CN105935550A - Composite treatment agent for acid gas and heavy metal and treating method for acid gas and heavy metal - Google Patents

Composite treatment agent for acid gas and heavy metal and treating method for acid gas and heavy metal Download PDF

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Publication number
CN105935550A
CN105935550A CN201510981166.0A CN201510981166A CN105935550A CN 105935550 A CN105935550 A CN 105935550A CN 201510981166 A CN201510981166 A CN 201510981166A CN 105935550 A CN105935550 A CN 105935550A
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hydroxide
heavy metal
basicity
sulfate
double salt
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CN105935550B (en
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山崎武志
益子光博
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Kurita Water Industries Ltd
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/81Solid phase processes
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D3/00Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
    • A62D3/30Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
    • A62D3/33Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents by chemical fixing the harmful substance, e.g. by chelation or complexation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/508Sulfur oxides by treating the gases with solids
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/68Halogens or halogen compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/68Halogens or halogen compounds
    • B01D53/685Halogens or halogen compounds by treating the gases with solids
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/40Inorganic substances
    • A62D2101/43Inorganic substances containing heavy metals, in the bonded or free state
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/40Alkaline earth metal or magnesium compounds
    • B01D2251/402Alkaline earth metal or magnesium compounds of magnesium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/40Alkaline earth metal or magnesium compounds
    • B01D2251/404Alkaline earth metal or magnesium compounds of calcium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/20Halogens or halogen compounds
    • B01D2257/204Inorganic halogen compounds
    • B01D2257/2045Hydrochloric acid
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • B01D2257/302Sulfur oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases
    • B01D2258/0291Flue gases from waste incineration plants
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2259/00Type of treatment
    • B01D2259/12Methods and means for introducing reactants
    • B01D2259/128Solid reactants

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
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  • Oil, Petroleum & Natural Gas (AREA)
  • General Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Business, Economics & Management (AREA)
  • Emergency Management (AREA)
  • Processing Of Solid Wastes (AREA)
  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention relates to a composite treatment agent for acid gas and heavy metal and a treating method for acid gas and heavy metat, which are capable of fully lowering alkalinity in flying ash in a wide additive amount range so as to solve a problem of late stage procedure of flying ash treatment caused by overdose or insufficiency of acid gas treatment agents come along with qualitative change of waste. The composite treatment agent for acid gas and heavy metal comprises a double salt and at least two chemical compounds chosen from chloride, sulfate and hydroxide, wherein the double salt contains calcium hydroxide and magnesium hydroxide. In order to achieve high raw material stability and mixing stability, the specific surface area of preferable double salt is higher than 20 m2/g, and a median particle diameter (d50) is less than 30 [mu]m. Preferably, an alkalinity lowering agent preferably contains at least two chosen from magnesium sulfate, sulfate-containing aluminium hydroxide, zinc sulfate, copper sulfate, magnesium hydroxide, aluminum hydroxide, ferric hydroxide, ferrous hydroxide, zinc hydroxide and copper hydroxide.

Description

Sour gas and the composite treating agent of heavy metal and sour gas and the processing method of heavy metal
Technical field
The present invention relates to sour gas and the composite treating agent of heavy metal and sour gas and heavy metal Processing method.More specifically, the present invention relates to composite treating agent and compounding method, this compound place Reason agent and compounding method be used for processing municipal refuse waste combustion stove, trade waste incinerator, Sour gas contained in the waste gas produced in the combustion plant of power plant boiler, retort, civil plant etc. Heavy metal contained in the flying dust produced in body (hydrogen chloride, oxysulfide etc.) and this combustion plant.
Background technology
Under normal circumstances, for containing hydrogen chloride, the waste gas of oxysulfide, entering with alkaline agents such as calcium hydroxide After row processes, discharge by chimney via after the dust arresters such as bag hose.On the other hand, with dust arrester dust Flying dust contains the heavy metals such as harmful lead, cadmium, after dust arrester dust, utilizes heavy metal fixative to carry out Heavy metal stabilization processes, and then carries out landfill stabilization (for example, with reference to patent documentation 1).
Prior art literature
Patent documentation
Patent documentation 1: Japanese Unexamined Patent Publication 9-99215 publication
Summary of the invention
The problem that invention is to be solved
The variation of the sour gas load that reason municipal refuse, the qualitative change of trade waste cause and lead When the addition of cause Sour gas disposal agent significantly changes, the Sour gas disposal agent of excess may be supplied to In flue.In this case, owing to Sour gas disposal agent is alkalescence, therefore, dust arrester dust is used Flying dust in can remain alkali compounds, even if fixing supplying heavy metal with the flying dust of dust arrester dust Agent, this heavy metal fixative also can be consumed, and reason is, it is not only to heavy metal contained in flying dust Being fixed, but also can with residual Sour gas disposal agent occur neutralize reaction, result sometimes without Method suppresses heavy metal contained in flying dust aptly.
The present invention completes in view of the foregoing, it is intended that in wide in range addition scope Basicity in interior fully reduction flying dust, thus solve the acidity produced by the qualitative change with garbage The problem of the flying dust treatment process of the excess of gas treatment agent and the not enough back segment caused.
For solving the scheme of problem
The present inventor etc. have been repeated have concentrated on studies to realize object defined above, it was found that pass through It is applied in combination the double salt constituted containing calcium hydroxide and magnesium hydroxide and basicity depressant is existing to substitute The Sour gas disposal agent with slaked lime as representative, contained sour gas can be processed in waste gas, with And reduce by the basicity of the flying dust of dust arrester dust, and after heavy metal fixative can be suppressed to process from The leaching ability of heavy metal amount of flying dust, thus complete the present invention.Specifically, the present invention provides following side Case.
(1) the present invention relates to the composite treating agent of a kind of sour gas and heavy metal, it comprises: containing hydrogen-oxygen The double salt changing calcium and magnesium hydroxide and constitute and basicity depressant.
(2) moreover, it relates to the composite treating agent described in (1) in, the specific surface area of aforementioned double salt For 20m2/ more than g, median particle diameter (d50) are less than 30 μm.
(3) moreover, it relates to the composite treating agent described in (1) or (2) in, aforementioned basicity depressant For more than a kind compound in chloride, sulfate and hydroxide.
(4) moreover, it relates to the composite treating agent described in (3) in, aforesaid compound comprises and is selected from Magnesium sulfate, the aluminium hydroxide of containing sulfate, zinc sulfate, copper sulfate, magnesium hydroxide, aluminium hydroxide, hydrogen In ferrum oxide, ferrous hydroxide, zinc hydroxide and Copper hydrate more than a kind.
(5) moreover, it relates to (1)~(4) in the composite treating agent described in any one in, aforementioned acid Property gas be sour gas contained in waste gas, aforementioned heavy metal is heavy metal contained in flying dust.
(6) moreover, it relates to a kind of sour gas and the processing method of heavy metal, add in the offgas After the double salt constituted containing calcium hydroxide and magnesium hydroxide, flying dust is carried out dust, and after dust Flying dust adds basicity depressant.
The effect of invention
According to the present invention, it is possible not only to process sour gas contained in waste gas aptly, it is also possible to reduce The basicity of flying dust, result can also suppress the leaching ability of heavy metal from flying dust after the process of heavy metal fixative Amount.
Accompanying drawing explanation
Fig. 1 represents the Sketch of the simulation dust arrester Lab-evaluation device used in embodiment.
Fig. 2 represents in addition and the device shown in Fig. 1 of the various inorganic agents of embodiment and comparative example The relation of hydrogen chloride gas clearance.
Fig. 3 represents the addition of the various inorganic agents of embodiment and comparative example and by the device shown in Fig. 1 The relation of the basicity of the residue obtained.
Detailed description of the invention
Below, embodiments of the present invention are illustrated, but these embodiments do not limit the present invention.
The composite treating agent > of < sour gas and heavy metal
The composite treating agent of the present invention comprises: the double salt constituted containing calcium hydroxide and magnesium hydroxide and alkali Degree depressant.
(double salt)
Double salt using calcium hydroxide and magnesium hydroxide as required constituent.The manufacture method of double salt is not had There is restriction especially, as simply example, can enumerate: to dolomite (dolomite, CaMg (CO3)2) Carry out roasting, and carry out hydroxide (digestion), thus obtain hydroxide dolomite (Ca (OH)2·Mg(OH)2)。
If double salt does not contains calcium hydroxide, then can not process sour gas contained in waste gas aptly, Therefore it is the most preferred.If not containing magnesium hydroxide, it is likely that speculate that the effect suppressing following situation reduces, Cannot fully reduce the basicity in flying dust, the most preferably, described situation is: the basicity of double salt is high, in system The double salt of residual can hinder the immobilization to heavy metal contained in flying dust of the heavy metal fixative, and possibly cannot Heavy metal contained in suppression double salt aptly;The product of calcium hydroxide and sour gas is passivated and presses down Make later reaction.
Calcium hydroxide is not contained only, but also containing magnesium hydroxide, therefore, and without hydrogen-oxygen due to double salt The situation changing magnesium is compared, and can suppress basicity at reduced levels.The basicity of double salt is not particularly limited, It is preferably 500mgCaCO3/ more than g and 1000mgCaCO3/ below g, more preferably 700mgCaCO3/g Above and 900mgCaCO3/ below g.As reference, powder is that basicity during calcium hydroxide monomer exists 1200mgCaCO3/ more than g and 1350mgCaCO3In the scope of/below g.
In this specification, basicity refers to the value obtained as described below: by sample (0.1~0.5g) with 1,000 times The pure water (100~500ml) of amount is put in beaker, by magnetic stirrer 1 hour, uses micropipette Device point takes ormal weight (ml) from the sample obtained from, after dropping few drops phenolphthalein indicator mixes, The sulphuric acid of titration 1/50N is to variable color (to pH8.3) rapidly, records the sulphuric acid titer (ml) of every 1g medicament, The value calculated by following conversion formula and obtain.
(conversion formula)
Basicity (mgCaCO3/g)
=0.02{ titrated sulfuric acid concentration (mol/L) } × A (ml) ÷ B (g) × C (ml) ÷ D (ml) × 100 ÷ 2
=A (ml) ÷ B (g) × C (ml) ÷ D (ml)
In conversion formula, A be sulphuric acid titer (ml), B be sample size (g), C is pure water addition (ml), D is point taken amount (ml) after stirring.
The composite treating agent of the present invention comprises the double salt constituted containing calcium hydroxide and magnesium hydroxide.Even if Composite treating agent comprises the salt-mixture of magnesium hydroxide powder and calcium hydroxide powder, this mixture the most not phase When in double salt, therefore, different from the composite treating agent of the present invention.In double salt, calcium atom and magnesium atom connect Closely constitute a salt, and in the salt-mixture that mono-salt is each other, magnesium hydroxide powder and calcium hydroxide powder End is in mutual scattered state.
And, double salt can get following basicity reducing effect: (a) double salt in addition to calcium hydroxide also by hydrogen Magnesium oxide, as required constituent, thus reduces the effect of basicity of double salt itself, (b) and thinks and pass through The product of suppression calcium hydroxide and sour gas is passivated and can be directed at inside granule by sour gas Basicity reducing effect, (c) utilize other composition of composite treating agent i.e. a kind in sulfate etc. with The basicity reducing effect of upper compound (basicity depressant) and (d) utilize the product with sour gas Basicity reducing effect, therefore it could be speculated that relative to prior art, can get and the basicity of flying dust can be made to drop As little as about 1/2, result can also suppress the special effect of the leaching ability of heavy metal amount etc from flying dust.
The specific surface area of double salt is not particularly limited, preferably 20m2/ more than g, more preferably 30m2/g Above, more preferably 40m2/ more than g.If specific surface area is too small, then with sour gas (hydrogen chloride Gas, sulphur oxide gas etc.) contact area little, it is possible to sour gas cannot be processed aptly. And, the most unreacted double salt increases, and the basicity of flying dust improves, and result likely cannot press down aptly The leaching ability of heavy metal amount from flying dust after heavy metal fixative processed process.
The median particle diameter (d50) of double salt is not particularly limited, below preferably 30 μm, more preferably Below 20 μm.
The lower limit of median particle diameter is not particularly limited, and the median particle diameter of double salt is preferably more than 5 μm.
It should be noted that in this specification, " median particle diameter " refers to be obtained by laser diffractometry The particle diameter that aggregate-value is 50% (d50) of the granule number in the particle size distribution in terms of volume reference.
The ratio of calcium hydroxide with magnesium hydroxide is not particularly limited, utilizes hydrogen from obtaining aptly Calcium oxide processes the effect of sour gas and utilizes magnesium hydroxide to reduce the effect of basicity of double salt itself Consider, with molar ratio computing, preferably at calcium hydroxide: in the range of magnesium hydroxide=0.79:1.0~3.15:1.0, More preferably in the range of 0.96:1.0~2.36:1.0.
(basicity depressant)
The composite treating agent of the present invention comprises chloride, sulfate, hydroxide etc. and has reduction basicity work Compound.Below, for convenience this compound is referred to as " basicity depressant ".
When composite treating agent is supplied to flue, sour gas (is wherein mainly hydroxide with above-mentioned double salt Calcium component) react.Product in this reaction and unreacted reactant with the form of flying dust by dust arrester Dust.Then, when adding water in the flying dust of dust, come from hydrogen-oxygen contained in unreacted double salt The alkali composition changing calcium reacts with basicity depressant and product, it is possible to decrease the basicity of flying dust.
For basicity depressant, come from calcium hydroxide contained in unreacted double salt as long as can reduce Alkali composition, be just not particularly limited, preferably comprise in chloride, sulfate and hydroxide More than a kind compound.As muriatic example, can enumerate: magnesium chloride, aluminum chloride, ferrous chloride (II), Iron chloride (III), zinc chloride, copper chloride etc..As the example of sulfate, can enumerate: magnesium sulfate, sulfur Acid aluminum, the aluminium hydroxide of containing sulfate, ferrous sulfate (II), iron sulfate (III), zinc sulfate, copper sulfate Deng.As the example of hydroxide, can enumerate: magnesium hydroxide, aluminium hydroxide, ferrous hydroxide (II), Hydrated ferric oxide. (III), zinc hydroxide, Copper hydrate etc..Wherein, high from the stability of material itself, can Heat release during supply basicity depressant is suppressed from the standpoint of reduced levels, it is preferred that basicity reduces Agent comprises selected from magnesium sulfate, the aluminium hydroxide of containing sulfate, zinc sulfate, copper sulfate, magnesium hydroxide, hydrogen In aluminium oxide, hydrated ferric oxide., ferrous hydroxide, zinc hydroxide, Copper hydrate more than a kind.
The ratio of double salt with basicity depressant is not particularly limited, multiple from utilization all can be obtained aptly Calcium hydroxide contained in salt and process the effect of sour gas, utilize magnesium hydroxide fall contained in double salt The effect of the basicity of low double salt own, utilize basicity depressant to reduce the effect of flying dust basicity from the standpoint of, By quality ratio, preferably at double salt: in the range of basicity depressant=10:0.5~10:8, more preferably exist In the range of 10:1~10:6.It addition, when setting the ratio of double salt and basicity depressant, so that flying dust Basicity is preferably 100mgCaCO3/ below g, more preferably 70mgCaCO3/ below g, more preferably 50mgCaCO3The mode of/below g is set.
(other composition)
As long as in not hindering the scope of the present invention, composite treating agent can also comprise and double salt and basicity fall Low dose of other different composition.As other composition, such as, can enumerate: process contained by sour gas The activated carbon of two English, the kieselguhr etc. of filtration adjuvant as bag hose.It addition, composite treating agent is also Heavy metal fixative can be comprised, in such a case, it is possible to omit the mixed processes of heavy metal fixative, It it is effective method.
(manufacture method of composite treating agent)
Above-mentioned various compositions can be mixed to come by utilizing currently known method by composite treating agent equably Obtain.
< sour gas and processing method > of heavy metal
The processing method of the present invention includes following operation: by flue and right for the supply of above-mentioned composite treating agent Sour gas contained in waste gas processes, and then flying dust is carried out dust, with heavy metal fixative pair Heavy metal contained in flying dust after dust processes.
The kind of waste gas is not particularly limited, such as, can enumerate: municipal refuse waste combustion stove, The combustion plant of trade waste incinerator, power plant boiler, retort, civil plant etc. produces Comprise the waste gas of the sour gas such as hydrogen chloride, oxysulfide.
For supplying the opportunity of composite treating agent, as long as being before dust arrester dust flying dust, just do not have yet Limit especially, such as, can enumerate: incinerate the moment of garbage etc. with incinerator;By giving up that incineration produces Gas is by flue, to the moment arrived between the temperature-reducing tower that the temperature to waste gas is lowered the temperature;Use temperature-reducing tower After being cooled down by waste gas, the waste gas after cooling is located at the moment etc. of dust arrester bag hose nearby to arriving.
The quantity delivered of composite treating agent is not particularly limited, in order to avoid very few, too much the appointing of quantity delivered Meaning situation, it is preferred that monitoring is by the concentration of the sour gas of flue, while suitably adjusting Joint, supplies in the way of the management objectives value of each combustion plant of object to make it meet.
After by composite treating agent supply to flue, to the product with sour gas Yu composite treating agent And unreacted reactant carries out dust as the flying dust of respective composition.The dust of flying dust is carried out with known dust arrester ?.
Here, illustrate as a example by the mode processing waste gas with composite treating agent, but as other side Formula, it is also possible to take double salt supply to flue, carry out flying dust adding in dust, flying dust after dust Add the mode of basicity depressant.It should be noted that when adding double salt and basicity depressant respectively, can Basicity depressant is added with the form with aqueous solution, slurry.
In the present invention, according to following effect, the basicity of the flying dust after dust is positively retained at reduced levels: A magnesium hydroxide is also thus reduced double salt as required constituent in addition to calcium hydroxide by () double salt Basicity effect itself and (b) utilize the sour gas of basicity depressant and the unreacted component of double salt and The according to circumstances basicity reducing effect of the product of sour gas and double salt.Therefore, even without a huge sum of money Belong to heavy metal contained in the flying dust after fixative processes dust, it is possible to the dissolution of the heavy metals such as suppression lead. But, in the case of the leaching ability of heavy metal or leaching ability of heavy metal in addition to lead of trace, preferably with weight Metal fixative processes heavy metal contained in the flying dust after dust.
As heavy metal fixative, can enumerate: normally used organic chelated system heavy metal fixative, Inorganic system heavy metal fixative etc..As inorganic system heavy metal fixative, can enumerate: phosphoric acid based compound, Silicon dioxide based compound, iron containing compounds and acid acceptor, it is possible to use selected from therein at least one More than Zhong.
Phosphoric acid based compound demonstrates the long-term fixed effect to the heavy metal in disposal site, protects from environment It it is effective material from the viewpoint of protecting.Phosphoric acid based compound can be anti-with such as lead as heavy metal Should, form chlorophosphate lead (Chloropyromorphite (Pb5(PO4)3Cl)), di lead (Hydroxypyromorphite(Pb5(PO4)3OH)), lead is fixed with the form of mineral.
As phosphoric acid based compound, as long as just can use without particular limitation containing phosphoric acid, Ke Yishi Phosphate can also be mineral.As concrete example, such as, can enumerate: orthophosphoric acid (Orthophosphoric Acid), polyphosphoric acids, Metaphosphoric acid, hypophosphorous acid, phosphorous acid, ortho phosphorous acid, pyrophosphoric acid, peroxophosphoric acid, Sodium dihydrogen phosphate, disodium hydrogen phosphate, sodium phosphate, potassium dihydrogen phosphate, dipotassium hydrogen phosphate, potassium phosphate, phosphorus Acid dihydride calcium, dicalcium phosphate, Magnesium biphosphate, phosphoric acid hydrogen two magnesium, ammonium dihydrogen phosphate, phosphoric acid hydrogen two Ammonium, calcium superphosphate, sodium tripolyphosphate, PTPP (potassium tripolyphosphate), sodium hexameta phosphate, hexa metaphosphoric acid potassium, burnt phosphorus Acid sodium, potassium pyrophosphate, sodium phosphite, potassium phosphite, sodium hypophosphite, ortho phosphorous acid potassium etc..Wherein, Orthophosphoric acid, dihydric phosphate, phosphoric acid hydrogen disalt, phosphate, tripolyphosphate, hexametaphosphate, Jiao Phosphate, have the mineral of the form of hydroxyapatite, especially apatite (apatite compounds) display Go out good heavy metal fixed effect.
In heavy metal, phosphoric acid based compound is particularly useful to the immobilization of lead.
For silica containing compound, it is believed that can obtain following effect: the calcium component in flying dust and two Silicon oxide reacts and generates calcium silicates mineral (3CaO 2SiO2·3H2O), thus heavy metal is enclosed Effect to these mineral;And silicon dioxide directly acts on heavy metal and generates the heavy metal of slightly solubility Silicate (PbSiO3Deng), thus fix the effect of heavy metal.Silica containing compound is to a huge sum of money Fixing of belonging to is affected by the alkali content in flying dust, in the case of the alkali content in flying dust is very big, required Addition increases.Thus, according to the present invention, silica containing compound can also significantly be cut down required Addition.
As long as silica containing compound contains SiO2The compound of composition, it is possible to limit the most especially System ground uses, and can be silicon dioxide itself, it is also possible to be salt, mineral.
For silica containing compound, can enumerate: sodium silicate, potassium silicate etc. comprise alkali metal or alkali The silicate of earth metal;Silicon ash, silica gel, active hargil, zeolite, bentonite, kaolinite, galapectite, Antigorite, pyrophyllite (pyrophyllite), Talcum, montmorillonite, saponite, Vermiculitum, white mica, sodium Muscovitum, illite, phlogopite, biotite, emerylite, holmesite, kaolinite chlorite (donbassite), Sudoite (Sudou stone), clinochlore, chamosite, meerschaum, Paligorskite, imogolite, The silicate mineral such as allophane and canbyite etc..
In heavy metal, silica containing compound is particularly useful to the immobilization of lead.
As iron containing compounds, as long as containing ferrum, can enumerate: ferrous chloride, iron chloride, sulphuric acid Ferrous iron, iron sulfate, polyiron sulfate, iron powder etc..
In heavy metal, iron containing compounds is particularly useful to the immobilization of Cr VI, arsenic, selenium and hydrargyrum.
Acid acceptor has the effect of the stripping quantity reducing heavy metal.Acid acceptor is also residued in fly The impact of the alkali of ash, in the case of the alkali content in residual flying dust is very big, required addition increases.Cause And, according to the present invention, acid acceptor can also significantly cut down required addition.
As acid acceptor, can be with example: hydrochloric acid, sulphuric acid, nitric acid, aluminum chloride, polyaluminium chloride, Aluminum sulfate etc..
Acid acceptor can be used alone, but from the viewpoint of suppression leaching ability of heavy metal further, excellent Choosing is applied in combination with above-mentioned inorganic heavy metal fixative.It addition, be applied in combination inorganic heavy metal fixative During with acid acceptor, it is preferred in terms of can reducing the consumption of inorganic heavy metal fixative of costliness 's.And then, it is applied in combination nertralizer and chelating system heavy metal the most also can get the effect of the present invention.
Here, the liquid-solid ratio that with the addition of the flying dust after inorganic heavy metal fixative and/or acid acceptor is Dissolution fluid pH when 10 is preferably 8.0~11.5, especially more preferably 9.0~10.5.
Embodiment
Below, the present invention is described in further detail by embodiment, but the present invention is not implemented by these Example limits.
The screening > of < basicity depressant
For basicity depressant, as long as the alkali one-tenth coming from calcium hydroxide contained in unreacted reactant can be reduced Point, as long as more than comprise in chloride, sulfate and hydroxide a kind compound, Just it is not particularly limited.
First, in order to confirm the effect of basicity depressant, the various compounds recorded for table 1, confirm With or without basicity reduction effect.
For ash (basicity: the 106mgCaCO produced by municipal refuse waste combustion stove A factory3/ g, Lead content: 4290mg/kg, lead release: 127mg/L), record with the ratio interpolation table 1 that table 1 is recorded Various basicity depressants.Then, the basicity after supply basicity depressant is measured.Show the result in table 1. According to table 1, for its result, various compound, confirm basicity reduction effect.
[table 1]
It addition, the sight of heat release during in order to find out stability from material self, suppression supply basicity depressant Basicity depressant preferably from the point of view of Dian, the various compounds recorded for table 2, carry out basicity reduction The screening of agent.
Raw material stability is by lower standing 1 week by basicity depressant and confirm outward appearance room temperature/normal being wet Evaluate.
Compounding stability is evaluated by the following method: add the high-specific surface area hydrogen-oxygen of explanation in embodiment Change dolomite 70 weight portion, basicity depressant 30 weight portion and water 20 weight portion, with spatula (spatula) It is stirred, and measures the temperature rise (Δ DEG C) before and after stirring.
The result of screening is shown in table 2.
[table 2]
Be can confirm that by table 2, copper chloride, magnesium sulfate, zinc sulfate, copper sulfate, magnesium hydroxide, hydroxide The raw material stability of aluminum, hydrated ferric oxide., ferrous hydroxide, zinc hydroxide and Copper hydrate, compounding are surely Qualitative equal excellence, preferably as basicity depressant.
It addition, when reducing for basicity with the relation of the dissolution concentration of harmful lead, use the flying dust of B factory Confirm.At this moment, use magnesium sulfate as basicity depressant.For the dissolution concentration of lead, based on industry The detection method (the Japanese Environment Room notified No. 13 in 1973) of metal etc. contained in garbage is tried by dissolution Test and obtain.Show the result in table 3.
[table 3]
Be can confirm that by table 3, when basicity reduces, lead release also reduces.
And then, for cannot meet land landfill reference value (0.3mg/L) condition, use as heavy metal The phosphoric acid based compound (75% positive acid solution) of fixative, carries out lead under the conditions shown in Table 4 and fixes Process.Result understands, and by reducing basicity, the required adding rate of heavy metal fixative reduces.
[table 4]
The preparation > of < composite treating agent etc.
(embodiment 1)
High-specific surface area hydroxide dolomite (using calcium hydroxide and magnesium hydroxide as constituent, is used Ca(OH)2·Mg(OH)2The double salt represented, specific surface area: 50m2/ g, median particle diameter (d50): 15 μm) 70 (name of product: Ash Knight I-201, uses chemical formula to the aluminium hydroxide of weight portion and containing sulfate Alx(SO4)y(OH)ZDeng expression compound, Kurita Water Industries Ltd. manufacture) 30 weight portions mix Close, obtain the composite treating agent of embodiment 1.
(embodiment 2)
The aluminium hydroxide of containing sulfate is changed into magnesium sulfate (specific surface area: 5.8m2/ g, median particle diameter (d50): 228 μm), in addition, by method similarly to Example 1, obtain the composite treating agent of embodiment 2.
It should be noted that in embodiment and comparative example, " specific surface area " is to be calculated by BET method The specific surface area gone out, " pore volume " is the pore volume calculated by BJH method.These physical property all can utilize The determinators such as the NOVA2000 that Quanta chrome Corporation manufactures measure.It addition, in " Value particle diameter (d50) " refer to adding up by the granule number in the particle size distribution that laser diffraction and scattering method is obtained Value is the particle diameter (d50) of 50%, it is possible to use the SALD-2100 that Shimadzu Scisakusho Ltd manufactures etc. survey Determine device to measure.
(comparative example 1)
By the most commercially available high response slaked lime (specific surface area: 46m2/ g, median particle diameter (d50): 7.9 μm, pore volume: 0.26ml/g) 70 weight portions and magnesium hydroxide (name of product: magnesium hydroxide 300, than Surface area: 35m2/ g, median particle diameter: 7 μm, Konoshima Chemical Co., Ltd. manufactures) 30 weights Mixture 70 weight portion of amount part and aluminium hydroxide 30 weight portion of the containing sulfate identical with embodiment mix Close, obtain the composite treating agent of comparative example 1.
(comparative example 2)
By high response slaked lime 70 weight portion identical with comparative example 1 and the sulfur acid identical with embodiment The aluminium hydroxide 30 weight portion mixing of salt, obtains the inorganic agent of comparative example 2.
(comparative example 3)
Using the high response slaked lime identical with comparative example 1 as the inorganic agent of comparative example 3.
One of the comparison of < process performance >
Use the various of the simulation dust arrester Lab-evaluation device that Fig. 1 records, evaluation embodiment and comparative example The process performance of inorganic agent.In this device, experimental condition is as described below.
Gas air quantity: 0.43m3/ minute
Filter area: 0.43m2
The rate of filtration: 1m/ minute
HCl concentration load: 350ppm
Dust storage chamber temperature: 180 DEG C
First, the HCl concentration of baghouse inlet is regulated to 350ppm, then, is initially supplied embodiment And the various inorganic agents of comparative example.Automatically supply beginning 20 minutes after rise, with HCl densitometer (name of product: HL-22, capital of a country Electronics Co., Ltd manufactures) measure outlet HCl concentration, the data that will gather every 1 minute The HCl exit concentration that is set under experimental condition of 30 minutes meansigma methodss.Then, by entrance HCl concentration and Outlet HCl densitometer calculates HCl clearance.Show the result in table 5 and Fig. 2.
[table 5]
In order to realize the addition of the inorganic agent needed for HCI clearance 90%
It has been confirmed that the composite treating agent of embodiment in the same manner as conventional various inorganic agents, can be suitable Ground processes sour gas.It should be noted that in order to realize HCl clearance 90% and required in embodiment The addition of composite treating agent be 1.4g/ minute, compared with the inorganic agent of comparative example, it can be seen that adding rate There is a little increase, but due to the basicity by reducing flying dust as described later, adding of heavy metal fixative can be made Dosage optimization, therefore, from including that exhaust-gas treatment and heavy metal are that there is no problem from the viewpoint of processing Scope.
Secondly, the residue basicity measuring the filter cloth attachment under the conditions of removing respectively and obtain.Show the result in Table 6 and Fig. 3.
[table 6]
HCI clearance is residue basicity when 90%
In the case of the composite treating agent using embodiment 1,2, basicity becomes 170mgCaCO3/ g~180mgCaCO3About/g, compared with the inorganic agent of comparative example 1~3, demonstrates aobvious The basicity reducing effect write.It addition, the addition of composite treating agent be 0.8g/ minute~1.6g/ minute this This tendency is all can confirm that in the wide in range scope of sample.
The ratio of < process performance is than two >
Embodiment and the various process of comparative example are evaluated in one of the comparison in above-mentioned < process performance > In residue after the process performance of agent, relative to 1 weight portion residue, mix being obtained by C factory of 4 weight portions The ash arrived, this ash is the ash of the 1st section that is not blown into Sour gas disposal agent and 2 sections of bag hoses, system It is made model fly ash.The characteristic of the ash obtained by C factory and the characteristic of various model fly ash are as shown in table 7.
[table 7]
It should be noted that in the present embodiment, measure lead content, dissolution fluid pH and lead by the following method Dissolution concentration.
The assay method of lead content
Flying dust concentrated nitric acid and concentrated hydrochloric acid carry out heating concentrate, cool down.After cooling, add pure water, will The solution quantitative filter paper after dissolving (Advantech Corporation manufacture, No.6) of heating filters, with former Sub-absorption spectrometer (Hitachi, Ltd. manufacture, Z-2000) measures the lead concentration in filtrate.
The assay method of dissolution fluid pH
After notifying that No. 13 test method(s)s carry out dissolution test based on the Japanese Environment Room, the pH carrying out dissolution fluid surveys Fixed.
The assay method of lead release
After notifying that No. 13 test method(s)s carry out dissolution test based on the Japanese Environment Room, use Atomic Absorption Spectrometer (Hitachi, Ltd. manufacture, Z-2000) measures the lead concentration in dissolution fluid.
It follows that for various model fly ashs, use the phosphoric acid based compound as heavy metal fixative (75% positive acid solution), carries out the fixing process of lead under the conditions shown in Table 8.Lead is fixed process and is passed through Following method is carried out: in various flying dust samples, add pure water and the rule of 20 weight % relative to flying dust Quantitative each heavy metal species fixative (phosphoric acid based compound, silica containing compound, iron content chemical combination Thing) and be sufficiently stirred for spatula.Then, the basicity and the lead that measure the various samples after lead fixes process contain Amount, and notify that No. 13 test method(s)s carry out dissolution test with the Japanese Environment Room, measure dissolution fluid pH and lead is molten Go out concentration.Show the result in table 8.
[table 8]
As shown in Table 8, for embodiment 1 and 2, it can be seen that basicity reduces, the stripping quantity fall of lead therewith Low.It addition, along with the reduction of basicity, for the stripping quantity of lead is reduced to fill the phosphorus of below reference value Acid is that the adding rate of heavy metal fixative reduces.

Claims (6)

1. sour gas and a composite treating agent for heavy metal, it comprises: containing calcium hydroxide and hydrogen-oxygen The double salt changing magnesium and constitute and basicity depressant.
Composite treating agent the most according to claim 1, wherein, the specific surface area of described double salt is 20m2/ more than g, median particle diameter d50 are less than 30 μm.
Composite treating agent the most according to claim 1 and 2, wherein, described basicity depressant is for being selected from More than a kind compound in chloride, sulfate and hydroxide.
Composite treating agent the most according to claim 3, wherein, described compound comprises selected from sulphuric acid Magnesium, the aluminium hydroxide of containing sulfate, zinc sulfate, copper sulfate, magnesium hydroxide, aluminium hydroxide, hydroxide In ferrum, ferrous hydroxide, zinc hydroxide, Copper hydrate more than a kind.
5. according to the composite treating agent described in any one in Claims 1 to 4, wherein, described sour gas Body is sour gas contained in waste gas, and described heavy metal is heavy metal contained in flying dust.
6. sour gas and a processing method for heavy metal, adds in the offgas containing calcium hydroxide and hydrogen Magnesium oxide and after the double salt that constitutes, carry out flying dust dust, and the flying dust after dust add basicity fall Low dose.
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112108109A (en) * 2020-09-29 2020-12-22 华中科技大学 Preparation method of kaolin-based composite heavy metal additive and product thereof
CN112121755A (en) * 2020-09-29 2020-12-25 华中科技大学 Preparation method of alumina carrier calcium ferrite microcrystal heavy metal curing agent and product
CN112156750A (en) * 2020-09-30 2021-01-01 华中科技大学 Preparation method of fly ash carrier heavy metal adsorbent for pulverized coal and product thereof

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR102604136B1 (en) 2021-03-31 2023-11-17 가부시끼가이샤 리켄 Side rail and oil control ring having it
CN114053997A (en) * 2021-11-10 2022-02-18 安徽博硕科技有限公司 Composite dioxin adsorbent and production process thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH09248541A (en) * 1996-03-14 1997-09-22 Kanegafuchi Chem Ind Co Ltd Waste treatment
CN102274605A (en) * 2010-06-09 2011-12-14 栗田工业株式会社 Stabilization treatment method for heavy metal containing heavy metal dust
CN102489134A (en) * 2011-12-07 2012-06-13 闻喜县瑞格镁业有限公司 Desulphurization method adopting calcined dolomite dust
CN102824833A (en) * 2011-06-17 2012-12-19 北京金源化学集团有限公司 Method for removing and recovering sulfur dioxide in gas by use of low-energy-consumption and regenerable absorbent
WO2013149241A1 (en) * 2012-03-30 2013-10-03 Fuel Tech, Inc. Dry processes, apparatus, compositions and systems for reducing sulfur oxides and hci

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61157328A (en) * 1984-12-28 1986-07-17 Hitachi Zosen Corp Purification of exhaust gas by dry dolomite method
JP2001149743A (en) * 1999-11-25 2001-06-05 Sumitomo Osaka Cement Co Ltd Waste gas treating agent and waste gas treating method
JP2001205047A (en) * 2000-01-27 2001-07-31 Sumitomo Osaka Cement Co Ltd Method for treating waste gas and soot dust
JP4525164B2 (en) * 2004-05-10 2010-08-18 任 安江 Digested dolomite powder and method for producing the same
JP5751689B2 (en) * 2013-01-23 2015-07-22 吉澤石灰工業株式会社 Exhaust gas treatment agent and method for producing the same
JP6199698B2 (en) * 2013-11-01 2017-09-20 栗田工業株式会社 Acid exhaust gas treatment method and exhaust gas treatment agent
JP2015178049A (en) * 2014-03-18 2015-10-08 栗田工業株式会社 Acidic waste gas-treating agent and method for preventing elution of heavy metals

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH09248541A (en) * 1996-03-14 1997-09-22 Kanegafuchi Chem Ind Co Ltd Waste treatment
CN102274605A (en) * 2010-06-09 2011-12-14 栗田工业株式会社 Stabilization treatment method for heavy metal containing heavy metal dust
CN102824833A (en) * 2011-06-17 2012-12-19 北京金源化学集团有限公司 Method for removing and recovering sulfur dioxide in gas by use of low-energy-consumption and regenerable absorbent
CN102489134A (en) * 2011-12-07 2012-06-13 闻喜县瑞格镁业有限公司 Desulphurization method adopting calcined dolomite dust
WO2013149241A1 (en) * 2012-03-30 2013-10-03 Fuel Tech, Inc. Dry processes, apparatus, compositions and systems for reducing sulfur oxides and hci

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112108109A (en) * 2020-09-29 2020-12-22 华中科技大学 Preparation method of kaolin-based composite heavy metal additive and product thereof
CN112121755A (en) * 2020-09-29 2020-12-25 华中科技大学 Preparation method of alumina carrier calcium ferrite microcrystal heavy metal curing agent and product
CN112156750A (en) * 2020-09-30 2021-01-01 华中科技大学 Preparation method of fly ash carrier heavy metal adsorbent for pulverized coal and product thereof
CN112156750B (en) * 2020-09-30 2022-04-29 华中科技大学 Preparation method of fly ash carrier heavy metal adsorbent for pulverized coal and product thereof

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