hydrocyclone, enters back into filter plant.In this way, further ensuring that filter plant obtains Solid CaSO4·2H2O product has bigger granularity, CaSO4·2H2O filtering mechanical entrapment adhesive water in kind is lower, it is ensured that Adhesive water index meets the requirement of industrial gypsum product standard, the industrial gypsum product of output qualification.
Further, in step 2, the equipment used that is separated by solid-liquid separation is filter press or belt vacuum filter.
Further, in step 2, the valuable metal is one of iron, aluminium, zinc, copper or a variety of.
Be using above-mentioned further beneficial effect: valuable metal refers in the raw material of extracting metals, in addition to main metal, Other metals with recovery value.In the raw materials for metallurgy of nonferrous heavy metal, these valuable metals be mostly noble metal and it is dilute dissipate Metal.
The beneficial effects of the present invention are:
(1) processing method of Sewage from Sulphuric Acid Plants of the invention, it can be ensured that Sewage from Sulphuric Acid Plants gets utilization.The present invention obtains The CaSO arrived4·2H2O filters mechanical entrapment attached water rate in kind less than 12%, SO3Content be greater than 40%, meet cement industry and Building material industry is to gypsum product standard basic demand, this CaSO4·2H2O filtering in kind is industrial gypsum product, Neng Gouxiao Cement industry or building material industry are sold, the purpose of Sewage from Sulphuric Acid Plants resource utilization is realized.
(2) processing method of Sewage from Sulphuric Acid Plants of the invention, process flow are short.Only there are two steps, so that it may which output is qualified Industrial gypsum product, the two steps, that is, continuous neutralization reaction process and separation of solid and liquid process.
(3) processing method of Sewage from Sulphuric Acid Plants of the invention, production cost are low.Since process flow is short, investment reduction also drops Low equipment investment cost and process maintenance maintenance cost also save cost of labor, while using cheap lime stone Powder makees neutralizer, reduces cost.
(4) processing method of Sewage from Sulphuric Acid Plants of the invention, process cleans environmental protection.The present invention selects agstone to neutralize Agent, agstone fly upward be greatly lowered in use, site environment be improved significantly;And what the present invention obtained is big The CaSO of particle4·2H2O filtering is in kind, i.e. qualified industrial gypsum product, has good water permeability, not only has faster Be separated by solid-liquid separation speed, and adhesive ability is low, small to production equipment, operating environment corrosion, and can direct marketing to cement industry Or building material industry, realize Sewage from Sulphuric Acid Plants resource utilization.
(5) processing method of Sewage from Sulphuric Acid Plants of the invention is simple, and operation is easy, wide market, is suitble to scale metaplasia It produces.
Detailed description of the invention
Fig. 1 is the process flow chart of the processing method of Sewage from Sulphuric Acid Plants of the invention.
Specific embodiment
Principles and features of the present invention are described below in conjunction with specific attached drawing, example is served only for explaining this hair It is bright, it is not intended to limit the scope of the present invention.
Embodiment 1
As shown in Figure 1, the processing method of the Sewage from Sulphuric Acid Plants of the present embodiment, includes the following steps:
Step 1: continuous neutralization reaction
During Copper making, the washing, purifying post of flash furnace off-gas acid making system, output H2SO4Concentration is the sulphur of 10g/L Sour sewage.By above-mentioned Sewage from Sulphuric Acid Plants with 6m3The flow of/h, successively from effective volume 30m3Neutralization reaction slot above be added, Reaction time of the Sewage from Sulphuric Acid Plants in neutralization reaction slot is 5h.The machine mixer of neutralization reaction slot is started, while therefrom Agstone is continuously added to the speed of 70kg/h with above reactive tank, the powder diameter of the agstone be 0.030mm~ 0.075mm, average diameter 0.05mm;CaCO in the agstone3Content is 90%, moisture content 11%, SO3Content It is 45%, neutralization reaction is carried out under conditions of reaction temperature is 20 DEG C, pH value is 3.0, the reaction mass residence time is 5h, is obtained To neutralized reaction product.
Step 2: being separated by solid-liquid separation
At interval of 1h, 6m is extracted from the bottom for neutralizing reactive tank with stainless steel pump3Neutralized reaction product, be put into 120m2Filters pressing Machine is filtered.At interval of 8h, to filter press solution plate 1 time, solution plate 3 times daily.Daily output CaSO after filters pressing4·2H2O filtering 3080kg in kind, CaSO4·2H2O filtering moisture content in kind is 11.5%, is converted into dry state CaSO4·2H2O filtrate is 2726kg, dry state CaSO4·2H2O filtrate SO3Content is 43.08%.CaSO4·2H2O filtering material object meets cement industry pair Gypsum product standard requirements are sold to cement plant by gypsum product;Obtained filtered fluid by otherwise processed recycle copper metal after, It is recycled back to the washing, purifying post of flash furnace off-gas acid making system.
Embodiment 2
As shown in Figure 1, the processing method of the Sewage from Sulphuric Acid Plants of the present embodiment, includes the following steps:
Step 1: continuous neutralization reaction
In zinc metallurgical process, the washing, purifying post of fluidized bed furnace flue gas acid preparing system, output H2SO4Concentration is 100g/L's Sewage from Sulphuric Acid Plants.By above-mentioned Sewage from Sulphuric Acid Plants with 3m3The flow of/h, successively from effective volume 75m3Neutralization reaction slot above plus Enter, reaction time of the Sewage from Sulphuric Acid Plants in neutralization reaction slot is 25h.The machine mixer of neutralization reaction slot is started, simultaneously Using spiral feeding mechanism, with the speed of 0.36t/h, agstone, the stone successively is added above neutralization reactive tank The powder diameter of limestone flour is 0.030mm~0.075mm, average diameter 0.05mm;CaCO in the agstone3Content It is 90%, moisture content 10%, SO3Content is 50%, under conditions of reaction temperature is 50 DEG C, pH value is 4.0 carry out in and Reaction, reaction mass residence time are 50h, obtain neutralized reaction product.
Step 2: being separated by solid-liquid separation
At interval of 2h, 6m is extracted from the bottom for neutralizing reactive tank with stainless steel pump3Neutralized reaction product, be put into 160m2Filters pressing Machine is filtered.At interval of 2h, to filter press solution plate 1 time, solution plate 12 times daily.Daily output CaSO after filters pressing4·2H2O filtering 15.88t in kind, CaSO4·2H2O filtering moisture content in kind is 11.1%, is converted into dry state CaSO4·2H2O filtrate is 14.12t dry state CaSO4·2H2O filtrate SO3Content is 41.6%.CaSO4·2H2O filtering material object meets cement industry to stone The requirement of cream product standard, is sold to cement plant by gypsum product;Obtained filtered fluid otherwise processed recycles zinc therein, returns to The washing, purifying post of fluidized bed furnace flue gas acid preparing system recycles.
Embodiment 3
As shown in Figure 1, the processing method of the Sewage from Sulphuric Acid Plants of the present embodiment, includes the following steps:
Step 1: neutralization reaction
In lead smelting process, bottom blowing aoxidizes the washing, purifying post of kiln gas acid making system, output H2SO4Concentration is 300g/ The Sewage from Sulphuric Acid Plants of L.By above-mentioned Sewage from Sulphuric Acid Plants with 2.0m3The flow of/h, successively from effective volume 200m3Neutralization reaction slot Top is added.Reaction time of the Sewage from Sulphuric Acid Plants in neutralization reaction slot is 100h.Start 4 side entering types of neutralization reaction slot Machine mixer, while screw fixed-weight feeder structure is used, with the speed of 0.7t/h, successively add above neutralization reactive tank Enter agstone, the powder diameter of the agstone is 0.030mm~0.075mm, average diameter 0.05mm;The lime CaCO in mountain flour3Content is 90%, moisture content 9%, SO3Content is 60%, reaction temperature is 80 DEG C, pH value is 5.0 Under the conditions of carry out neutralization reaction, obtain neutralized reaction product.
Step 2: being separated by solid-liquid separation
At interval of 2h, 8m is extracted from the bottom for neutralizing reactive tank with stainless steel pump3Neutralized reaction product, and be transported to by 10 The cyclone separator of hydrocyclone composition is classified.In classification process, the overflow pipe stream from hydrocyclone is obtained Overflow slurry 4m out3.Above-mentioned 4m3Overflow slurry lesser CaSO containing particle4·2H2O crystal returns to neutralization reaction slot Continue to grow up.In addition, flowing out slurries 4m from hydrocyclone bottom liquid pipe3, 150m is flowed to automatically using nature height difference2Band Formula vacuum filter is filtered.After belt vacuum filter filtering, daily output CaSO4·2H2O filters material object 30.7t, CaSO4·2H2O filters moisture content 9.6% in kind, is converted into dry state CaSO4·2H2O filtrate is 27.73t, dry state CaSO4· 2H2O filtrate SO3Content is 42.3%.CaSO4·2H2O filtering material object meets building material industry to gypsum product standard requirements, presses Gypsum product is sold to plasterboard compacting factory;The washing of obtained filtering liquid back to bottom blowing oxidation kiln gas acid making system is net Change post to recycle.
Comparative example 1
The processing method of the Sewage from Sulphuric Acid Plants of this comparative example 1, includes the following steps:
Step 1: continuous neutralization reaction
During Copper making, the washing, purifying post of flash furnace off-gas acid making system, output H2SO4Concentration is the sulphur of 10g/L Sour sewage.By above-mentioned Sewage from Sulphuric Acid Plants with 6m3The flow of/h, successively from effective volume 30m3Neutralization reaction slot above be added, Reaction time of the Sewage from Sulphuric Acid Plants in neutralization reaction slot is 5h.The machine mixer of neutralization reaction slot is started, while therefrom CaCO is continuously added to the speed of 70kg/h with above reactive tank3Content is 90% graininess lime stone, graininess lime stone Average diameter is 10mm, carries out neutralization reaction under conditions of reaction temperature is 20 DEG C, pH value is 3.0, obtains neutralized reaction product.
Step 2: being separated by solid-liquid separation
At interval of 1h, 6m is extracted from the bottom for neutralizing reactive tank with stainless steel pump3Neutralized reaction product, be put into 120m2Filters pressing Machine is filtered.At interval of 8h, to filter press solution plate 1 time, solution plate 3 times daily.Daily output CaSO after filters pressing4·2H2O filtering 3780kg in kind, CaSO4·2H2O filtering moisture content in kind is 31.5%, is converted into dry state CaSO4·2H2O filtrate is 2589kg, dry state CaSO4·2H2O filtrate SO3Content is 28.59%.CaSO4·2H2O filtering SO in kind3Content and moisture Content does not comply with the requirement of industrial gypsum product standard, and no product selling market can only take stacking to dispose, and pollutes environment.
Comparative example 2
The processing method of the Sewage from Sulphuric Acid Plants of this comparative example 2, includes the following steps:
Step 1: continuous neutralization reaction
During Copper making, the washing, purifying post of flash furnace off-gas acid making system, output H2SO4Concentration is the sulphur of 10g/L Sour sewage.By above-mentioned Sewage from Sulphuric Acid Plants with 6m3The flow of/h, successively from effective volume 30m3Neutralization reaction slot above be added, Reaction time of the Sewage from Sulphuric Acid Plants in neutralization reaction slot is 5h.The machine mixer of neutralization reaction slot is started, while therefrom CaCO is continuously added to the speed of 70kg/h with above reactive tank3Content be 90% agstone, reaction temperature be 10 DEG C, PH value carries out neutralization reaction under conditions of being 3.0, obtains neutralized reaction product.
Step 2: being separated by solid-liquid separation
At interval of 1h, 6m is extracted from the bottom for neutralizing reactive tank with stainless steel pump3Neutralized reaction product, be put into 120m2Filters pressing Machine is filtered.At interval of 8h, to filter press solution plate 1 time, solution plate 3 times daily.Daily output CaSO after filters pressing4·2H2O filtering 3488kg in kind, CaSO4·2H2O filtering moisture content in kind is 22.1%, is converted into dry state CaSO4·2H2O filtrate is 2715kg, dry state CaSO4·2H2O filtrate SO3Content is 40.92%.CaSO4·2H2O filters moisture content in kind and does not meet The requirement of industrial gypsum product standard, no product selling market can only take stacking to dispose, and pollute environment.
Comparative example 3
The processing method of the Sewage from Sulphuric Acid Plants of this comparative example 3, includes the following steps:
Step 1: continuous neutralization reaction
During Copper making, the washing, purifying post of flash furnace off-gas acid making system, output H2SO4Concentration is the sulphur of 10g/L Sour sewage.By above-mentioned Sewage from Sulphuric Acid Plants with 6m3The flow of/h, successively from effective volume 30m3Neutralization reaction slot above be added, Reaction time of the Sewage from Sulphuric Acid Plants in neutralization reaction slot is 5h.The machine mixer of neutralization reaction slot is started, while therefrom CaCO is continuously added to the speed of 75kg/h with above reactive tank3Content be 90% agstone, reaction temperature be 20 DEG C, PH value carries out neutralization reaction under conditions of being 5.5, obtains neutralized reaction product.
Step 2: being separated by solid-liquid separation
At interval of 1h, 6m is extracted from the bottom for neutralizing reactive tank with stainless steel pump3Neutralized reaction product, be put into 120m2Filters pressing Machine is filtered.At interval of 8h, to filter press solution plate 1 time, solution plate 3 times daily.Daily output CaSO after filters pressing4·2H2O filtering 3275kg in kind, CaSO4·2H2O filtering moisture content in kind is 12.9%, is converted into dry state CaSO4·2H2O filtrate is 2850kg, dry state CaSO4·2H2O filtrate SO3Content is 38.47%.CaSO4·2H2O filters material object SO3Content and moisture contain Amount does not comply with the requirement of industrial gypsum product standard, and no product selling market can only take stacking to dispose, and pollutes environment.
Comparative example 4
The processing method of the Sewage from Sulphuric Acid Plants of this comparative example 4, includes the following steps:
Step 1: continuous neutralization reaction
During Copper making, the washing, purifying post of flash furnace off-gas acid making system, output H2SO4Concentration is the sulphur of 10g/L Sour sewage.By above-mentioned Sewage from Sulphuric Acid Plants with 6m3The flow of/h, successively from effective volume 30m3Neutralization reaction slot above be added, Reaction time of the Sewage from Sulphuric Acid Plants in neutralization reaction slot is 2h.The machine mixer of neutralization reaction slot is started, while therefrom CaCO is continuously added to the speed of 70kg/h with above reactive tank3Content be 90% agstone, reaction temperature be 10 DEG C, PH value carries out neutralization reaction under conditions of being 3.0, obtains neutralized reaction product.
Step 2: being separated by solid-liquid separation
At interval of 1h, 6m is extracted from the bottom for neutralizing reactive tank with stainless steel pump3Neutralized reaction product, be put into 120m2Filters pressing Machine is filtered.At interval of 8h, to filter press solution plate 1 time, solution plate 3 times daily.Daily output CaSO after filters pressing4·2H2O filtering 5234kg in kind, CaSO4·2H2O filtering moisture content in kind is 47.94%, is converted into dry state CaSO4·2H2O filtrate is 2725kg, dry state CaSO4·2H2O filtrate SO3Content is 43.11%.CaSO4·2H2O filters moisture content in kind and does not meet The requirement of industrial gypsum product standard, no product selling market can only take stacking to dispose, and pollute environment.
The foregoing is merely presently preferred embodiments of the present invention, is not intended to limit the invention, it is all in spirit of the invention and Within principle, any modification, equivalent replacement, improvement and so on be should all be included in the protection scope of the present invention.

Claims (5)

1. a kind of processing method of Sewage from Sulphuric Acid Plants, which comprises the steps of:
Step 1: continuous neutralization reaction
Sewage from Sulphuric Acid Plants and agstone are continuously put into neutralization reaction equipment, continuous neutralization reaction, control reaction are carried out Temperature be 20 DEG C~80 DEG C, pH value is 3.0~5.0, the reaction mass residence time be 5h~100h, obtain neutralization reaction slurries Product;
Step 2: being separated by solid-liquid separation
The neutralization reaction product slurry that step 1 is obtained, is separated by solid-liquid separation, respectively obtains industrial gypsum and filtered fluid, by work Industry gypsum is for sale, discharges or recycles again after filtered fluid is recycled valuable metal.
2. a kind of processing method of Sewage from Sulphuric Acid Plants according to claim 1, which is characterized in that in step 1, the sulfuric acid is dirty In water, H2SO4Concentration is 10g/L~300g/L;The powder diameter of the agstone is 0.030mm~0.075mm, average straight Diameter is 0.05mm;CaCO in the agstone3Content is 90%, moisture content < 12%, SO3Content > 40%.
3. a kind of processing method of Sewage from Sulphuric Acid Plants according to claim 1, which is characterized in that in step 2, in the solid-liquid Before separation, classification processing is also carried out using hydrocyclone.
4. a kind of processing method of Sewage from Sulphuric Acid Plants according to claim 1, which is characterized in that in step 2, the solid-liquid point From the equipment used for filter press or belt vacuum filter.
5. a kind of processing method of Sewage from Sulphuric Acid Plants according to claim 1, which is characterized in that, it is described valuable in step 2 Metal is one of iron, aluminium, zinc, copper or a variety of.
CN201811427663.6A 2018-11-27 2018-11-27 A kind of processing method of Sewage from Sulphuric Acid Plants Pending CN109354252A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811427663.6A CN109354252A (en) 2018-11-27 2018-11-27 A kind of processing method of Sewage from Sulphuric Acid Plants

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811427663.6A CN109354252A (en) 2018-11-27 2018-11-27 A kind of processing method of Sewage from Sulphuric Acid Plants

Publications (1)

Publication Number Publication Date
CN109354252A true CN109354252A (en) 2019-02-19

Family

ID=65343230

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811427663.6A Pending CN109354252A (en) 2018-11-27 2018-11-27 A kind of processing method of Sewage from Sulphuric Acid Plants

Country Status (1)

Country Link
CN (1) CN109354252A (en)

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5207927A (en) * 1992-03-18 1993-05-04 Uop Treatment of an aqueous stream containing water-soluble inorganic sulfide compounds
CN101041520A (en) * 2007-03-23 2007-09-26 长沙矿冶研究院 Treatment method for recycling zinc electrolysis washing wastewater
WO2012113958A1 (en) * 2011-02-23 2012-08-30 Abengoa Water, S. L. U. Brine treatment method
US20130048562A1 (en) * 2011-08-31 2013-02-28 Prochemtech International, Inc. Treatment of gas well production wastewaters
US8900535B2 (en) * 2010-01-07 2014-12-02 Barrick Gold Corporation Production of zinc sulphate concentrates from a dilute zinc sulphate solution
CN105439357A (en) * 2015-12-28 2016-03-30 中南大学 Mine acid wastewater utilization and deep purification method
US20160137524A1 (en) * 2013-06-17 2016-05-19 Sumitomo Metal Mining Co., Ltd. Hematite manufacturing process and hematite manufactured by same
CN106380018A (en) * 2016-10-10 2017-02-08 华南理工大学 Titanium dioxide wastewater treatment method favorable for improving utilization ratio of calcium oxide and dehydration property of byproduct gypsum
WO2017117626A1 (en) * 2016-01-04 2017-07-13 Glencore Queensland Limited Precipitation of nickel and cobalt
CN107777802A (en) * 2016-08-25 2018-03-09 上海江柘环境工程技术有限公司 A kind of acid waste water processing system and its handling process method

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5207927A (en) * 1992-03-18 1993-05-04 Uop Treatment of an aqueous stream containing water-soluble inorganic sulfide compounds
CN101041520A (en) * 2007-03-23 2007-09-26 长沙矿冶研究院 Treatment method for recycling zinc electrolysis washing wastewater
US8900535B2 (en) * 2010-01-07 2014-12-02 Barrick Gold Corporation Production of zinc sulphate concentrates from a dilute zinc sulphate solution
WO2012113958A1 (en) * 2011-02-23 2012-08-30 Abengoa Water, S. L. U. Brine treatment method
US20130048562A1 (en) * 2011-08-31 2013-02-28 Prochemtech International, Inc. Treatment of gas well production wastewaters
US20160137524A1 (en) * 2013-06-17 2016-05-19 Sumitomo Metal Mining Co., Ltd. Hematite manufacturing process and hematite manufactured by same
CN105439357A (en) * 2015-12-28 2016-03-30 中南大学 Mine acid wastewater utilization and deep purification method
WO2017117626A1 (en) * 2016-01-04 2017-07-13 Glencore Queensland Limited Precipitation of nickel and cobalt
CN107777802A (en) * 2016-08-25 2018-03-09 上海江柘环境工程技术有限公司 A kind of acid waste water processing system and its handling process method
CN106380018A (en) * 2016-10-10 2017-02-08 华南理工大学 Titanium dioxide wastewater treatment method favorable for improving utilization ratio of calcium oxide and dehydration property of byproduct gypsum

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
DENG LICONG等: "Reactive Crystallization of Calcium Sulfate Dihydrate from Acidic Wastewater and Lime", 《CHINESE JOURNAL OF CHEMICAL ENGINEERING》 *
周至祥等: "《火电厂湿法烟气脱硫技术手册》", 30 June 2006, 中国电力出版社 *
戴金辉等: "《无机非金属材料概论》", 31 July 2018, 哈尔滨工业大学出版社 *
郭东明等: "《硫氮污染防治工程技术及其应用》", 30 April 2001, 化学工业出版社 *

Similar Documents

Publication Publication Date Title
CN100427617C (en) Method of comprehensive utilizing iron making blast furnace dust resources
CN107213774B (en) Flue gas desulfurization and resource utilization method based on smelting tailing slag
CN112692042B (en) Aluminum electrolysis cell waste refractory material treatment process and system thereof
CN105567976B (en) A kind of vanadium extraction industrial acidic wastewater processing and the method for valuable metal synthetical recovery
CN102008886B (en) Zinc oxide wet turbulent washing flue gas desulfurization device and process
CN101845562A (en) Improved device and method for producing electrolytic manganese metal by two-ore method
CN101760613B (en) Method for leaching zinc-containing ores
CN103526017A (en) Extraction method of valuable elements from acid mud produced in sulfuric acid production by copper smelting flue gas
CN103588240B (en) A kind of green utilization method of dirty acid
CN107963642A (en) SO is absorbed using the water logging of industrial caustic containing arsenic lye2The process of flue gas, dearsenification purification production sodium sulfite product
CN108220606A (en) A kind of method of lead, mercury, selenium synthetical recovery in Copper making acid mud
CN106215863B (en) A kind of heavy metal absorbent of purification diluted sulfric acid and its application
CN107619068A (en) A kind of iron sulfonium prepares the method that hydrogen sulfide is used for waste acid processing
CN101545038B (en) Method for producing iron ore concentrate by using poor-tin sulfide ore tailings
CN109988902B (en) Method for dealkalizing iron-reinforced red mud and separating and recovering iron
CN102849814A (en) Treatment method for purifying sewage and tail gas from furnace gas in acid production from gypsum
CN101545037B (en) Method for producing iron ore concentrate by using poor-tin oxidized ore tailings
CN113044815A (en) Method and system for comprehensively treating selenium-tellurium-containing waste
CN112676029A (en) Method for preparing water glass by using purified iron tailings
CN111979421A (en) Method for comprehensively utilizing copper-containing arsenic-containing soot produced in copper smelting process
CN109354252A (en) A kind of processing method of Sewage from Sulphuric Acid Plants
CN215667159U (en) System for comprehensive treatment contains selenium tellurium waste material
CN101816979A (en) Flotation activating agent of marmatite and blende and preparation method thereof
CN108866331A (en) A method of zinc oxide being produced under zinc ammonia complexing environment using containing zinc ore crude
CN108033589A (en) The method that a kind of waste acid removal of impurities in acid making system recycles

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20190219

RJ01 Rejection of invention patent application after publication